Encyclopedia of Biodiversity [Illustrated] 0816077266, 9780816077267

Biodiversity and ecology are founded in evolutionary science. In order to understand why species of organisms occupy dif

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Table of contents :
Cover
Contents
Acknowledgments
Introduction
The National Science Education Standards
Entries A-Z
A
B
C
D
E
F
G
H
I
J
K
L
M
N
O
P
Q
R
S
T
W
Appendix I: Chronology
Appendix II: Glossary
Appendix III: Further Resources
Appendix IV: Classification System Used in Encyclopedia of Biodiversity
Index
Recommend Papers

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ENCYCLOPEDIA OF Biodiversity

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ENCYCLOPEDIA OF

Biodiversity

Stanley A. Rice, Ph.D.

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ENCYCLOPEDIA OF BIODIVERSITY Copyright © 2012 by Stanley A. Rice, Ph.D. All rights reserved. No part of this book may be reproduced or utilized in any form or by any means, electronic or mechanical, including photocopying, recording, or by any information storage or retrieval systems, without permission in writing from the publisher. For information contact: Facts On File, Inc. An imprint of Infobase Learning 132 West 31st Street New York NY 10001 Library of Congress Cataloging-in-Publication Data Rice, Stanley A., 1957–   Encyclopedia of biodiversity / author, Stanley A Rice.    p. cm.—(Science encyclopedia)   Includes bibliographical references and index.   ISBN 978-0-8160-7726-7 (hardcover) ISBN 978-1-4381-3779-7 (e-book) 1. Biodiversity—Encyclopedias—Juvenile literature. I. Title.   QH541.15.B56R53 2012   578.703—dc22 2010050557 Facts On File books are available at special discounts when purchased in bulk quantities for businesses, associations, institutions, or sales promotions. Please call our Special Sales Department in New York at (212) 967-8800 or (800) 322-8755. You can find Facts On File on the World Wide Web at http://www.infobaselearning.com Excerpts included herewith have been reprinted by permission of the copyright holders; the author has made every effort to contact copyright holders. The publishers will be glad to rectify, in future editions, any errors or omissions brought to their notice. Text design by Annie O’Donnell Composition by Hermitage Publishing Services Photo research by Elizabeth H. Oakes and the author Cover printed by Bang Printing, Brainerd, Minn. Book printed and bound by Bang Printing, Brainerd, Minn. Date printed: December 2011 Printed in the United States of America 10 9 8 7 6 5 4 3 2 1 This book is printed on acid-free paper.

This encyclopedia is dedicated to Edward Osborne Wilson, who has spent his life studying the biodiversity that most people overlook, particularly ants and all the things they do that help to keep Earth alive. He has scientifically described many ant species and made major discoveries in ant biology. For decades, he has championed the public understanding and appreciation of biodiversity and has recently been focusing his attention on an online database of the species of the world (Encyclopedia of Life). Wilson has also made major contributions to evolutionary biology. Though one of the most famous scientists in the world, he is not too proud to get down on his knees to look at ants.

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Contents

acknowledgments

ix

introduction

x

the national Science education Standards entries a–Z

xiii 1

Essays: “Why are there So Many Species?”

50

“Ghosts of Biodiversity Past”

118

“ecosystem Services: Public or Private costs?”

214

“life of earth: Portrait of a Beautiful, Middle-aged, Stressed-Out Planet”

268

“if Humans Vanished . . .”

501

Appendixes: i. chronology

548

ii. Glossary

550

iii. Further Resources

556

iV. classification

564

index

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569

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Acknowledgments

the author acknowledges the energetic encouragement of Facts On File’s executive editor Frank Darmstadt, who was instantly available to guide and assist the author at all stages of manuscript preparation, from start to finish. the author also thanks agent Jodie Rhodes for zealous encouragement and for making this book possible. the author also thanks Michael axon, editorial assistant, for his meticulous preparation of the manuscript materials; the production staff

of Facts On File for preparing figures and facilitating electronic file transfer; the copyediting department; and elizabeth Oakes, for locating outstanding photographs. the author also greatly benefited from Southeastern Oklahoma State University’s providing internet resources and funds from Organized Research for the author to participate in scientific conferences. the author thanks his wife, a. lisette Rice, for making internet publicity of the author’s works possible.

ix

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Introduction

the loss of global biodiversity is one of the major crises in the world today. Plus, unlike other crises, it is irreparable: Once a species has become extinct, it is gone forever. Driving species into extinction is, as eminent evolutionary biologist edward O. Wilson states, the act for which future generations are least likely to forgive the present one. Political and economic problems can be solved, and even the most persistent pollutants will eventually decompose, but new species will not evolve to replace those that have been driven into extinction on any time scale meaningful to humans. the extinction of species is a crisis that can be easily dismissed. We may seldom notice the biodiversity around us. We may be accustomed to lawns that consist of just one species of grass, but natural grasslands contain many dozens of plant species, as did even the lawns around people’s houses in earlier centuries (see figure on page xi). to many people, nonhuman species (other than those upon which we directly depend for food) are not critically important. Some people believe that the only effect of global warming is the extinction of polar bears and that the only way in which polar bears are important is that wealthy ecotourists or watchers of cable television like to observe them. they are wrong in both ways. First, humans will suffer from global warming perhaps even more than the polar bears. Second, polar bears, as well as all other species, provide benefits that are essential for the human economy, particularly to agriculture and medicine. Most people do not realize how much our health care system depends on medicinal plants and animals and the native peoples who know about them. (that is right—the physiology of bears may help scientists understand how to treat some human diseases.) Most people do not realize how our food production systems depend on wild pollinators and the genes from wild species. they do not realize that intact ecosystems, with all of their component species, provide trillions of dollars of free services to the human economy. that is, if we do not protect wild

species and the ecological communities in which they live, we are putting the world economy at risk. Someone needs to explain this to them. this encyclopedia does so. the extinction crisis is also easy to overlook. to someone who has not studied them, the different species of oak trees or of frogs all look pretty much alike, and if one of them becomes extinct, there are plenty of others. However, each species has its own unique set of genes, and no other species can completely substitute for it. Most extinctions today are caused by human activity. the most detrimental human activity is habitat destruction. Humans cut down forests to provide wood and create pastures and pave over grasslands with suburban expansion. Some of the most rapid destruction of natural habitats is in the parts of the world with the most species, such as california and the western amazon basin. extinctions caused by habitat destruction have skyrocketed in the last century. the rate of extinction occurring today is at least as great as during most of the five mass extinction events in earth history, and human activity is now causing the sixth mass extinction. nevertheless, an even greater extinction crisis looms as global warming begins to disrupt natural habitats and all the species that live in them. in the 19th century, some people tried to “shoot the last buffalo,” but in the 21st century, humans can disrupt the whole prairie ecosystem in which buffalo used to live. People need to learn to notice and appreciate biodiversity, and they have to begin doing so while they are young. as kids, they need to spend some time outdoors in direct contact with trees and grasses and spiders and birds. By the time they are in high school or have entered college, they need to learn a great deal about biodiversity, its importance to humans, and the nature of the threats against it. Encyclopedia of Biodiversity enables high school and college students to fi nd information about all of these things. the 153 cross-referenced entries and five essays average at least 2,000 words each, x

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Introduction long enough to provide a good understanding but small enough to not discourage reading. High school teachers can use these entries to meet many of the science education goals established by the National Academy of Sciences, as outlined in the section on the National Science Education Standards. If people do not discover biodiversity when they are young, they may never do so. I once had a student who barely passed a college plant diversity course. However, he told me that he had previously driven his truck down the highway not noticing the trees; now, as he drove, he recognized how many different species of trees were there and how the ones that lived near the rivers were different from those that lived on the hillsides (even if he forgot what they were). We had remediated his biodiversity ignorance just a little, and just in time. Educators and scientists realize that citizens need to have “science literacy” in order to make informed decisions as consumers and voters. Despite the abundance of information available on the Internet and massive expenditures on education, most citizens are unable to draw a valid conclusion from scientific information, whether it concerns their own health or the health of the environment. The National Academy of Sciences even referred to the danger that the lack of science literacy poses to the future of the United States as “The Gathering Storm.” One of the goals of this encyclopedia is to make information about groups of organisms, from bacteria to mammals, and about ecological concepts and processes, such as biogeography and ecological succession, clearly and readily available to students and the general public. Fortunately, biodiversity is one of those topics for which it is easy to generate interest. The world is full of millions of colorful and fascinating species. The entries and colorful illustrations of this encyclopedia will invite readers to explore worlds that they already know will interest them, but such material must be presented in an interesting way. That is what I have tried to do. I am a trained professional botanist, but most of my work for the past two decades has been to make botany and other biodiversity and ecological topics interesting to students and to readers. I have little interest in writing things that will be read only by other scientists. I have traveled all over the United States (and some other parts of the world) in search of ecology and biodiversity stories. I have seen and been excited by many of the things I write about in this encyclopedia and hope to pass the enthusiasm on to my readers. All stories about biodiversity and ecology are founded in evolutionary science. It is not possible to understand why some species of organisms live

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xi

Albrecht Dürer painted The Great Piece of Turf in 1503. The lawn depicted in this painting contains species such as dandelions and plantains, which most people today consider to be weeds and which are seldom tolerated in modern lawns.  (Graphische Sammlung Albertina, Vienna)

in one part of the world and others in a different part of the world without understanding how they evolved. In this encyclopedia, I consistently provide the evolutionary framework in which biodiversity must be understood. The figures and tables are designed to be useful. Several of the tables contain lists of species. Such a list would be meaningless in itself, but these lists compare the species in one part of the world with those in other parts, allowing global and evolutionary patterns of biodiversity to be seen. To my knowledge, such lists are available in no other publication. Humans live in a world of species, and we depend upon them not only for our physical survival but our psychological health. We need to save these other species and the ecological communities that they form. We will save only what we love, and we will love only what we closely observe and learn about. I intend this encyclopedia to help students and general readers learn about and love the world of biodiversity. See also biodiversity, resources for agriculture; biodiversity, resources for medicine;

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xii xii Introduction ecosystem services; environmental psychology; mass extinctions. Further Reading Carson, Rachel. Silent Spring. New York: Houghton Mifflin, 1962/2002. Darwin, Charles. On the Origin of Species by Means of Natural Selection, 1st ed. London: John Murray, 1859. Available online. URL: http://darwin-online.org.uk/ content/frameset?itemID=F373&viewtype=side&p ageseq=1. Accessed July 7, 2011. Louv, Richard. Last Child in the Woods: Saving Our Children from Nature Deficit Disorder. Chapel Hill, N.C.: Algonquin Books, 2008.

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first entry McKibben, Bill. The End of Nature. New York: Random House, 1990/2006. Millennium Ecosystem Assessment. “Millennium Ecosystem Assessment.” Available online. URL: http://www. maweb.org/en/index.aspx. Accessed December 4, 2010. Rands, Michael R. W., et al. “Biodiversity conservation: Challenges beyond 2010.” Science 329 (2010): 1,298–1,303. Wilson, Edward O. The Diversity of Life. Cambridge, Mass.: Harvard University Press, 1992. ———. The Creation: An Appeal to Save Life on Earth. New York: Norton, 2006.

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The National Science Education Standards

the national Research council has identified life sciences content standards for grades 9–12. entries in this encyclopedia are relevant to four of the content standards (c, D, F, and G) established by the national Research council. Standard c includes: ● ● ●

continental shelves, biodiversity on convergence coral reefs cretaceous extinction cretaceous period, biodiversity in crustaceans Darwin’s fi nches decomposers deep oceans, biodiversity in deserts, cool deserts, polar deserts, warm Devonian period, biodiversity in dicots dinosaurs disjunct species disturbances, ecological Dna studies of biodiversity ecology ecosystems ediacaran organisms endangered species endemic species eukaryotes extinction fishes flowering plants (angiosperms) fossils and fossilization founder effect and genetic drift fungi Galápagos islands grasslands and savannas herbivory hybridization ice ages insects island biogeography Jurassic period, biodiversity in keystone species lichens life history, diversity of living fossils

Biological evolution interdependence of organisms Behavior of organisms

the encyclopedia entries that provide information for this standard, which includes the diversity of organisms, are the following: adaptation adaptive radiation amphibians animals archaea arthropods bacteria biodiversity, concept of biodiversity, patterns of biodiversity, quantification of biogeography biological classification birds bogs, life in boreal and subalpine forests cambrian explosion cambrian period, biodiversity in camouflage and mimicry carboniferous period, biodiversity in carnivorous plants cladistics cloud forests coevolution commensalism communities, ecological competition, ecological conifers xiii

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xivxiv The National Science Education Standards mammals marshes and swamps mass extinctions monocots mutualism natural selection Neogene period, biodiversity in Ordovician period, biodiversity in Paleogene period, biodiversity in parasitism Permian extinction Permian period, biodiversity in Pleistocene extinction pollination predation primates protists Quaternary period, biodiversity in reptiles rivers, streams, ponds, and lakes seed dispersal seedless plants seed plants sexual selection shrublands Silurian period, biodiversity in speciation spiders succession, ecological symbiogenesis temperate coniferous forests temperate deciduous forests temperate dry forests temperate rain forests Triassic period, biodiversity in tropical rain forests and deforestation tropical seasonal forests tundra Standard D includes: ●● ●● ●●

Energy in the Earth system Geochemical cycles Origin and evolution of the Earth system

The encyclopedia entries that provide information for this standard are the following: biogeochemical cycles carbon cycle ecosystems Gaia greenhouse effect greenhouse effect and biodiversity hydrological cycle

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first entry ice ages nitrogen cycle Standard F includes: ●● ●● ●● ●● ●● ●●

Personal and community health Population growth Natural resources Environmental quality Natural and human-induced hazards Science and technology in local, national, and global challenges

The encyclopedia entries that provide information for this standard are the following: acid rain and fog agriculture biodiversity, resources for agriculture biodiversity, resources for medicine biomagnification biomimicry bioremediation conservation biology cultural diversity ecosystem services endangered species environmental ethics federal government role in conservation (United States) greenhouse effect greenhouse effect and biodiversity habitat fragmentation integrated pest management (IPM) invasive species natural systems agriculture pollution population biology population genetics resistance, evolution of restoration ecology tropical rain forests and deforestation Standard G includes: ●●

Historical perspectives

The encyclopedia entries that provide information for this standard are the following: Bates, Henry Walter Carson, Rachel Darwin, Charles Grant, Peter and Rosemary Humboldt, Alexander von

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The National Science Education Standards  Jackson, Wes Janzen, Daniel H. Leopold, Aldo Linnaeus, Carolus Maathai, Wangari Margulis, Lynn Muir, John Pinchot, Gifford Thoreau, Henry David Wallace, Alfred Russel Wilson, Edward O.

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xv

Further Reading National Research Council. National Science Education Standards. Washington, D.C.: National Academies Press, 1996. Available online. URL: http://www.nap. edu/openbook.php?isbn=0309053269. Accessed January 6, 2011.

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Entries A–Z

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A acid rain and fog  acid rain and fog, also called

acid precipitation, occur when air pollution acidifies the water droplets in clouds and the resulting acid comes in contact with objects and organisms. the major air pollutants that cause acid precipitation are nitric acid (HnO3) and sulfuric acid (H 2SO4), which are the dissolved forms of nitrous and nitric oxide and sulfur dioxide gases, although natural sources of pollutants include wetlands and volcanoes. Sulfur dioxide is particularly common in the smoke from power plants that burn high-sulfur coal. Many power plants now have “scrubbers” that remove sulfur dioxide from the effluent before it is released into the atmosphere. in some cases, rain downwind from industrial areas has been as acidic as orange juice or vinegar. the record pH is 2.4. (Pure water is pH 7, and changes in pH represent orders of magnitude of difference in acidity.) acid rain and fog can be considered the unintended consequence of the control of particulate air pollution (soot) in the second half of the 20th century. Soot helps to neutralize some of the acid. By producing less soot, power plants caused more acidproducing compounds. Moreover, by using taller smokestacks, power plants displaced air pollution away from cities and into layers of air that brought acid rain and fog into the mountains. acid dissolves limestone. Before the limitation of air pollution in cities, acid rain was steadily dissolving limestone statues and architecture. acid rain has also been reported to damage the fi nish on automobiles. the major impact of acid precipitation has been on biodiversity, as in these examples. ●







acid rain has the potential to cause direct damage to plants by harming the waxy

cuticles of leaves and penetrating into the photosynthetic tissues. this kind of damage has not occurred very extensively, however, because only the fi rst few minutes of a rain event are significantly acidic; thereafter, rain that is less acidic rinses much of the previously deposited acid away before it can damage plants. acid rain has the potential to remove nutrients from soils. the negatively charged surfaces of soil clay particles attract and hold positively charged ions such as potassium and magnesium, which are plant nutrients. Hydrogen ions (which are the cause of acidity) displace the plant nutrients, thus reducing the fertility of the soil. Moreover, some toxic ions such as lead and aluminum, normally scarce in soil water, may become common if the water is acidified. this does not occur, however, in soils derived from limestone, as the limestone will neutralize the acidic rain. acid rain has the potential to accumulate in lakes, thereby reducing the growth of algae and making less food available for the entire food chain. acidity can directly affect some kinds of fi sh, particularly their eggs. trout are especially sensitive to acidified water. this does not occur in lakes fed by groundwater that fi lters through limestone. acid precipitation has been most harmful in the form of acid fog. acidified droplets in clouds settle on the leaves of plants, especially coniferous trees of mountains, and remain for long periods of time. Often, these trees die. extensive areas of forest in

1

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2

2 adaptation  Europe (such as the forests of Switzerland and the Black Forest of Germany) have suffered from acid fog. In many cases, acid fog is an indirect cause of death. Much of the subalpine fir forest near Mount Mitchell, at the summit of the Appalachians, has died from disease introduced by woolly adelgid bugs (Adelges tsugae). The firs normally resist the bugs—unless they are weakened by acid fog. Acid precipitation was identified as a major problem during the 1970s. Congress passed the Acid Deposition Act in 1980, which established a 10-year study. The Reagan administration convened the Acid Rain Peer Review Panel of the National Academy of Sciences. They then insisted that a scientist notorious for his outspoken antienvironmental views, S. Fred Singer, be included on the panel. Singer’s fame arose from his work on nuclear weapons three decades earlier, and he did not have recognized expertise in the study of acid pollution. He claimed, without adequate study, that controlling the acid rain problem would devastate the American economy and cause utility prices to increase immensely. The panel, with the exception of Singer, concluded that acid rain was a serious problem and that utilities and industry should reduce sulfur emissions. The Reagan administration’s Office of Science and Technology Policy, however, altered the executive summary of the report and focused on Singer’s viewpoint as the major conclusion of the panel. As a result, meaningful action on acid rain was delayed until the administration of George H. W. Bush. Congress passed amendments to the Clean Air Act in 1990, establishing a system of “cap and trade” to encourage industrial polluters to limit their emissions. Corporations could comply with the law by reducing emissions or by buying pollution credits from other corporations that produced fewer emissions than those permitted by law. The economic devastation predicted by Singer did not occur, and the price of electricity even decreased slightly. Singer continues his attacks on environmental issues, presently focusing on global warming. Although sulfur dioxide emissions have decreased by 40 percent since the law took effect and acid rain has decreased 65 percent since 1976, it remains a serious problem. The ecosystem ecologist Gene Likens indicated in 2009 that the forests of northeastern North America, damaged by acid rain, have not yet begun to grow back. The cap and trade system apparently worked, but not well enough to reverse the problem. Acid precipitation is also an international problem, as the air pollution of one country (such as the United States or Germany) can cause the death of

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first entry forests in another (such as in Canada or Switzerland). The control of air pollution, particularly of sulfur dioxide, has reduced the impact of acid precipitation since the 1980s. Due to pressure from industry, the U.S. government has been reluctant to call attention to acid precipitation. For example, National Park Service displays in Shenandoah National Park attributed the death of subalpine fir trees to the adelgid bugs, not mentioning the effects of acid fog. See also boreal and subalpine forests; greenhouse effect; pollution. Further Reading Galloway, J. N., et al. 1987. “Acid rain: a comparison of China, United States and a remote area.” Science 236 (1987): 1,559–1,562. Kizlinski, M. L., et al. “Direct and indirect ecosystem consequences of an invasive pest on forests dominated by eastern hemlock.” Journal of Biogeography 29 (2002): 1,489–1,503. Likens, G. E., and F. H. Bormann. “Acid rain: A serious regional environmental problem.” Science 184 (1974): 1,176–1,179. ———, et al. “Long-term effects of acid rain: Response and recovery of a forest ecosystem.” Science 272 (1996): 244–246. ———, and Jerry F. Franklin. “Ecosystem thinking in the northern forests—and beyond.” BioScience 59 (2009): 511–513. Menon, Manoj, et al. “Effects of heavy metal soil pollution and acid rain on growth and water use efficiency of a young model forest ecosystem.” Plant and Soil 297 (2007): 171–183. Mphepya, J. N., et al. “Precipitation chemistry and wet deposition in Kruger National Park, South Africa.” Journal of Atmospheric Chemistry 53 (2006): 169–183. Oreskes, Naomi, and Erik M. Conway. “Sowing the seeds of doubt: Acid rain.” Chapter 3 in Merchants of Doubt: How a Handful of Scientists Obscured the Truth on Issues from Tobacco Smoke to Global Warming. New York: Bloomsbury, 2010.

adaptation  Adaptation is the fit of an organism to its environment, which allows successful survival and reproduction. The environment of an organism includes other organisms of the same and different species. For any physical or biological environment, many different adaptations are possible, and this has resulted in exuberant biodiversity on Earth. Characteristics That Are Not Genetically Based Physiologists often use the word adaptation to describe environmentally induced characteristics

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adaptation  rather than genetically based ones. These physiological adjustments can occur on the following three different levels:

they would have had they lived at sea level; larger lungs compensate for the lower oxygen availability at high elevations.

Physiological response occurs when an organism makes immediate physiological or behavioral changes to its environment. On a hot day, the stomata (pores) of a leaf may open. This allows water to evaporate from the leaf, making it cooler through the process of transpiration. The evaporation of water may also cool a mammal on a hot day (perspiration). The mammal may also respond behaviorally by seeking shade and by exposing its skin surface areas, allowing heat to diffuse into the air. In contrast, on a cold night, the mammal curls into a ball, reducing its heat loss. These responses typically do not involve changes in gene expression. Instead, the molecules and structures that are already present behave differently under the changed conditions. Acclimatization occurs when an individual organism adjusts its physical characteristics. Consider again the example of a leaf on a hot day. The leaf cells accumulate or manufacture molecules, which cause water to diffuse into them. The influx of water makes the leaf more resistant to wilting. Or consider humans at high elevations. When humans live at high elevations for a week or more, their bone marrow begins to manufacture more red blood cells, which compensates for the lower availability of oxygen at high elevations. These are not immediate responses; they require the genetically controlled manufacture of new materials. In animals, such changes can occur also as a result of behavioral changes (e.g., muscle building). Phenotypic plasticity occurs when individual organisms adjust to their environments as they develop. The leaves of plants that grow in cool, shady, moist conditions are often larger than those of plants that grow in warm, bright, dry conditions, even if all the plants are genetically identical, and the plants that grow in warm, bright, dry conditions have relatively larger root systems. This is illustrated by an experiment with the weed Abutilon theophrasti (see figure on page 4). The characteristics of both kinds of leaf result from the same genes, but the genes are expressed differently in each group of plants. Or consider humans who live from childhood at high elevations. These people may develop larger lungs than

Plasticity is rarely reversible and rarely changes after development of an organ or organism is complete. Although leaves can change the amount of dissolved substances in their cells, they cannot change their size once their development is complete. That is, acclimatization is reversible and plasticity, in this case, is not. The red blood cell count can change, but lung size cannot after childhood. In this case also, acclimatization is reversible and plasticity is not. As a result of plasticity, various cells or tissues of an organism can respond differently to the same environmental conditions. Plasticity and acclimatization are responsible for much of the phenotypic variability observed in natural environments. Not all environmentally induced differences among individuals in a population are plasticity; in some cases, they may result simply from patterns of growth. As herbaceous plants grow, they accumulate stems and roots but shed their old leaves. A bigger plant will therefore have a relatively lesser amount of leaf material. Plants that grow in the shade are smaller and have relatively more leaf material than plants that grow in bright sunlight. The greater amount of leaf material is not necessarily plasticity; it may be due solely to the smaller size of the shade plants. Plasticity can be passed down from one generation to another. For example, a large, healthy plant may produce not only more seeds but bigger seeds that contain more nutrients. These seeds may grow into plants that have different characteristics than those that grow from the seeds of smaller plants, even if they are genetically identical. Research by the botanists Laura Galloway and Julie Etterson showed that in populations of a forest floor wildflower, plants that had grown in deeper shade produced seeds that grew into plants that had superior growth in deeper shade compared to seeds from plants that had grown in patches of sunlight. Such “intergenerational plasticity” may result from epigenetics, in which the expression of the gene, rather than the gene itself, changes, and this change is passed on to the next generation.

●●

●●

●●

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3

Characteristics that Are Genetically Based Evolutionary and conservation biologists restrict the use of the word adaptation to the genetic results of natural selection and sexual selection. Therefore, not all genetic variation is adaptation. There are several sources of genetically based variation that are not produced by selection. Some of the genetic differences among individuals, populations, and species may have resulted from historical accidents that

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4

4 adaptation

first entry

Plants that develop in the shade grow taller and produce smaller root systems and more leaf area than plants that develop in full sunlight. Plants that develop in dry conditions grow shorter and produce larger root systems and less leaf area than plants that develop in moist conditions. This is an example of phenotypic plasticity, which is sometimes called adaptation, but which does not involve genetic changes. The numbers come from an experiment by the author using the weed Abutilon theophrasti. The three treatments are compared at the overall average weight of 854 mg.

affected the course of evolution. the most common genes may have been the ones that got lucky, rather than being selected. Genetic drift and the founder effect are examples of historical accidents. the genes that are most common in a population or a species may simply be those that were most common when the species almost became extinct or when it was fi rst founded by a small number of individuals. in both cases, the species experienced a genetic bottleneck in which, by chance, much of the genetic

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variation was lost. consider a population of flowering plants on an island. all the flowers might be red not because natural selection favored red flowers on the island but because the only seeds that reached the island in the original population were those of red-flowered individuals. Populations of many endangered species have genetic characteristics that resulted from genetic bottlenecks. exaptations are genetically based traits that may have originally evolved because they performed one

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adaptation  function but then were available for another function. This means that selection may not have acted directly on the trait being considered; the trait may have been a side effect of selection. A frequently cited example of an exaptation is feathers. The earliest birds apparently used feathers as insulation. After feathers had evolved as insulation, natural selection acted upon them as flight structures. After that, sexual selection acted upon them as colorful adornments. Feathers, therefore, can be considered adaptations for insulation and exaptations for flight and sexual adornment. It can be difficult to distinguish adaptations from exaptations. The classic example of an adaptation that has appeared in numerous popular science books and textbooks for more than a century is the neck of the giraffe (see below). To most observers, it would appear obvious that long necks are an adaptation that allows giraffes to feed at the tops of trees, but if this is so, why do female giraffes have shorter necks than male giraffes, and why are giraffes so frequently observed actually bending down to eat leaves? Observations of giraffes in the wild have shown that males with longer necks prevail in maleto-male competition, and females choose the males with longer necks. Now that giraffes have long necks, they can use them for eating leaves from treetops, but that may not have been the original reason that long necks evolved in these animals. The long neck of the giraffe appears to be an adaptation to combat and an exaptation for reaching leaves at the tops of trees. Some characteristics of organisms are structurally inevitable. Large plants must have relatively thick trunks, and large animals must have relatively

5

thick legs. Structurally inevitable features are called allometric characteristics and are not considered to be adaptations. In most cases, an adaptation does not have just a single function. The glands within an animal’s epidermis have several functions, each of which may have provided a separate evolutionary advantage. Some of the glands produce sweat, which allows the animal to become cooler as the sweat evaporates. Sweat also contains dissolved molecules. The body of the animal uses sweat as one of its methods of disposing of excess or toxic materials. Molecules in sweat can also serve as chemical communication between animals. Mammary glands are modified sweat glands. Sweat glands, therefore, are an adaptation with at least four different functions. Adaptations are never perfect. Natural and sexual selection produce adaptations that are only as good as they need to be. One example is the digestive system of the panda. The immediate ancestors of pandas were carnivores, but pandas are herbivores, living exclusively on leaves. Pandas have intestines that are better suited to a carnivore. In well-adapted herbivores, such as sheep, the intestines are up to 35 times as long as the body, while in well-adapted carnivores, the intestines are much shorter, only four to seven times as long as the body. With the help of bacteria, longer intestines allow herbivores more time to digest coarse plant materials, such as cellulose. Meat, in contrast, requires less digestive breakdown. Pandas have intestines that are in the carnivore, not the herbivore, range. The panda’s digestive system is, therefore, not well adapted to its function. Modern evolutionary scientists attribute this to the recent evolutionary shift from meat to leaves in the diet of the panda’s ancestors: There has not been time for better adaptation in this case.

Adaptation and Biodiversity

Giraffes can drink only with the greatest difficulty. Their long necks appear to be as much a hindrance as an adaptation to their daily work of eating and drinking and seem to have evolved by sexual selection, not natural selection.

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Adaptation is the reason there is such an astonishingly large number of species. If there were only one perfect adaptation for every situation, such as a dry climate, then there would be very few species. All plants in a dry climate would look more or less the same, and one species would dominate that climate. However, this is far from the case. There are many possible plant adaptations to a dry climate. Some plants, such as mesquite shrubs, grow very deep roots to draw water up from the water table. They also have small leaves, which diffuse heat into the air more quickly than do large leaves. In this way, the small-leaved shrubs can keep their leaves cool without much transpiration. Some plants do both of these things. Others, such as cactuses, have shallow roots, but they store water in their succulent tissues. Still others, such as the spring ephemeral ­wildflowers

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6 adaptive radiation  of the desert, have neither of these adaptations. Instead, they germinate and grow rapidly during the brief rainy season, surviving the long drought in the form of seeds. A similar diversity of adaptation can be seen in desert animals, some of which, such as kangaroo mice, function with very little water, while others, such as desert frogs, remain dormant in the soil between periods of rain. Throughout evolutionary history, various evolutionary lineages have responded to environmental circumstances in many different and equally successful ways. Coevolution also produces many different adaptations and promotes biodiversity. Coevolution occurs when the evolution of one type of organism influences the evolution of another; they adapt to one another. When flowering plants evolved near the beginning of the Cretaceous period, they began to depend upon many different kinds of pollination. Some depended upon the wind, but many engaged the services of animals such as insects to carry their pollen. This began an explosive diversification of flowering plant species, each evolving the ability to attract a different insect species. Meanwhile, the insects were also evolving numerous different and equally successful adaptations that allowed them to obtain food from the flowers they pollinated. Evolutionary diversification in flowering plants and pollinators reinforced each other. The adaptations that have resulted from coevolution have been the major source of biodiversity on Earth. See also endangered species; extinction; founder effect and genetic drift; natural selection; sexual selection. Further Reading Dawkins, Richard. The Blind Watchmaker: Why the Evidence of Evolution Reveals a Universe Without Design. New York: Norton, 1996. Galloway, Laura F., and Julie R. Etterson. “Transgenerational plasticity is adaptive in the wild.” Science 318 (2007): 1,134–1,136. Gould, Stephen Jay, and Elisabeth Vrba. “Exaptation—a missing term in the science of form. Paleobiology 8 (1982): 4–15. Rice, Stanley A., and Fakhri A. Bazzaz. “Plasticity to light conditions in Abutilon theophrasti: comparing phenotypes at a common weight.” Oecologia 78 (1989): 502–507.

adaptive radiation  Adaptive radiation is the evolution of species from a single, ancestral population. Throughout the history of life, many species have become extinct either by natural selection or simply bad luck, while others have produced many new species by adaptive radiation from the surviving

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first entry species. Adaptive radiation can result either from the dispersal of a species to a new location, after which the founding population undergoes radiation, or the survival of remnant populations of a once widespread species, after which the remnants undergo radiation. The net result has been a steady increase in biodiversity through evolutionary time. Adaptive radiation occurs because a single ancestral population separates into distinct populations that do not interbreed, thus allowing separate directions of evolution to occur in each. The world is full of numerous examples of adaptive radiation. Nearly every genus that contains more than one species or any family that contains more than one genus can be considered an example. Two examples follow. First, consider the white oaks, part of the genus and subgenus Quercus. At one time, probably before 80 million years ago, there was a single species of white oaks that may have lived in what is now East Asia. In the late Mesozoic and Cenozoic eras, warm conditions were widespread on Earth. Oaks spread throughout the Northern Hemisphere. Three of the locations in which they are now found are Europe, eastern North America, and California. North America then separated from Eurasia, new mountain ranges such as the Rocky Mountains arose, and conditions became cooler and drier during the latter part of the Cenozoic era. These events separated the white oaks of Europe, eastern North America, and California. Separate species evolved in each of these locations, including Quercus robur (English oak) in Europe, Quercus macrocarpa (bur oak) in eastern North America, and Quercus douglasii (blue oak) in California (see figure on page 7). Furthermore, in each of these locations, cooler conditions allowed the evolution of the deciduous pattern of leaf production in some areas, while warmer conditions encouraged the evolution of the evergreen pattern in other areas. The previously mentioned species are all deciduous. Quercus suber (cork oak) is an evergreen white oak of Europe; Quercus virginiana (live oak) is the evergreen white oak of eastern North America; and Quercus dumosa (scrub oak) is an evergreen white oak of California. In all three areas, both deciduous and evergreen (live) oaks evolved (with some exceptions). These oak species and many others constitute an example of adaptive radiation within the white oak subgenus. Second, while the adaptive radiation of oaks occurred over the course of about 80 million years, the adaptive radiation of the approximately 500 species of cichlid fishes of Lakes Malawi, Tanganyika, and Victoria in Africa has occurred in just the last few thousand years. From what was probably a single ancestral species, the cichlids in Lake Victoria

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adaptive radiation

7

An ancestral population of deciduous white oak trees may have grown in the northern continents before they separated by continental drift. The formation of the Atlantic Ocean and the origin of the Rocky Mountains, deserts, and grasslands separated this population into European, eastern North American, and Californian populations, which evolved into three species of deciduous oaks (Quercus robur, Q. macrocarpa, and Q. douglasii). Separately in each location, evergreen (live) oak species subsequently evolved (Q. suber, Q. virginiana, and Q. dumosa).

have radiated into such different species as fish with heavy jaws that crush mollusks; slender, swift fish that eat plankton; small fish that eat parasites off the skins of larger cichlid fishes; large fish that eat other fishes; and fish with sharp teeth that scrape algae off rocks. there is very little genetic variation among these species, so rapid and recent has been their adaptive radiation. the Hawaiian archipelago also provides an example of adaptive radiation in both time and space. the Hawaiian archipelago, on the Pacific Plate, sits over a plume of lava that rises from the mantle, known as a hot spot. Volcanic eruptions occur at the site of the hot spot. the Pacific Plate has moved northwest, while the hot spot has remained stationary. the oldest islands in the Hawaiian archi-

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pelago are toward the northwest, and the youngest toward the southeast. the oldest islands have now eroded and are beneath sea level. the oldest major islands still in the Hawaiian archipelago are niihau and Kauai, which were formed about 5 million years ago. they have no active volcanoes anymore. the islands of Oahu, Molokai, lanai, and Maui are of intermediate age. the youngest island, Hawaii, is less than 1 million years old and still has active volcanic eruptions. Plant and animal species have dispersed to the islands, primarily from the southwest, and species unique to the Hawaiian archipelago have evolved. Species have also dispersed from older islands to younger islands once the younger islands became suitable for life, radiating into new species on each island. adaptive radiation has occurred in

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8 agriculture  space (unique species on each island) and in time (from older to younger islands) in the Hawaiian archipelago. Perhaps the most famous adaptive radiation has been the evolution of Darwin’s finches in the Galápagos Islands. A single ancestral species, which may have come from the South American mainland, has radiated out into 13 species in four genera. Finches in three of the genera live in trees. Some of them have some amazing adaptations, such as the species that uses sticks to pry insects out of holes in branches. The largest genus, with six species, consists of finches that hop on the ground and eat mostly seeds. Sometimes, speciation occurs as one species coevolves in the presence of another. However, the presence of other species can preclude some directions of speciation. On the Galápagos Islands, predators are largely absent, and some of the finches have figured out a way to drink blood from the legs of boobies (large marine birds) by pecking them. Also, woodpeckers are absent, and some of the finches, as mentioned above, use sticks to get insects out of holes. In a habitat already filled with efficient predators and woodpeckers, the amateurish adaptations displayed by the blood-drinking and insect-prying finches would probably not have succeeded. Therefore, adaptive radiation can occur rapidly when a population invades a new habitat—if, that is, the population is adapted to the conditions of the new habitat and if the new habitat does not have potential competitors. Release from competition is the reason adaptive radiation has occurred most spectacularly in the history of Earth after large disasters. During the Mesozoic era, mammals were few in number and low in diversity. Their constant body temperatures made them successful nocturnal animals. The dinosaurs, meanwhile, ruled the daytime. After the Cretaceous extinction, which cleared away the dinosaurs, mammals underwent an explosive adaptive radiation. Large mammals did not exist before the Cenozoic era; any mammal species that began to evolve a large size would have been unsuccessful in competition with large dinosaurs, but many huge mammals evolved in the early Cenozoic. Along with the big mammals, many of the modern categories of mammals, including whales, primates, and bats, evolved. Mammals have continued to have adaptive radiations, but none quite as spectacular as the adaptive radiation that occurred early in the Cenozoic era. Within species, the adaptive radiation of subspecies and varieties continues. These represent possible future species. The preservation of biodiversity requires not just the protection of species but of subspecies and varieties as well.

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first entry See also biogeography; coevolution; Darwin’s finches; extinction; mass extinctions; speciation. Further Reading Gillespie, Rosemary G. “The ecology and evolution of Hawaiian spider communities.” American Scientist 93 (2005): 122–131. Grant, Peter R., and B. Rosemary Grant. How and Why Species Multiply: The Radiation of Darwin’s Finches. Princeton, N.J.: Princeton University Press, 2007. Schilthuizen, Menno. Frogs, Flies, and Dandelions: The Making of Species. New York: Oxford University Press, 2001. Schluter, Dolph. The Ecology of Adaptive Radiation. New York: Oxford University Press, 2000.

agriculture  Agriculture is the deliberate cultiva-

tion of plants or fungi by animals. Cultivation here refers to planting, care, and harvest. Agricultural plants and fungi are usually very different from wild plants and fungi; they have characteristics that allow them to be adapted to the agricultural system in which they live, useful to the animals that cultivate them, and poorly adapted to living in the wild. Agriculture is an example of mutualism, which confers benefits on both the agricultural plant or fungus and the animal that cultivates it. In agriculture, crops and the animals that cultivate them are mutually dependent. Agriculture has been, perhaps, the most significant component of human cultural evolution. More broadly defined, agriculture may include the care and use of livestock animals by other animals. Agriculture interacts with biodiversity in two ways: First, it has an impact upon biodiversity, as explained below, and second, it depends upon wild biodiversity as a source of new crops or genes, as explained in another entry.

Evolution of Agriculture Several species of ants carry out activities that bear striking parallels to human agriculture. Leaf-cutter ants (genera Atta and Acromyrmex) cultivate gardens of fungus (family Lepiotaceae). Massive foraging parties of leaf-cutter ants gather pieces of leaves from many species of tropical plants and carry them back to their nests. Leaf-cutter ants are the single most important source of herbivory in rain forest areas where they are abundant. The ants do not eat the leaves, which contain many toxins. Instead, they chew them up into compost, on which a kind of fungus grows and breaks down the toxins. The fungus grows nowhere else except in the mounds of leafcutter ants; when the ants disperse, they take fungus tissue with them. The ants eat fungus tissue and almost nothing else. Beneficial bacteria that grow on

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agriculture  the bodies of the ants produce chemicals that inhibit the growth of other bacteria in the compost. For this reason, some biologists consider these and other ants to be a promising source of new antibiotics. Because the ants deliberately prepare compost for the fungus and because of the mutual dependence of ants and fungus upon each other, the ant-fungus relationship can be considered an example of agriculture. Several species of ants in the seasonal tropics of Central America live on and in trees of the genus Acacia. The ants do not eat the leaves of the acacia. Instead, they consume nectar that is produced by glands on the stems (not in the flowers) of the trees, and they eat globules of protein and fat, called Beltian bodies, that grow on the tips of immature leaves. The ants chew out the insides of the acacias’ unusually large thorns and live inside the thorns. In some cases, experimental manipulation has shown the ants to be dependent upon the acacias for survival. The ants attack and kill other insects and drive away larger animals that attempt to feed on the acacias. When vines or other plants begin to grow in the immediate vicinity of the acacias, the ants chew them down. In most cases, the acacias are completely dependent upon the ants; when the ants are experimentally removed, vines overgrow the acacias, and animals browse the leaves heavily. The acacias remain green during the dry season, when most of the other trees lose their leaves, but these green targets go undisturbed by herbivores because of their protective ant army. Because the ants weed out other plants from the vicinity of the acacias and defend their crops and because of the mutual dependence of ant and acacia, the ant-acacia relationship can be considered an example of agriculture. Ant partnerships with other kinds of trees in the rain forests of Africa have evolved independently of the ant-acacia partnership. As natural selection favored the characteristics that allowed the partnerships of ants with fungi and ants with acacias, hybridization between these species and others closely related to them was unsuccessful. The result was the evolution of new species of fungi, acacias, and ants. In this way, agriculture has increased biodiversity. As the above examples illustrate, when agriculture evolved in the human species about 10,000 years ago, it was not the first time that agriculture had evolved on the planet. Hereafter, agriculture will refer to human agriculture. Some scholars once believed that agriculture was invented by a brilliant man in a tribal society of hunter-gatherers. Other scholars pointed out that since women gathered most of the plant materials, agriculture was probably invented by a woman. Both the brilliant man theory and the brilliant woman theory are incorrect, however, because agriculture

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9

could not have been invented in a single step by anyone. It had to evolve. Unmodified wild plants are unsuitable for agriculture. The following are four reasons for this. ●●

●●

●● ●●

The seeds of most wild plant species are dormant when they are mature; that is, when planted, the seeds will not germinate. Many require a period of exposure to cool, moist conditions before the inhibitors within the plant embryo break down and the seed germinates. If a brilliant man or woman planted the first agricultural seed from a wild plant, it would not have grown, and the person would have rightly concluded that agriculture was not a good idea. The seeds of many wild grains shatter or fall off the stem as soon as they are mature. Since natural selection generally favors seeds that disperse to new locations, shattering is beneficial to the plant, but it is extremely inconvenient for a human harvester. The seeds of many wild plant species contain toxins. The seeds of many wild grains are small.

Furthermore, the advantages of primitive agriculture would not have been immediately apparent to intelligent hunter-gatherers. Agriculture requires intense labor. Modern hunter-gatherers often barely eke out an existence in marginal habitats such as the Kalahari Desert of Africa or the Great Outback of Australia, but these are the habitats to which tribes and nations with more advanced tools have driven them. Before agriculture, many tribes lived in rich habitats in which hunting and gathering in many cases provided a comfortable level of existence. For these reasons also, agriculture had to evolve gradually. Agriculture originated separately in several parts of the world: at least twice in the New World (Central America and South America), in Mesopotamia, and in China. Agriculture may have had several separate origins in each of these areas, as well as in New Guinea. The only inhabited part of the world in which agriculture did not evolve was Europe; European agriculture was imported from the Middle East. Scientists and historians know that agriculture originated separately in these locations because the staple crops were different in each (see table on page 10). The domesticated sumpweeds and sunflowers grown by inhabitants of North America were replaced by Mexican maize and beans in pre-Columbian times. Agriculture began earliest (about 10,000 years ago) in the Middle East, especially in the TigrisEuphrates floodplain of Mesopotamia. It began there first apparently because there were many wild

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10 10 agriculture 

first entry

Centers and Times of Origin of Major Crop Plants* Time of Origin (years BP)

Center of Origin

Crop*

Eastern North America

Squash Sunflower Chenopod Marshelder

Mexico

Squash Maize Bean

10,000 9,000 4,000

Northern South America

Squash Arrowroot Yam Cotton Sweet potato Lima bean

10,000 9,000 6,000 6,000 4,500 6,500

Andes

Potato Quinoa

7,000 5,000

Central South America

Peanut Manioc Chili pepper

8,500 8,000 6,000

Africa

African rice Pearl millet Sorghum

2,000 3,000 4,000

Middle East

Rye Wheat Barley Fig

India

Mung bean Millet

4,500 4,000

China

Millet Rice

8,000 8,000

New Guinea

Yam Banana Taro

7,000 7,000 7,000

5,000 5,000 4,000 4,000

13,000 10,500 10,000 11,400

*Millet, squash, and yam are different species or varieties domesticated independently in different centers of origin. Note: From Balter

species of plants that were almost suited for agriculture. Of the 56 species of wild grains that have large seeds, 32 grow in the Middle East. These wild grains needed little evolutionary transformation to become crops. The transformation from gathering to agriculture would have been a relatively quick and easy process in the Middle East. At first, the gatherers unconsciously transformed wild into domesticated plants. Within each species

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of grain (such as wild wheat and wild barley), the largest seeds, the seeds that shattered the least, and the ones that tasted the best were what people preferentially gathered. The gatherers also would take grain seeds with them when they traveled and also may have cast them onto the ground in new locations. In this way, the seeds with the least dormancy were the ones most frequently chosen by the gatherers. Small, shattering, less palatable, dormant grains (the wild type) were thus gradually transformed, by unconscious natural selection and by deliberate artificial selection, into large, nonshattering, palatable, nondormant grains similar to today’s crops. A similar process occurred with other wild food plants. This same process occurred in all the other places where agriculture originated, but it took longer. There were fewer suitable wild food plants in Mexico and even fewer in the Andes. It took longer for wild teosinte to evolve into maize (see figure on page 11), as a greater evolutionary transformation was needed; it took even longer for poisonous wild potatoes to evolve into edible ones. Meanwhile, the human population was growing. By 10,000 years ago, all available favorable habitats were occupied by humans. Hunters and gatherers were much less free to move to a new location when resources became scarce. About the same time, the weather became cooler and drier in the Middle East. Hunting and gathering became a much less desirable way of life. When certain tribes then tried deliberate cultivation, it was worth the extra work, and the plants were suitable. Once agriculture had evolved, societies that depended upon it could not easily revert to hunting and gathering for several reasons: ●●

●●

Agriculture allowed greater food production and greater population growth. A large population could not revert to hunting and gathering. This is obvious today, for the Earth cannot support billions of hunters and gatherers, but it was also true in all local regions in which agriculture evolved thousands of years ago. Since agriculture allowed greater food production, it was no longer necessary for nearly all tribal members to participate in food procurement. Farmers raised enough food for everybody, which allowed other people to become soldiers and priests. A hunting, gathering tribe was ill equipped to fight an agricultural tribe with a dedicated army. A world trapped in agriculture was now trapped into war. Agriculture allowed the rise of religious and governmental hierarchies as well as armies.

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agriculture 

11

Native American farmers developed modern maize from wild teosinte grass by selecting for larger ears (which are clusters of female flowers).  (Nicole Rager Fuller, National Science Foundation)

●●

With the evolution of agriculture, productive farmland became valuable. People settled into cities because they had to stay in one place at least long enough for one harvest. Agriculture promoted the rise of civilization. Civilization rose earlier in Mesopotamia than in other places because agriculture began earlier there. With civilization came advanced technology. Because they needed to defend particular tracts of territory, the armies now had a lot more to fight about. The cultural groups that developed agriculture first were the first to be civilized and to have advanced technology that allowed them to conquer the cultural groups in which this process had not progressed as far. The biologist Jared Diamond explains that this is why Europeans conquered America and drove natives onto reservations, rather than Native Americans conquering Europe and driving Europeans into remote corners of the Alps and Pyrenees.

The evolution of agriculture is a perfect illustration that evolution does not operate for the good of the species. Agriculture evolved in the human spe-

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cies because it provided an advantage to some individuals within human societies. Agriculture did not improve the average health of human beings. In fact, the average life span in early agricultural societies was shorter than that in contemporaneous huntergatherer societies. This occurred for two reasons: ●●

●●

Diseases spread more rapidly in cities, in which people were trapped with one another’s wastes, garbage, and germs. Agriculture actually decreased the quality of human nutrition by making people dependent upon a few crop plants rather than a diversity of wild foods. In particular, the human body evolved under conditions in which ascorbic acid (vitamin C) was readily available from wild fruits. When entire populations became dependent upon crops with little vitamin C, scurvy became a way of life.

Herding began when people started to manage herds of wild animal species that were most amenable to survival and reproduction under captivity. Unconscious natural selection and then conscious artificial selection resulted in the evolution of livestock species such as the cow, which evolved in western Eurasia

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12 12 agriculture  and Southeast Asia from two distinct wild species. Once again, the earlier development of herding in the Middle East than in other areas occurred because many wild animal species of the Middle East such as goats and sheep were amenable to herding, whereas wild animal species such as deer in North America were not. Livestock animals provided high-quality food (meat and milk), often by consuming wild foods that humans could not eat. This was especially true of goats. Pigs, on the other hand, eat many of the same foods as humans. This competition between pigs and humans for food may be one reason that pigs are considered undesirable (“unclean”) by some cultures in the arid regions of the Middle East. As with agriculture, herding caused a narrowing of the food diversity base, from many wild animal species to a few livestock species.

Effects of Agriculture on Biodiversity of Natural Systems Agriculture has had several effects upon biodiversity, as indicated by the following examples. Escape of agricultural species into natural ecosystems. The result of agriculture has been the evolution of many new species of plants and animals that are adapted to human care and often cannot survive in the wild. In this sense, agriculture has created new biodiversity, even though crop species do not grow well in the wild. For example, since wheat (Triticum aestivum) and maize (Zea mays) do not have seed dormancy and do not shatter their seeds, they can usually survive only where they have been planted. However, crop species have contributed, in a largely negative way, to natural biodiversity because wild relatives of cultivated plants are frequent invaders of natural ecosystems. Examples include Johnson grass (Sorghum halepense), a relative of cultivated sorghum (S. bicolor), and wild oats (Avena fatua and A. barbata), relatives of cultivated oats (A. sativa). Hybridization between crops and wild relatives can produce new, aggressive strains of weeds. The ecologists Norm Ellstrand and Christina Schierenbeck have listed 28 examples. The new weeds are particularly hard to control since they so closely resemble the crops they infest. This same process may endanger some of the wild relatives also. Some varieties of wild maize in Mexico have been essentially hybridized out of existence. The use of GMO (genetically modified organism) crops became widespread in the 1990s. For some crops, such as soybean and cotton, most of the acreage consists of GMO breeds. Many GMO crops have wild relatives with which they can interbreed. For example, cultivated mustards such as canola (domesticated Brassica napus and B. campestris) can exchange pollen with wild mustard species. This raises the pos-

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first entry sibility that modern agriculture may introduce genetic changes, such as herbicide resistance or the production of compounds that are toxic to insect herbivores, into some wild populations. Wild, weedy mustards with leaves that are toxic to insects might undergo population explosions as a result of release from herbivore damage, and the herbivores might suffer a population crash. Such “genetic pollution” has occurred, but not yet on a large scale. Numerous domesticated animals have escaped into the wild. Livestock animals, though they have also been artificially selected to live under artificial conditions, can thrive under wild conditions. Though cows (Bos taurus) are not so well adapted to survival in the wild as were their wild ancestors, they may form extensive wild herds in grasslands from which natural predators such as wolves have been exterminated. The same is true of feral horses (Equus caballus) and donkeys (Equus asinus). Most animals that have been bred as pets are incapable of surviving in the wild, though dogs (Canis familiaris) and especially cats (Felis catus) have formed large and successful feral populations. Feral cats kill hundreds of millions of songbirds in the United States each year. These feral populations often lose some of their domesticated characteristics and quickly revert to the characteristics of their wild ancestors. Escaped livestock have had a particularly strong impact upon wild ecological communities. Most notorious are wild pigs and goats. Feral pigs (Sus scrofa), such as the razorbacks of the forests of the southeastern United States, trample and tear up woodlands and wetlands through which they wander in search of food. Wild pigs have caused extensive damage on islands with moist climate, such as the Hawaiian Islands, in which the plants have evolved no protection against grazing animals. Escaped goats (Capra aegagrus) have had an even more severe impact upon islands with dry climate, such as the Channel Islands of California and the Galápagos Islands of Ecuador, though they also thrive in moist climates. A population explosion of sheep (Ovis aries), since their introduction in about 1820, has transformed Tasmania, where plants that cannot grow back after grazing have been replaced by grasses that can in many areas. Destruction of natural habitats for agriculture. Large areas—perhaps a third of the dry land of Earth—have been transformed into farmland and pasture. As the human population grows, so will the demand for food. Expansion of agricultural land is not a good option to meet this demand, as most of the natural habitat that is suitable for agriculture has already been used. Most of what remains is too cold or too dry or has soil that is too poor for good agricultural production. Moreover, most of the pro-

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agriculture  duction of the principal crops in the United States is used to feed livestock. More people could be fed if farmland were used to raise food that people could eat rather than to raise livestock feed. The transformation of natural habitats into agricultural land has caused the extinction of many tropical plant and animal species that formerly had very limited ranges; several species of wild plants and animals can be driven to extinction by the development of a single oil palm plantation. Temperate zone plant and animal species generally have greater geographical ranges, and extinctions as a result of agriculture in this zone are less common. Nevertheless, agriculture, like urban sprawl, has brought about the fragmentation of natural ecosystems and a reduction in the size and genetic diversity of wild populations. Agriculture need not have such a negative impact on biodiversity. Hedgerows of shrubs and trees around small agricultural fields provide habitat for predatory birds, bats, spiders, and insects that prey upon insect pests. These predators may not venture out into the middle of large fields because other predators may detect and eat them, or they may simply be killed by insecticides. An agricultural landscape of small fields surrounded by hedgerows will have a much greater biodiversity (and require fewer pesticides) than will large fields devoted to one species of crop. Organic agriculture uses hedgerows and natural pest control. Because they use natural rather than chemical fertilizers, organic farms also have richer soil, which enhances the diversity of soil organisms, including insects and earthworms. Impact of agriculture on natural ecosystems. Agriculture is not simply the replacement of one type of habitat by another. Agricultural fields are usually a monoculture of a single crop, perhaps just a single breed of crop. The animals that live in these monocultures are also less diverse and consist primarily of insect pests of the crops. Monocultures encourage the spread of pests and diseases. This has two effects. First, some of these pests, such as grasshoppers and locusts, can grow into swarms that result in the defoliation of nearby natural ecosystems. Second, monocultures require heavy applications of chemicals to control the pests. All the plants in the field use the same nutrients from the same soil depth, which requires increased dependence on chemical fertilizers. Monoculture also encourages erosion of the soil by wind and water. Because most crops are annuals, large fields are left barren during the nonproductive season. Mainstream agriculture is considered a “highinput” system because a lot of energy and chemicals are necessary. Many of these chemicals pollute surrounding ecosystems. Fertilizer from farms, particularly phosphate, is a major contributor to the

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13

explosive growth of cyanobacteria in streams and lakes, resulting in eutrophication, which greatly alters the food chain of such wetland ecosystems. The decomposition of dead cyanobacteria contributes to oxygen depletion in wetlands and on ocean bottoms. The huge feedlots used for livestock produce as much sewage as do human cities, and much of this waste also contributes to pollution and eutrophication. The writer Wendell Berry compared preindustrial agriculture, in which animal wastes fertilized the fields, with industrial agriculture, in which crops are raised with artificial fertilizers, while animal wastes become a source of pollution. Industrial agriculture, he said, has taken a solution and divided it into two problems. Many of the environmental problems of modern agriculture can be avoided by increasing the diversity of crops and by the use of perennial rather than annual crops. The fact that leguminous crops, such as beans and alfalfa, benefit soil fertility has been known since the time of the Roman writer Virgil. Leguminous crops have nitrogen-fixing bacteria in their roots and can actually enrich the soil with nitrogen fertilizer rather than depleting it. Terraces, used for millennia in East Asia for rice production, not only reduce soil erosion but also allow organic matter in the soil to accumulate, thereby enriching it. Crop rotations, or rotations involving both crops and livestock, also avoid many environmental problems. Fred Kirschenmann, director of the Aldo Leopold Center at Iowa State University, has shown that crop rotations in organic agriculture can be successful on a large scale. On a large farm in North Dakota, Kirschenmann grows durum wheat, rye, flax, sunflower, buckwheat, and oats. He uses alfalfa and two species of sweet clover as cover crops and has organic pasture. He alternates warm with cool season crops and cereals with broadleaf crops, thus avoiding buildup of pests. By rotating shallowrooted with deep-rooted crops, he avoids depleting the soil layers. Crop rotation often means that the farmer must give up a marketable crop yield for one year in four while cover crops grow, but lower chemical and energy costs compensate for this loss. The writer Michael Pollan describes the example of Argentina, where the agricultural industry raises cattle on grassland for five years, followed by a three-year production of grains or beans. The grassfed cattle produce high-quality beef, and the cattle wastes provide fertilizer for the crops. Insect pests are a relatively small problem, since the insects that attack the crops cannot survive in pastures. Many GMO crops have been bred to resist herbicides. In the past, a farmer could not spray herbicide over a whole field because it would kill the crops as well as the weeds, but now an extensive application

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14 14 agriculture 

first entry ers, wholesalers, retailers, processors, packagers, transporters, and the manufacturers and salesmen of machines, building materials, feeds, pesticides, herbicides, fertilizers, medicines, and fuels.  .  .  . [And they] are all dependent on the petroleum industry.

A sign in Kansas boasts of the efficiency of modern agriculture. However, modern agriculture, being utterly dependent on fossil fuels, is very inefficient in its use of energy.  (Stanley A. Rice)

of herbicide will kill only the weeds. The result has been a vast increase in the use of herbicides, which can spread into surrounding natural ecosystems. Effects of agriculture on global climate. Agriculture is one of the major sources of greenhouse gases. A tremendous amount of fossil fuel is used in modern systems of food production, from the production of fertilizers and pesticides, to the use of farm equipment, to the processing of food. When soil is left bare following the harvest of annual crops, decomposition can release carbon dioxide into the atmosphere that was previously sequestered in the humus. Agriculture may also be the major source of atmospheric methane, another greenhouse gas. Flooded soils, such as rice paddies, and the digestive systems of cows produce a lot of methane. The tremendous agricultural production of greenhouse gases need not occur. Plants can be considered a way of removing carbon dioxide from the air and storing it in the soil as leaves, stems, and roots die and decompose into humus. Agriculture based on perennials can store carbon in the soil rather than releasing it. Modern agriculture might appear to be very efficient (see figure). However, it is efficient only in terms of the amount of food produced per farmer. In every other way, it is wasteful. By some calculations, only 4 percent of Americans are farmers or farmworkers, but, as the writer Wendell Berry explains .  .  . the four percent of our population that is left on the farm does not, by any stretch of imagination, feed the rest. That four percent is only a small part, the worst-paid part, of a food production network that includes purchas-

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For this reason, agriculture puts a lot of carbon dioxide into the atmosphere. In addition to being environmentally destructive, modern agriculture is also precarious, because it is dependent on the uninterrupted availability of inexpensive fossil fuels. For numerous environmental and economic reasons, humans need to change the way they raise their food. See also biodiversity, resources for agriculture; biodiversity, resources for medicine; greenhouse effect; habitat fragmentation; invasive species. Further Reading Baker, Herbert G. Plants and Civilization. Belmont, Calif.: Wadsworth, 1970. Balter, Michael. “Seeking agriculture’s ancient roots.” Science 316 (2007): 1,830–1,835. Berry, Wendell. Bringing It to the Table: On Farming and Food. Berkeley, Calif.: Counterpoint, 2009. Diamond, Jared. Guns, Germs, and Steel: The Fates of Human Societies. New York: Norton, 1997. Dutton, A., et al. “Prey-mediated effects of Bacillus thuringiensis spray on the predator Chrysoperia carnea in maize.” Biological Control 26 (2003): 209–215. Ellstrand, Norman. Dangerous Liaisons? When Cultivated Plants Mate with Their Wild Relatives. Baltimore, Md.: Johns Hopkins University Press, 2003. ———, et al. “Gene flow and introgression from domestic plants into their wild relatives.” Annual Review of Ecology and Systematics 30 (1999): 539–563. ———, and Kristina A. Schierenbeck. “Hybridization as a stimulus for the evolution of invasiveness in plants?” Proceedings of the National Academy of Sciences USA 97 (2000): 7,043–7,050. Foster, Nelson, and Linda S. Cordell, eds. Chilies to Chocolate: Food the Americas Gave to the World. Tucson: University of Arizona Press, 1992. Glover, Jerry D., Cynthia M. Cox, and John P. Reganold. “Future farming: A return to roots?” Scientific American 297 (2007): 82–89. ———. “Harvested perennial grasslands: Ecological models for farming’s perennial future.” Agriculture, Ecosystems and Environment 137 (2010): 1–2. ———, and John P. Reganold. “Perennial grains: Food security for the future.” Issues in Science and Technology, Winter 2010, 41–47. Harlan, Jack R. The Living Fields: Our Agricultural Heritage. New York: Cambridge University Press, 1995.

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amphibians  Heiser, Charles B. Seed to Civilization: The Story of Food. Cambridge, Mass.: Harvard University Press, 1990. Hobhouse, Henry. Seeds of Change: Five Plants that Transformed Mankind. New York: Harper and Row, 1986. International Society of Organic Agriculture Research. “International Society of Organic Agriculture Research.” Available online. URL: http://www.isofar. org. Accessed August 8, 2011. Jordan, N., et al. “Sustainable development of the agricultural bio-economy.” Science 316 (2007): 1,570–1,571. Land Institute. “The Land Institute.” Available online. URL: http://www.landinstitute.org. Accessed May 1, 2010. Leopold Center for Sustainable Agriculture, Iowa State University. “Welcome to the Leopold Center.” Available online. URL: http://www.leopold.iastate.edu. Accessed August 8, 2011. Local Harvest. “Local Harvest.” Available online. URL: http://www.localharvest.org. Accessed August 8, 2011. Lu, Yanhi, et al. “Mirid bug outbreaks in multiple crops correlated with wide-scale adoption of Bt cotton in China.” Science 329 (2010): 1,151–1,154. Marvier, M., and R. Van Acker. “Can crop transgenes be kept on a leash?” Frontiers in Ecology and the Environment 3 (2005): 93–100. Natural Resource Conservation Service, United States Department of Agriculture. “Plants database.” Available online. URL: http://www.plants.usda.gov. Accessed May 1, 2010. Pilson, D., and H. Prendeville. “Ecological effects of transgenic crops and the escape of transgenes into wild populations.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 149–174. Pollan, Michael. The Omnivore’s Dilemma: A Natural History of Four Meals. New York: Penguin, 2006. ———. “Farmer in chief.” New York Times Magazine, October 12, 2008. Rice, Stanley A. “How agriculture changed the world.” Chapter 10 in Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Rindos, David. The Origins of Agriculture: An Evolutionary Perspective. San Diego: Academic Press, 1984. Salaman, Redcliffe. The History and Social Influence of the Potato. New York: Cambridge University Press, 1949 (reissued 1985). Simpson, Beryl Brintnall, and Molly Conner Ogorzaly. Economic Botany: Plants in Our World. New York: McGraw-Hill, 1995. Snow, Allison A., et al. “A Bt transgene reduces herbivory and enhances fecundity in wild sunflowers.” Ecological Applications 13 (2003): 279–286. Stotzky, G. “Persistence and biological activity in soil of the insecticidal proteins from Bacillus thuringiensis, especially from transgenic plants.” Plant and Soil 266 (2004): 77–89.

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amphibians  Amphibians are vertebrates that

live in aquatic environments during their juvenile phase and usually on land during their adult phase. Amphi is Greek for “both” and bio is Greek for “life.” Frogs undergo the most dramatic metamorphosis among the vertebrates, from herbivorous tadpoles with tails and gills to carnivorous adults with lungs and legs. They also undergo changes in physiological adaptation. In adult frogs, as in most vertebrates, hemoglobin releases oxygen into tissues under acid conditions that result from muscular exertion, but many tadpoles live in acidic water. They have a type of hemoglobin that absorbs, rather than releases, oxygen under acidic conditions, thus allowing them to absorb oxygen from the acidic waters in which they live.

Evolution of Amphibians Amphibians are one of the lineages that evolved from the fleshy-finned (sarcopterygian) fishes. During the middle Paleozoic era, there were many animals that were intermediate between sarcopterygian fishes and modern amphibians. Most of these “missing link” fish-amphibians were members of lineages that became extinct. All modern amphibians evolved from one amphibian lineage, for which fossils may or may not have been found. The fossils demonstrate, however, that there were many examples of the transition from fish to amphibian during the Paleozoic. Numerous transitional forms have been discovered from the Devonian and Carboniferous periods, including the following. Eusthenopteron foordi was a sarcopterygian fish that lived in the late Devonian period. It had all the same fins that modern sarcopterygian fishes still possess, rather than hands or feet. At the bases of the fins, it had bones analogous to the arm and leg bones of terrestrial vertebrates. Eusthenopteron had no bones that corresponded to the digits of modern tetrapods. Even though it did not have lungs and did not breathe air, it had nostrils, which perhaps allowed water to flow over olfactory cells and may have enhanced the sense of taste. This organism looked very much like an ordinary sarcopterygian fish, and it probably spent nearly all of its time in shallow water. Panderichthys rhombolepis was another sarcopterygian fish that lived during the late Devonian period. It lacked some of the fish fins and had thicker ribs than fishes possess. The thicker ribs were important in supporting the weight of the body when on land and away from the buoyancy of water. However, lacking legs, this species must have spent nearly all of its time in water. Tiktaalik roseae created a sensation in the world of science when the evolutionary biologist Neil Shubin announced its discovery in 2004. He called it a

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first entry

allow rapid movement on land, and they probably spent most of their time in shallow water, as do many amphibians and reptiles today. in fishes, the hyomandibular bone helps to support the gills; this bone corresponds to the stapes, the ear bone of tetrapods (the innermost ear bone of mammals). the stapes of Acanthostega has been found, and it resembles a fish hyomandibular bone. it was not free to vibrate and therefore could not have functioned in hearing on land. later amphibians, in the carboniferous period, had stapes that functioned in hearing. By the early carboniferous Tiktaalik roseae, discovered in 2006 by the biologist Neil Shubin and period, there were many differassociates, was an early amphibian called a “fishapod” that had nearly ent amphibian lineages. all have an equal mix of fish and amphibian characteristics. become extinct except for two: the branch that led to modern “fishopod” because it was almost directly intermeamphibians, and the branch that led to modern diate between fishes (such as Eusthenopteron and reptiles. Panderichthys) and tetrapods (such as Ichthyostega there has been debate regarding the reasons and Acanthostega, see below). its name derives from for the evolution of legs in the transitional forms a word in the language of the nunavat, the native between fishes and amphibians. Suggestions include peoples who live on ellesmere island, where the fosthe following. sil was discovered. Tiktaalik’s fishlike characteristics ● One early proposal was that fi shes had included (see figure above). to walk on land to get from one pond to ● it had gills. another if their home pond began to dry up. ● it had scales. there are fishes today that crawl on land ● it had no fi ngers. and even climb trees entirely without legs. ● Modern salamanders have legs, yet many Tiktaalik’s intermediate characteristics included: of them live underwater. they use their legs for walking underwater on rock surfaces ● its shoulder partially resembled that of later against the current. it is possible that the amphibians, permitting it a limited ability to fi rst legged amphibians evolved in rushing move its legs in a walking fashion. water. ● it had partly amphibian wrist and elbow ● Recent analyses suggest that legs were more bones, which allowed it a limited ability to useful for lifting the earliest amphibians support its weight with its fi ns. above the water to watch for predators than for efficient walking. Tiktaalik’s amphibian characteristics included: ● the evolutionary biologist Robert a. Martin suggests that legs assisted in clasping ● it had amphibian ribs, necessary for supduring sexual reproduction, a function they porting its body weight outside of water. still possess in many modern amphibians. ● it could move its neck, which fish cannot do. ● it had lungs that were like those of amphibit is probable that legs proved useful for several ians, not lungfishes. different functions over a long period of time. Whatever combination of advantages may have selected Ichthyostega stensioei and Acanthostega gunfor the evolution of legs, it had to be something nari had more adaptations for life on land than that worked in a primitive condition. the earliest did Tiktaalik. they had hands and feet with fi namphibians with legs could scarcely lift themselves at all. gers. their ribs were thicker. their anatomy did not

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amphibians  The evolution of limbs would not require the acquisition of many new genes. Hox genes control the pattern of body part development in most animals. Some of these hox genes (numbers 9 to 13) control limb development in mice, from shoulder to feet. Analogs of these genes are found in all vertebrates. Activation of specific hox genes can produce limbs; evolution would then work out the structural details of these limbs, rather than produce them from scratch. While the arm and leg bones have analogs in some fishes, digits were an amphibian invention. The earliest tetrapods had more than five digits (Ichthyostega had seven and Acanthostega had eight). All surviving tetrapods have a five-digit fundamental pattern, even though some, such as horses, have lost the ability to produce all five of them. In addition to the “missing links” between fishes and amphibians, amphibians (as their name implies) are themselves intermediate between fishes and fully terrestrial animals.

Diversity of Amphibians There are more than 6,000 species of amphibians (see table). Amphibians include caecilians, salamanders, and frogs. Caecilians are legless tropical amphibians that burrow through soil. Both larval and adult salamanders have four legs, all about the same size, and tails. Adult frogs have large jumping hind legs and external eardrums but do not have tails. Amphibians, like other groups of vertebrates, vary greatly in size. The smallest salamander (in the genus Thorius) is only an inch (2.5 cm) long, while the largest are Asiatic salamanders (genus Andrias), which are up to 5.5 feet (1.7 m) long and can weigh 88 pounds (40 kg). Frogs are generally small. The largest is the goliath frog (Conraua goliath), which can reach 13 inches (33 cm) in length and weigh eight pounds (3 kg). Amphibians have some amazing adaptations to their environments. Frogs can leap for great distances. Some frogs can jump almost 30 feet (9 m).

Estimated Number of   Amphibian Species Group

Number of Species

Anurans (frogs)

5,892

Caecilians

186

Salamanders

586

Total *Note: From Amphibiaweb.org

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6,664

17

Frogs keep their tongues folded inside their mouths, with the tip pointing backwards. Their tongues can extend almost as long as their bodies to catch flying insects. Their sticky tongues capture the insects, which they swallow whole; the small teeth, present only in the upper jaw, serve little function. Caecilians have a unique sensory structure, called a tentacle, which develops from the eyes and nose. Amphibians are important components of aquatic ecosystems. Both as juveniles and adults, they eat a lot of invertebrates. Their main protection comes from either camouflage or from its opposite, a bright display of color that indicates poisonous skin. Many colorful salamanders produce large amounts of tetrodotoxin in their skins and are among the most toxic animals known. “Poison dart” frogs of many species also have colorful skin in which poison glands produce venom (see figure on page 18). Examples include batrachotoxin, epibatidine, histrionicotoxin, and pumiliotoxin. Most frogs are nocturnal, but poison dart frogs are most visible, and thus safest, during the day. In some frogs, such as the Colorado River toad, Bufo alvarius, the poison is not deadly and is used as a recreational hallucinogen by some people. The poison compounds in amphibian skins have already proven to be of medical importance. Researchers at Abbott Labs used a poison in the skin of a tree frog from the Ecuadorean Amazon rain forest, Epipedobates tricolor, as a model for the development of a new painkiller. These rain forests are among the most threatened habitats on Earth, and amphibians are among the most threatened species that live in them. Captive poison dart frogs do not generate poison because they do not synthesize it themselves; they concentrate it from their prey animals, such as centipedes and ants. Juvenile amphibians (such as the tadpoles of frogs) obtain oxygen from water and release carbon dioxide into water through their gills. In contrast, most adult amphibians breathe with lungs and are therefore at least partly adapted to life on dry land. Salamander larvae have external gills. Adult frogs and most adult salamanders lose their gills and develop lungs, but they still rely heavily on oxygen uptake through their soft skins. Most amphibians, even as adults, must live in moist environments. Most have skins that cannot resist desiccation. The skins of some toads resist water loss. The adults of some Australian and North American frogs can survive for years in the desert, dormant and underground. Amphibians neither generate very much body heat nor regulate their body temperatures. Therefore, they are both ectothermic (from the Greek for “heat from outside”) and heterothermic (signifying variable body heat).

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18 18 amphibians 

first entry sexually mature while they are still larvae. Injection of thyroid hormones can cause an axolotl to develop into an adult form that has never been encountered in the wild. This experiment allowed the evolutionary biologist Julian Huxley to describe how neoteny (retention of juvenile characteristics during sexual maturity) can lead to the evolution of new species.

Extinctions of Amphibians All around the world, populations of many amphibian species have declined precipitously. The following are factors that are directly threatening the survival of amphibians, especially adult frogs. ●●

Many tropical frogs, such as this blue poison dart frog (Dendrobates azureus), have brightly colored skin that functions as a warning that it contains toxins.  (Adrian Pingstone)

Juvenile amphibians release ammonia as a waste product. Ammonia is toxic, but the water washes the ammonia away. In contrast, many landdwelling adult amphibians produce urea, which is less toxic than ammonia. Wastes from kidneys and intestines are voided together with gametes through a cloaca. Most adult amphibians return to the water to lay and fertilize eggs. Amphibian eggs dry out quickly unless kept in moist conditions. Though most amphibians keep their eggs moist by depositing them underwater, some species brood their eggs in a pouch or inside their bodies. Even desert amphibians require an aquatic environment for reproduction. They emerge from underground dormancy only during a rainy season, mate, and lay eggs. Their juveniles grow rapidly and reach adulthood before the pools of water dry up. Some species of amphibians have external fertilization, while in others the males clasp the females while eggs and sperm are released. In some, the males leave sperm on a structure that the females take into their cloacae. In others, the males and females press their cloacae together to achieve internal fertilization. Although most amphibians have an aquatic juvenile and terrestrial adult phase, there is some variation in this pattern. All frogs go through a larval stage, but some of them, such as the Puerto Rican tree frog Eleutherodactylus coqui, do so before the eggs hatch, with the result that adult frogs emerge from the mother. Plethodont salamanders also do this. Some salamander species, such as the mudpuppy Necturus maculosus and the axolotl Ambystoma mexicanum, are famous for becoming

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●● ●●

●●

The direct cause of most population declines has been funguslike protists that live in the skins and produce toxins. The chytrid protist Batrachochytrium dendrobatidis grows in the skins of tree frogs. By upsetting cellular salt balance, toxins from the pathogen cause cardiac arrest in the frogs. Saprolegnia ferax is another chytrid that kills frogs. Other parasites, such as the trematode worm Ribeiroia ondatrae, cause deformities in frogs. Chytrid parasites may have been introduced into susceptible populations by toads that escaped from experimental laboratories, because the common laboratory toad Xenopus laevis is a symptomless carrier. In some cases, amphibians are threatened by invasive fishes that eat their larvae. Global warming can cause changes in climate that lead to amphibian extinction. The golden toad (Bufo periglenes) may have become extinct because climate change has caused the cloud forests in which it lived to not be wet enough. Frogs also have very permeable skin, which makes them vulnerable to pollutants such as glyphosate and atrazine. These herbicides are very toxic to amphibians at far below the recommended level of agricultural use. Atrazine causes frogs to develop hermaphroditism at a concentration a thousand times less than is commonly found in farm runoff water and 400 times less than is found in some rainwater in agricultural areas. Their thin skin also makes frogs vulnerable to environmental threats such as acid rain and ultraviolet radiation.

What has become apparent is that these threat factors interact. Pollutants, ultraviolet light, and acid rain may make the amphibians more susceptible to protist and other parasite infections. It is

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animals  the interaction of pollution and parasites that is threatening so many species of amphibians. Global warming is also contributing to this interaction. For example, the spread of Batrachochytrium has been enhanced by warmer temperatures. Amphibians today are facing a rate of extinction greater than they endured during the two largest mass extinctions in the past: the Permian extinction and the Cretaceous extinction. See also biodiversity, resources for medicine; camouflage and mimicry; Carboniferous period, biodiversity in; Devonian period, biodiversity in; fishes; mass extinctions; parasitism; pollution; reptiles. Further Reading Amphibiaweb. “Amphibiaweb.” Available online. URL: http://www.amphibiaweb.org. Accessed August 8, 2011. Bank, M. S., et al. “Mercury bioaccumulation in northern two-lined salamanders from streams in the northeastern United States.” Ecotoxicology 14 (2005): 181–191. Beebee, T. J. C. “Amphibian breeding and climate.” Nature 374 (1995): 219–220. Berger, L., et al. “Chytridiomycosis causes amphibian mortality associated with population declines in the rain forests of Australia and Central America.” Proceedings of the National Academy of Sciences USA 95 (1998): 9,031–9,036. Blauenstein, A. R., et al. “UV repair and resistance to solar UV-B in amphibian eggs: A link to population declines.” Proceedings of the National Academy of Sciences USA 91 (1994): 1,791–1,795. ———, et al. “Ultraviolet radiation, toxic chemicals, and amphibian population declines.” Diversity and Distributions 9 (2003): 123–140. Callery, Elizabeth M. “Frogs without polliwogs: Evolution of anuran direct development.” BioEssays 23 (2001): 233–241. Chivian, Eric, and Aaron Bernstein. “Threatened groups of organisms valuable to medicine: Amphibians.” In Sustaining Life: How Human Health Depends on Biodiversity, edited by Eric Chivian and Aaron Bernstein, 204–223. New York: Oxford University Press, 2008. Clack, Jennifer. Gaining Ground: The Origin and Evolution of Tetrapods. Bloomington, Ind.: Indiana University Press, 2002. ———. “From fins to limbs.” Natural History (July 2006): 36–41. Coates, Michael I., et al. “Ever since Owen: Changing perspectives on the early evolution of tetrapods.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 571–592. Daeschler, Edward B., Neil H. Shubin, and Farish A. Jenkins, Jr. “A Devonian tetrapod-like fish and the evolution of the tetrapod body plan.” Nature 440 (2006): 757–763.

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Davic, Robert D., and Hartwell H. Welsh, Jr. “On the ecological roles of salamanders.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 405–434. Dupuis, L. A., et al. “Relation of terrestrial-breeding amphibian abundance to tree-stand age.” Conservation Biology 9 (1995): 645–653. Feder, M. E., and W. W. Burggren, eds. Environmental Physiology of the Amphibians. Chicago: University of Chicago Press, 1992. Hall, Brian K., ed. Fins into Limbs: Evolution, Development, and Transformation. Chicago: University of Chicago Press, 2007. Hayes, T. B., et al. “Hermaphroditic, demasculinized frogs after exposure to the herbicide atrazine at low ecologically relevant doses.” Proceedings of the National Academy of Sciences USA 99 (2002): 5,476–5,480. LaMarca, E., et al. “Catastrophic population declines and extinctions in neotropical harlequin frogs (Bufonidae: Atelopus).” Biotropica 37 (2005): 190–201. Lips, K. R., et al. “Emerging infectious disease and the loss of biodiversity in a neotropical amphibian community.” Proceedings of the National Academy of Sciences USA 103 (2006): 3,165–3,170. Myers, C. W., et al. “A dangerously toxic new frog (Phyllobates) used by Emberá Indians of western Colombia, with discussion of blowgun fabrication and dart poisoning.” Bulletin of the American Museum of Natural History 161 (1978): 307–366. Petranka, J. W., et al. “Effects of timber harvesting on southern Appalachian salamanders.” Conservation Biology 7 (1993): 363–377. Pierce, B. “The effects of acid precipitation on amphibians.” Ecotoxicology 2 (1993): 65–77. Pounds, J. A., et al. “Widespread amphibian extinctions from epidemic disease driven by global warming.” Nature 439 (2006): 161–167. Stuart, S. N., et al. “Status and trends of amphibian declines and extinctions worldwide.” Science 306 (2004): 1,783–1,786. Voyles, Jamie, et al. “Pathogenesis of chytridiomycosis, a cause of catastrophic amphibian declines.” Science 326 (2009): 582–585. Vredenburg, V. T. “Reversing introduced species effects: Experimental removal of introduced fish leads to rapid recovery of a declining frog.” Proceedings of the National Academy of Sciences USA 101 (2004): 7,646–7,650.

animals  Animals are multicellular eukaryotes

that consume other organisms or molecules produced by them and that are usually motile at some stage of their lives. Animals (kingdom Animalia) are one of four kingdoms within the domain Eucarya (eukaryotes). Animals differ from the other eukaryotic kingdoms in ways such as the following:

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20 20 animals ●

● ● ●

animals, unlike animal-like protists, are not only multicellular but organized into tissues and organs. animals, unlike animal-like protists, develop from a single fertilized egg. animals, unlike plants, never use photosynthesis or have cellulose cell walls. animals, unlike fungi, never have dikaryotic cells or chitin cell walls.

animals also have a sexual life cycle that contrasts with almost all plants and fungi. in plants and fungi, meiosis produces spores, which grow into multicellular haploid structures (the mycelia of fungi and the gametophytes of plants). in animals, meiosis directly produces gametes, which are eggs and sperm. an animal develops from a single fertilized egg. in some cases, development from a fertilized egg is almost the only evidence that an organism is an animal rather than a protist. the protists that are most closely related to animals are the choanoflagellates, which form small clusters of cells that resemble the choanocytes of sponges. the earliest animals may have been choanoflagellatelike cells that formed clusters that resembled the blastula stage of embryonic development. From the human viewpoint, animals have been classified as invertebrates and vertebrates based on the absence or presence of bony vertebrae surrounding the main nerve cord along the dorsal (back) surface of the body. all the phyla of animals except the chordates are invertebrates; even the chordate phylum contains some invertebrates. “invertebrate,” therefore, is not a taxonomic category. the animal kingdom is traditionally divided into phyla. there are 35 phyla currently recognized in the animal kingdom. it appears that all animal phyla evolved more than 540 million years ago, at which time all organisms still lived in the sea; no new animal phyla have arisen since.

first entry etons. Buoyancy supports the weight of aquatic animals, but terrestrial animals need skeletons to hold them up. arthropods have external skeletons, and vertebrates have internal skeletons. Most animal phyla are fully aquatic, have little or no protection against drying out, and are unable to tolerate terrestrial conditions unless they live in moist soil or inside the bodies of other animals. Body structure. animals can be distinguished by their types of symmetry. animals in four of the phyla are either too simple to have any recognizable symmetry or are asymmetrical. animals in some phyla have radial symmetry, while in others they have bilateral symmetry. the organs of radially symmetric animals (such as jellyfish) are arranged outward from a central point; there is no front or rear, left or right, though there may be a top and bottom (see figure). the organs of bilaterally symmetric animals, such as humans, are paired left and right along an axis from front to rear. they have dorsal (back) and ventral (belly) surfaces. Many bilaterally symmetrical animals, such as earthworms, have segmentation, repeating units from front to rear, sometimes with the same organs in each segment. Some animals have a tissue-lined body cavity (coelom), which contains the internal organs, and some do not (acoelomate). Circulation and respiration. Many animals are so small and simple that they do not have circulatory or respiratory systems. the ratio of external surface to internal volume is so great that they can

Body formS aNd adapTaTIoNS Scientists distinguish among animals in numerous ways, including the following: Habitat. Many animals live only in the oceans or in freshwater. in order to survive and reproduce on land, animals require Animals with radial symmetry (left) have a front and back side but radiate protection from water loss and equally in all directions. Animals with bilateral (“two-sided”) symmetry support structures such as skel- (right) have a front and back, top and bottom, and left and right sides.

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animals  absorb and release molecules from and to the environment. Many animals, (for example, the arthropods) have open circulatory systems, in which the blood is pumped through a system of vessels that are open at both ends. The blood bathes the internal organs. Other animals (such as vertebrates and some mollusks, such as the squid) have closed circulatory systems, in which blood flows through a network of closed blood vessels throughout the body. Many aquatic animals obtain oxygen from moist environments by means of gills, which are thin flat layers of tissue through which oxygen can diffuse into the body from the environment. Some animals, such as spiders and terrestrial vertebrates, have lungs, in which the oxygen exchange surfaces are internal rather than external, like gills. Many insects breathe by means of tracheae, a network of air vessels that penetrate their bodies. Sexual reproduction and life cycles. All terrestrial animals have internal fertilization, in which one individual transfers sperm to another without allowing the sperm to dry out and die. Many aquatic animals also have internal fertilization. Some aquatic animals, however, have external fertilization, in which sperm and eggs are released into the water, where fertilization occurs. Some animals also reproduce asexually. The eggs of terrestrial animals allow them to survive on land. For example, the wax and protein covering of an insect’s egg and the calcium shell of a bird’s egg let in oxygen but prevent the loss of water. Many animals, such as butterflies and many amphibians, have complex life cycles in which an individual progresses through very different developmental stages. In these cases, the adults may differ radically in body structure from the juveniles. In other animals, such as grasshoppers and mammals, the juveniles are similar in body structure to the adults.

Overview of Animal Diversity The 35 phyla of animals are presented in the table. Below is a review of the major groups of animals except for the arthropods and vertebrates, which have their own encyclopedia entries. They are presented in a roughly evolutionary order, beginning with those that appear to have undergone the least change since the Cambrian period. This is what is meant by primitive. Most of the animal phyla have been recognized for centuries, but some have been discovered only recently, or their distinctiveness has only recently been recognized. The phylum Loricifera was not recognized until 1983. Until 1994, the one species in the phylum Micrognathozoa was assumed to be just be a type of rotifer. One of only three known species of the phylum Cycliophora was discovered in 1994 on the mouth parts of a lobster.

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21

Estimated Number of Species in the 35 Phyla of Animals Phylum Name

Common Name

Number of Species

Acanthocephala

thorny-headed worms

1,100

Annelida

segmented worms

16,500

Arthropoda

arthropods

more than 1,130,000

Brachiopoda

brachiopods

335

Chaetognatha

arrow worms

125

Chordata

chordates

100,000

Cnidaria

coelenterates

11,000

Ctenophora

comb jellies

100

Cycliophora

cycliophorans

3

Echinodermata

echinoderms

7,000

Echiura

spoon worms

140

Ectoprocta

bryozoans

4,500

Entoprocta

goblet worms

150

Gastrotricha

hairy back worms

690

Gnathostomulida

jaw worms

100

Hemichordata

acorn worms

85

Kinorhynchia

kinorhynchs

150

Loricifera

loriciferans

10

Micrognathozoa

micrognathozoans

1

Mollusca

mollusks

93,000

Myxozoa

myxozoans

3

Nematoda

roundworms

25,000

Nematomorpha

horsehair worms

320

Nemertea

ribbon worms

900

Onychophora

velvet worms

110

Oronectida

oronectids

20

Phoronida

horseshoe worms

20

Placozoa

placozoans

1

Platyhelminthes

flatworms

20,000

Porifera

sponges

5,500

Priapula

penis worms

16

Rotifera

rotifers

1,800

Sipuncula

peanut worms

300

Tardigrada

water bears

800

Xenoturbellida

xenoturbellids

2

Total

more than 1,420,000

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22 22 animals

first entry

aSymmETrICal aNImalS

mineral. the skeletal protein of some sponges is similar to the collagen found in vertebrate bones and cartilage. in addition, many sponges have spicules, crystallike mineral structures, which contain either calcium carbonate (the same kind of lime found in the hard parts of many invertebrates) or silicon. the skeleton gives support, and spicules make the sponge a very spiny mouthful for predators. Specialized cells secrete the skeletal materials. the skeleton is all that is left of the sponge when it has been cleaned and dried for humans to use. Processed sponges hold much water because their skeletons form many thousands of tiny passageways. Sponges are fi lter feeders. they obtain food by fi ltering small food particles from the water in which they live. Feeding cells, known as choanocytes, have flagella and line most of the internal passages of sponges. these cells move massive amounts of water through the passageways by beating their flagella in the same direction, causing water to move in one direction—in through pores all along the sides of the sponge, through the thousands of passageways, into a large central tunnel, and out through a chimneylike structure at the top (see figure). Since sponges have no nerves, the coordination, even synchronicity, with which choanocytes beat their flagella is an emergent property in which the cells respond to one another. cells obtain oxygen and ingest food particles from the water that flows through these passages. For the most part, each cell of a sponge is on its own for obtaining food. the diversity of asymmetrical shapes in sponges helps to increase their surface area, making fi lter feeding more efficient. this is not the only way that sponges obtain food, however. Many sponges contain symbiotic cyanobacteria within their tissues. these cyanobacteria absorb light directly with green chlorophyll and indirectly with a red pigment that transfers the light energy to chlorophyll. the red pigment absorbs blue light. these pigments give sponges a variety of hues. Sponges come in many Sponges (phylum Porifera) draw water through pores, filter food particles from the water, and push the water out through a chimney like hole in the top. shapes, and many of these shapes

Placozoans (phylum Placozoa) appear to be flat discs of cells, many with cilia. the largest placozoans are less than a tenth of an inch (3 mm) in diameter. they look like multicellular amoebas. they are not known to exist in natural conditions and have been found only on the glass sides of aquariums. laboratory cultures of placozoans consume single-celled algae. Under crowded conditions, placozoans produce cells that appear to be sperm and eggs, which form an embryo. Placozoan embryos have not been observed to develop fully into new placozoans. analysis of placozoan Dna indicates that they are the most primitive animals. Sponges (phylum Porifera) have no true organs, nerves, or muscles. the adults cannot move. Sponges have a skeleton that consists of protein and, usually,

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animals 

23

increase the surface area for light absorption. Since blue light penetrates more deeply into the water (which is why underwater scenes appear blue), the red pigment of the cyanobacterial symbionts allows many sponges to survive at depths where only a modest amount of light is available. Sponges can produce sperm, which sometimes emerge from the chimney in large numbers. The sperm may encounter and be drawn inside other sponges of the same species, where they fertilize eggs. The fertilized egg develops into a larva, which is a cluster of cells that swims by its flagella. The other very simple phyla of animals, consisting of very few cells, are internal parasites: myxozoans (phylum Myxozoa) and orthonectidans (phylum Orthonectida).

Radially Symmetrical Animals Cnidarians (phylum Cnidaria; also called coelenterates) include jellyfish, sea anemones, hydras, and corals (see figure). Cnidarians can have a major influence on their aquatic environments. For example, corals secrete lime skeletons, which build up into massive reefs and whole islands. Cnidarians can thus be important to many other species, as whole coral reef ecological communities are built upon their activities. Explosions of jellyfish populations sometimes occur when predatory fishes become rare. Cnidarians have a very delicate structure that consists of two tissue layers. The inner tissue layer lines a central digestive cavity into which they secrete digestive enzymes. Cnidarians have a single opening on one surface for food to enter and wastes to exit. Between the two cell layers is a gelatinous material, which in jellyfish can constitute most of the weight. The gelatinous mass is slightly lighter than water, which gives the animals some buoyancy. A network of nerves stimulates the contraction of cells; cnidarians have no specialized muscular tissue. Both the inner and outer tissue layers are in direct contact with the water. Each cell exchanges oxygen and carbon dioxide directly with the water. Cnidarians have no circulatory system. Cnidarians produce stinging tentacles around the opening of the central cavity. The stinging cells (nematocysts) on these tentacles inject tiny barbs into the prey. A toxin paralyzes the prey, and the tentacles draw the prey into the central cavity, where the prey is digested. Most cnidarians are harmless to humans, though the stings of some jellyfish can cause pain to and even kill swimmers. Algae cells live in the skin tissue of many cnidarians. This is mutually beneficial both to the photosynthetic cells, which use the animal’s carbon dioxide for photosynthesis and the animal’s wastes as fertilizer, and the cnidarian, for which

xviii+598_Biodiversity_F.indd 23

This purple-striped jellyfish (Pelagia panopyra) is very large and has very potent stingers.  (NOAA/Department of Commerce)

the photosynthetic cells are a built-in food factory. When these photosynthetic guests die, the cnidarian host may die. Coral bleaching occurs when corals lose their photosynthetic symbionts and then starve. Extensive reefs of corals have been bleached, perhaps due to increases in water temperature caused by global warming or increases in salinity caused by reduced water flow from rivers. The jellyfish Mastigias papua, found in a lagoon on the Pacific island of Palau, swim from one end of the lagoon to the other and back each day, keeping themselves in the sun and thus promoting the photosynthesis of their symbiotic algae. Many cnidarians have complex life cycles (see figure on page 24). The cylindrical polyp form is sessile, which means it remains attached to a surface such as a rock. With its tentacles reaching up, it grabs food that happens to come by. New polyps can branch off of, then break free from, old polyps (an example of asexual reproduction). In many cases, however, polyps produce another body form, the medusa, which is umbrella or bell shaped, such as the jellyfish. Medusae break free and swim, trailing their tentacles behind them. The medusae produce eggs and/or sperm for external fertilization. Some species have no medusa stage, some have no polyp stage, and some have both stages. In most species, however, either the polyp or the medusa phase of the life cycle predominates. Some cnidarians form colonies that consist of many individuals. For example, the Portuguese man-of-war (Physalia physalis) is a cluster of cnidarians. Ctenophores, or comb jellies (phylum Ctenophora), superficially resemble jellyfish. Unlike jellyfish, ctenophores propel themselves with cilia

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24 24 animals

first entry

Coelenterates (Phylum Cnidaria) alternate between the free-swimming, sexual medusa (“jellyfish”) form and the nonsexual polyp form that attaches to hard surfaces.

found in rows along the outside of the body. also, ctenophores have a mouth on the forward end and an anus on the back end, while jellyfish have a single opening for eating and evacuating. ctenophores do not produce their own stinging cells, though in some cases they can incorporate the stinging cells of jellyfish that they have eaten into their own tentacles.

BIlaTErally SymmETrICal aNImalS: proToSTomES Protostomes are animals whose embryos undergo cell division (cleavage) in a spiral pattern. as a result, the structures into which the cells develop are determined at a very early stage. the major groups of protostomes are the flatworms, mollusks, annelids, animals with lophophores, and animals with ecdysis. Flatworms (phylum Platyhelminthes) are freeliving or parasitic worms. Many flatworms, such as the planarians, live in aquatic habitats. Other flatworms, such as the oval-shaped flukes (trematodes) and the very long tapeworms (cestodes) live as parasites in the moist environments inside larger animals. Planarians have a head, eyespots, and a nervous system. Planarians move about to fi nd food and ingest it through a tube in the center of the ventral (lower) surfaces of their bodies. the planarian’s internal digestive tract, like that of cnidarians, has a single opening for both the intake of food and

xviii+598_Biodiversity_F.indd 24

the expulsion of wastes. Flukes and tapeworms, in contrast, absorb nutrients from and release wastes into the tissues or intestinal fluid of their hosts. therefore, flukes and tapeworms, unlike planarians, possess neither digestive tracts nor organs to eliminate wastes. the microscopic convolutions of their skin increase the surface area through which they can absorb food. Flukes and tapeworms live under anaerobic conditions, in which cellular respiration is impossible. they are continually bathed in the host’s intestinal fluid, which is full of digestive enzymes, but are protected by their outer layer of cells. in order to keep from being evacuated from the intestine, flukes and tapeworms attach themselves to the intestinal lining with suckers or hooks. Flatworms do not have circulatory systems. Because the digestive tract is highly branched, digested food diffuses from the gut to every part of the body of the planarian. Because planarians are very flat, oxygen has a very short distance to diffuse from the water into all the internal tissues. in most flatworms, each individual has both male and female reproductive organs. Many planarians reproduce by simply dividing in two, while others copulate; some switch seasonally between the two modes of reproduction. in most flukes and tapeworms, male and female reproductive organs form a large portion of each individual’s body. these organs

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animals produce millions of fertilized eggs and embryos. Massive egg production is essential for parasites, because it is unlikely that any single egg will encounter another suitable host. in some flukes, the male surrounds the female, and copulation goes on continuously. Flukes and tapeworms have very complex life cycles. they change forms as they move from one host or environment to another. Parasitic flatworms affl ict millions of people, where treatment is unavailable, making them permanently ill and thereby producing a tremendous impact on the economies of some countries (see below). Mollusks (phylum Mollusca) include the gastropods such as snails, bivalves such as clams, and cephalopods such as octopuses. Mollusks are active only underwater or in moist environments on land. Some mollusks have shells into which they can retreat to avoid drying out, but this is only a temporary measure, because they cannot then obtain food. in some cases, mollusk eggs can survive desiccation. Mollusk eggs can be carried to new locations on the legs of birds, and the eggs hatch when exposed to moisture. Some mollusks crawl, and some propel themselves using muscular contractions of a single foot. above the foot, the body cavity with its organs is surrounded by layers of muscles, which make up a

25

large percentage of the mollusk body (see figure). the three major classes of mollusks have different body structures: ●





Gastropod mollusks include snails and slugs. Most have a single coiled shell. Gastropod means “stomach-foot.” as they crawl, their heads, with antennae and eyes, project forward, but the mouth is in the foot. Bivalve mollusks, such as oysters, clams, and scallops, have two hinged shells, which they can close to protect themselves from desiccation and from predators. large muscles keep the shells closed. Unlike the other two classes of mollusks, bivalves do not have heads (see figure on page 26). Cephalopod mollusks (including squids and octopuses) look like their Greek name: a head (cephalo-) over a foot (-pod), which consists of tentacles. an octopus, therefore, does not have eight legs; it has one foot divided into eight parts. the squid and the octopus have either no shells or very small internal shells, while the chambered nautilus has a large conical shell. Squids propel themselves by squirting water out through a siphon. When

Mollusks (Phylum Mollusca) have organs over a large foot—the mouth is in the middle of the foot. In snails, the head has sensory organs but no mouth.

xviii+598_Biodiversity_F.indd 25

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26 26 animals  a predator pursues them, they may release ink to confuse the pursuer. Jet propulsion imparts great speed to some cephalopods. Mollusks have diverse ways of getting food. Many gastropods crawl over plant, soil, or rock surfaces on a layer of slime that they secrete, scraping up food (such as algae) with a radula, which is a rasplike structure covered with teeth, as they go along. Other gastropods, such as cone snails, have a poisonous harpoon near the mouth, which captures prey. In contrast, bivalves are filter-feeders. They use the cilia near their mouths to catch microscopic food particles from water that flows through them. Zebra mussels (Dreissena polymorpha) are European bivalves that were accidentally introduced into American lakes, where they are undergoing a population explosion. They filter plankton from the water so effectively that they can deplete the food base of whole aquatic food chains. Suckers on the underside of the tentacles allow cephalopods to grasp prey and cling to surfaces. The mouth, with a powerful beak, is located in the middle of the tentacles. Not being small or flat enough to exchange materials directly with their environments, mollusks have circulatory systems. In most mollusks, circulation is open and blood fills the whole body, although cephalopods have closed circulation. Mollusks have blood cells, but these cells do not carry oxygen. Oxygen is carried by hemocyanin, a copper-based molecule dissolved in the blood plasma. Aquatic mollusks absorb oxygen from a stream of water that is pushed through the body by the movements of internal cilia. Some terrestrial snails have lungs. Reproductive patterns are varied in mollusks. Gastropods and cephalopods have internal fertil-

This scallop has numerous simple eyes—the eyes allow the scallop to detect moving shadows that may represent danger.  (Bill Capman)

xviii+598_Biodiversity_F.indd 26

first entry ization. Gastropods typically have both male and female organs. A male cephalopod inserts a packet of sperm into a female with one of his tentacles. Bivalves, in contrast, have external fertilization. For this reason, as well as because they are filter feeders, bivalves cannot survive on land. Most mollusks, even those in which the adult phase is spent glued to a rock, have aquatic larvae that can swim. Cephalopods have evolved a level of intelligence higher than that of all other animals except vertebrates, and they evolved this intelligence independently of vertebrates. An octopus can learn by watching another. They can open jars with their tentacles. They can escape from predators by changing color and imitating their surroundings. The octopus has a complex eye that, due to its separate evolutionary origin, has a different structure from that of a vertebrate eye: The nerves are behind the retina in the octopus but in front of the retina in the vertebrate. Annelids (phylum Annelida) are segmented worms. Annelid means “little ring.” Each segment is a unit in which muscles, nerves, and some organs are repeated nearly throughout the worm’s length. The worm’s muscles exert pressure against watertight segments, allowing the worm to move. Because water is incompressible, it remains firm when muscles press against it. The water therefore acts as a skeleton, called a hydrostatic skeleton (hydrostatic is Greek for “water remaining in place”). The main nerve cord in annelids is ventral (along the belly), unlike humans and other chordates, in which the nerve cord is dorsal (along the back). Earthworms are the most familiar annelids. Many marine annelids grab and eat small particles of food. Earthworms ingest leaf litter or soil containing decomposed organic matter, which they further break down. Leeches are annelids, many of which suck blood from larger animals. The blood meal may allow a leech to increase greatly in size. It may live off of one meal for up to 200 days. Not being small or flat enough to exchange materials directly with their environments, annelids have circulatory systems. In some annelids, a hemoglobinlike substance that contains iron, which may or may not be in cells, carries oxygen and makes their blood red; in others, hemocyanin carries oxygen. The circulatory system is often open to allow the blood to bathe the internal organs. Marine annelids have external reproduction. In some cases, whole populations release reproductive segments synchronously. The palolo worms of Samoa release millions of reproductive segments in October at the Moon’s last quarter. The fertilized eggs develop into larvae, which develop into adults. Earthworms, unlike most marine annelids,

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animals  reproduce by internal fertilization. The easily visible clitellum produces a cocoon from which larval worms hatch. Annelids can regenerate readily from fragments, which is fortunate for worms that live in heavily gardened soil. Because they draw leaf litter down into the soil and fill the soil with burrows, earthworms aerate the soil and enhance its organic matter content. In both ways, earthworms exert an extremely beneficial effect on soil fertility, an economic benefit beyond calculation. However, the introduction of earthworms into habitats that previously did not have them can be severely disrupting. Animals with lophophores. A lophophore is a ring of hollow, ciliated hairs that create a current and help to capture food items. Animals with lophophores are therefore filter feeders. The lophophore surrounds the mouth. The digestive tract curls around in a horseshoe shape and usually emerges outside the lophophore. ●●

●●

●●

●●

Brachiopods, or lampshells (phylum Brachiopoda), closely resemble bivalve mollusks, except for the lophophore. Brachiopods and mollusks lived in roughly equal abundance before the Permian extinction, from which the mollusks recovered more vigorously. Brachiopods of the genus Lingula live in sediments and are largely unchanged from the early Paleozoic era. Bryozoans, or moss animals (phylum Bryozoa, or Ectoprocta), are small animals that form extensive colonies on rocks and other marine surfaces. They have an outer layer of tissue that secretes a hard coat, usually calcium carbonate, with an opening on the top through which the animal sticks out its lophophore. Individuals within the (sometimes very large) colonies have different structures and specialize in different activities. Phoronids, or horseshoe worms (phylum Phoronida), look like small roundworms but have an external lophophore around the mouth. Goblet worms (phylum Entoprocta) are filter feeders with lophophores. Unlike the others, goblet worms have digestive tracts in which both ends are inside the ring of hairs.

Animals with ecdysis. Ecdysis is the molting of a hard outer covering. The major phyla of animals with ecdysis are the roundworms, the arthropods, and their relatives. Roundworms (phylum Nematoda) can, like flatworms, be free living or parasitic. Most roundworms

xviii+598_Biodiversity_F.indd 27

27

are nematodes that live in water and soil. An acre of farmland can contain 100 billion nematodes; a single rotting apple can contain 90,000. Species diversity of nematodes has been explored only barely, and new species are found as new soil samples are examined. Most nematodes are decomposers or predators, but many infect plant roots and cause much crop loss. Some roundworms are parasites inside other animals. Roundworms are more or less cylindrical rather than flat. A thick covering of collagen (the same protein found in many animal skeletons) protects their bodies. Roundworms move as their muscles exert force against the water contained within their bodies, giving them a hydrostatic skeleton like that of annelids. Roundworms have a digestive tract with separate openings for ingesting food and expelling wastes. Food can diffuse from the digestive tract as well as oxygen from the environment (unless it is anaerobic, as in the intestines of hosts) to all parts of the roundworm’s body. Therefore, roundworms do not have circulatory or respiratory systems. Roundworms usually live as separate male and female individuals and usually copulate. Parasitic roundworms may have complex life cycles. For example, one species of nematode, Fergusobia curriei, spends one part of its life cycle in a fly and another part in eucalyptus trees. The simple roundworm Caenorhabditis elegans consists, at maturity, of exactly 959 body cells with a variable number of reproductive cells. Its DNA and development have been intensively studied. It is one of the most important laboratory animals. The largest phylum of animals with ecdysis is the arthropods (phylum Arthropoda). The most familiar arthropods are the centipedes, millipedes, spiders, and insects. Based on the number of species or the number of individuals, arthropods have been the evolutionary success story of the animal kingdom. These animals are so diverse and important that they are described in their own entries. Two phyla of animals with ecdysis resemble arthropods in structure and on the basis of DNA comparisons, as follows: ●●

The tardigrades, or water bears (phylum Tardigrada), are microscopic aquatic segmented animals that walk slowly on eight legs. They are most famous for surviving extreme environmental conditions: They can survive at temperatures close to absolute zero and as high as 300° F (150° C), can absorb a thousand times as much radiation as any other known animal, and can revive after being dehydrated for years. They can even survive in outer space conditions.

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28 28 animals  ●●

The velvet worms (phylum Onychophora) look like annelids with stubby legs. They walk around in tropical vegetation looking for prey, which they trap in slime. Like many arthropods, velvet worms breathe through tracheae, which are air tubes that branch through the body. Some of them produce live offspring, which is very rare outside the vertebrates.

In addition to the roundworms, water bears, velvet worms, and arthropods, the following phyla have ecdysis: ●●

●●

●●

●●

Kinorhynchians (phylum Kinorhynchia) are animals that look like worms with segmented outer plates, and they pull themselves through sediments with a ring of bristles around their retractable heads. Horsehair worms (phylum Nematomorpha) are parasitic worms that resemble long, thin roundworms. Penis worms (phylum Priapulida) are filter feeders that burrow in sediments and extend a spiny proboscis out into the water. Loriciferans (phylum Loricifera) are filter feeders that embed themselves in marine sediments. They can retract their heads into the protective outer coverings of their bodies. The other phyla of protostomes are the following:

●●

●●

●●

Rotifers (phylum Rotifera) are microscopic animals that live in freshwater or the thin layers of water on soil particles. Their heads are surrounded by rapidly moving cilia that scoop food particles into their stomachs. Many bdelloid rotifers are totally asexual. Evolutionary scientists generally understand that sexual reproduction creates genetic diversity, which allows animals to evolve faster than their parasites. Bdelloid rotifers, however, can desiccate and blow away in the wind, leaving their fungal parasites behind. Ribbon worms (phylum Nemertea) are long, thin worms that live mostly on the ocean floor. A ribbon worm can eject a proboscis out of its head to capture prey. Some ribbon worms are almost 100 feet (more than 30 m) long. Spiny-headed worms (phylum Acanthocephala) look like simple parasitic roundworms, except that they have a spiny proboscis they can distend from the body and imbed in the intestinal wall of a host.

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first entry ●●

●●

●●

●●

●●

●●

●●

Only three species of cycliophore (phylum Cycliophora) are known. Symbion pandora lives on the mouth bristles of some lobsters but is not a parasite. Though it has a horseshoe-shaped gut and a ring of cilia around its mouth, it does not have a true lophophore. Because its anatomy matches no other known animal and because of its complex life cycle, which matches the molting phases of the lobster, it is assigned to its own phylum. Arrow worms (phylum Chaetognatha) are small predatory worms with grasping spines, tiny compound eyes, and tiny teeth. Gastrotrichs (phylum Gastrotricha) are tiny worms that live in freshwater or marine sediments. They live only about three days. There is only one species of micrognathozoan (phylum Micrognathozoa). It was mistaken for a rotifer until close observation showed it had complex jaws, which are absent in rotifers. Peanut worms (phylum Sipuncula) have a retractable, tentacled proboscis and live in burrows in shallow water. Spoon worms (phylum Echiura) are genetically similar to annelids but are not segmented. Jaw worms (phylum Gnathostomulida) are tiny worms with relatively big jaws that they use to scrape food off sediment particles.

Bilaterally Symmetrical Animals: Deuterostomes Deuterostomes are animals whose embryos undergo cell division (cleavage) in a radial pattern. As a result, the structures into which the cells develop are not determined until a later stage than that of protostome embryos. The major groups of deuterostomes are the echinoderms, the hemichordates, and the chordates. The simplest deuterostomes are the simple, marine, mollusklike xenoturbellidans (phylum Xenoturbellida), recognized as deuterostomes only by DNA analysis. Echinoderms (phylum Echinodermata) include starfish, sea urchins, and sand dollars as well as other forms less frequently seen. Adult echinoderms appear radially symmetrical, but their larval forms and their internal organs have some bilaterial symmetry. Echinoderms have an external skeleton containing calcium or magnesium, often with knobs or spines (echinoderm is Greek for “spiny skin”). The skeleton offers protection from many predators, but not from desiccation. Echinoderms are entirely

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animals  marine. The five “legs” of a starfish are not really legs, they are portions of the body. Starfish move by means of hundreds of tiny tube feet on the underside of their bodies. Water inside the tube feet is pressurized by structures at the bases of the feet. The tube feet create suction against the surfaces on which they walk. Starfish and many other echinoderms have a mouth in the center of the underside of the body. A starfish uses its tube feet to pull open tightly closed shells of bivalves, then disgorges its stomach out through its mouth and into the bivalve. The bivalve shells need to be pulled apart as little as one 200th of an inch (a 10th of a millimeter) to allow the starfish to insert its stomach. Once it has partly digested the bivalve’s tissues, it absorbs the digested material. Starfish eat animals such as corals by placing their stomachs directly on the corals and digesting them. No other phylum has the water vascular system found in echinoderms. Seawater circulates and carries oxygen throughout the body in this system of canals. The tube feet are connected to this system. Echinoderms release eggs and sperm into the water, and fertilization occurs externally. A bilaterally symmetrical larva, which swims with cilia, develops from the fertilized egg. Populations of some starfish have exploded and have eaten many coral polyps, causing extensive damage to some Pacific reefs. Populations of some sea urchins have exploded in the Pacific Ocean. The urchins have eaten up entire seaweed forests, causing disaster for many other species. Many hemichordates (phylum Hemichordata), the acorn worms, look like simple worms with a proboscis, collar, and trunk. They burrow in sediments. Other hemichordates are filter feeders that form extensive colonial networks. As the name implies, they have a number of features that resemble those of chordates: The adults may have gill slits and a nerve cord along the dorsal (back) surface rather than the ventral (front) surface, as in most other phyla. DNA studies have identified them as close relatives of echinoderms and chordates. The chordates (phylum Chordata) include all of the vertebrates, but some invertebrates as well. All chordates have, at some stage of their life cycles, these characteristics: ●● ●● ●●

a dorsal nerve cord (along the back) slits in the neck region called gill slits a notochord

The notochord is a flexible rod that provides reinforcement for muscles. Some of the simplest chordates retain these features throughout their

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29

lives, while others have them only in their juvenile stages. Most vertebrates have gill slits and notochord only during embryonic development. At birth, most vertebrates have a backbone with vertebrae instead of a notochord. Because of these similarities, the invertebrate chordates are probably similar to the ancestors of vertebrates. Lancelets are fish-shaped invertebrate chordates that retain all three chordate features throughout their lives. They lie half buried on the bottoms of shallow seas, with their tails in the sand and their jawless mouths filtering small particles of food from the water. Tunicates have some chordate features during their fishlike larval stage. As adults, however, tunicates do not resemble fish. The larvae settle onto rock surfaces and change into adults. Adult tunicates draw water in through an opening on top, filter food particles from the water, and eject the water through a pore along their sides. This manner of life has earned adult tunicates the name “sea squirts.” A layer of muscle surrounds their internal organs, including a heart, intestines, and reproductive organs. The vertebrates are the fishes, amphibians, reptiles, birds, and mammals. Like the arthropod exoskeleton, the vertebrate structure has allowed an explosion of diversity and adaptation.

Parasitic Invertebrates Parasitic flatworms and roundworms cause an immense amount of human suffering, mostly in developing tropical countries. Usually, parasitic worms do not kill the human in which they live. The worms may, however, cause much pain and weakness in muscles and other organs and if they live in the intestines may consume a large share of the food that the person has eaten, food the victim probably has not gotten enough of anyway. The weakened victim becomes vulnerable to microbial diseases and is a less productive member of society. Adult liver flukes, Opisthorchis sinensis, may reach several centimeters in length inside a human body. They live in the duct that conducts fluids from the liver to the intestines. The flukes mate and can produce millions of eggs, which drain into the intestines, ending up in sewage (see figure on page 30). The eggs, if ingested by a snail, hatch into larvae, which form cysts (protective casts) in the snail’s tissues. Inside the cysts, these larvae develop into another type of larva. Each of these larvae can undergo sexual reproduction to form up to 50 larvae of yet a third developmental stage. These larvae emerge from the snail’s skin into the water. When they encounter a fish, they burrow into the fish’s muscle, changing form yet again to become another kind of larva inside cysts. When the fish is caught by a human and

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30 30 animals

first entry

Some tapeworms reach sexual maturity in the intestines of mammals, such as humans. The tapeworms release eggs and sperm into human wastes, which can then enter polluted water. The fertilized eggs develop into freeliving larvae. The tapeworm larvae develop into another form inside the bodies of aquatic arthropods. When fish eat the arthropods, the tapeworms develop into yet another form in the tissues of the fish. Mammals are infected by tapeworms by eating uncooked or undercooked fish.

eaten without adequate cooking, the cysts hatch out in the human’s intestines, becoming adult flukes that find their way to the duct that connects the liver with the intestines, completing the cycle. in order for liver flukes to affl ict people, two conditions are necessary. First, there must be a cultural practice of eating raw fish, which is common in the Orient. Second, there must be sewage contamination of the water in which the fish are caught. Most sashimi (Japanese raw fish), which is becoming increasingly popular in the United States, is safe because it is prepared from fish caught in clean water, and the preparers are trained to look for evidence of parasites. at least 200 million people suffer from schistosomiasis, in which the blood fluke (genus Schistosoma) lives in human blood. adult schistosomes produce so many eggs that when the eggs lodge in the capillaries of various organs, mainly the liver, inflammation results. the resulting blockage of blood flow can damage the organs. the schistosome life cycle is similar to, but less complex than, that of the liver fluke. High human population densities

xviii+598_Biodiversity_F.indd 30

around stagnant waters in which snails thrive provide ideal conditions for the spread of schistosomiasis. Humans frequently create the stagnant waters, as when the aswan Dam was built across the freely flowing nile River. Before the dam was built, only 5 percent of the egyptians along the river suffered from schistosomiasis; after the dam’s completion, 75 percent of those who lived beside the still waters above the dam suffered from this parasite, as did 33 percent of the people who lived below the dam. tapeworms (such as the beef tapeworm, Taeniarhynchus saginatus) in the human intestines produce up to a dozen new segments each day and can keep doing so for 20 years, forming a chain up to 30 feet (almost 10 m) in length. any two segments can mate with each other. Segments at the end can break off and crawl out the anus and onto the skin, clothes, or bed of the infected person. Usually, however, segments split open, each releasing up to 100,000 fertilized eggs. the eggs usually end up in sewage. if a cow eats grass that has been contaminated with tapeworm eggs, the eggs will hatch inside the cow’s intestines and burrow into its muscles. the cycle is

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animals  completed when a human eats undercooked beef. The pork tapeworm, Taenia solium, has a similar life cycle. Most beef and pork is not infected, but meat inspections are incomplete. Eating rare meat therefore carries significant risk of infection by tapeworms. Trichinella spiralis roundworms have a life cycle similar to tapeworms and also spread through the consumption of undercooked meat. Adults of the dog tapeworm, Dipylidium caninum, grow and produce eggs in the intestines of dogs. Eggs can get into the dog’s blood, also, and from there get into the guts of fleas that feed on the dog’s blood. The fleas can then spread the parasite to another dog. Dogs may get tapeworm eggs in their mouths from licking surfaces contaminated by dog feces. Humans can be accidentally infected by the dog tapeworm, either from the bites of infected fleas or from direct contact with dogs. The tapeworm larvae can form cysts in various human organs, including the brain. Eight kinds of filarial worms cause disease in 400 million people. Adult worms feed and mate within the lymph system of humans, blocking the vessels and causing the swelling and disfigurement often called elephantiasis. After mating, the female worms release larvae into the lymph. The larvae can spread to other humans by mosquito bites. Other filarial worms cause river blindness. Adult worms live in the outer cell layer of the cornea, causing severe itching and eventually blindness. The bites of black flies transmit the worms to humans. In some African and South American villages, nearly every elderly person is blind from this disease. Acanthocephalan worms usually live in the intestines of crustaceans. When shorebirds eat the crustaceans, the acanthocephalans can infest the birds’ intestines as well. In at least one case, the acanthocephalan produces massive amounts of serotonin, a hormone that influences the crustacean’s behavior. Crustaceans that normally hide will, as a result of the serotonin, stick their bodies out where ducks can easily find and eat them. Parasitic worms have a major impact on a billion people in the world. It is not necessary to wait for a medical breakthrough in order to treat these illnesses. Medicines, though sometimes expensive, are available. It is more effective, however, to control the disease ecologically by preventing the spread of the worms, in most cases by sewage treatment. However, many governments are unable or unwilling to undertake the building of sewage treatment facilities. Until they do, these diseases will persist. The unsanitary conditions of poverty encourage the spread of these worms, but the illnesses caused by these worms, even when mild, make it difficult for the victims to raise themselves out of poverty.

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31

See also amphibians; arthropods; birds; continental shelves, biodiversity on; crustaceans; deep oceans, biodiversity in; eukaryotes; fishes; insects; invasive species; mammals; mutualism; parasitism; reptiles. Further Reading Arizono, Naoki, et al. “Diphyllobothriasis associated with eating raw Pacific salmon.” Emerging Infectious Diseases 15 (2009): 866–870. Dellaporta, Stephen L., et al. “Mitochondrial genome of Trichoplax adhaerens supports Placozoa as the basal lower metazoan phylum.” Proceedings of the National Academy of Sciences USA 103 (2006): 8,751–8,756. Donoghue, P. C. J., and M. A. Purnell. “Genome duplication, extinction, and vertebrate evolution.” Trends in Ecology and Evolution 20 (2005): 312–319. Emlen, Douglas J. “The evolution of animal weapons.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 387–413. Fenwick, Alan. “Waterborne infectious diseases—Could they be consigned to history?” Science 313 (2006): 1,077–1,081. Glenner, Henrik, et al. “The origin of insects.” Science 314 (2006): 1,883–1,884. Jönsson, K. Ingemar, et al. “Tardigrades survive exposure to space in low Earth orbit.” Current Biology 18 (2008): R729–731. Lafferty, K. D. “Fishing for lobsters indirectly increases epidemics in sea urchins.” Ecological Applications 14 (2004): 1,566–1,573. Mather, Jennifer A. “Cephalopod consciousness: Behavioral evidence.” Consciousness and Cognition 17 (2008): 37–48. Pearse, J. S. “Ecological role of purple sea urchins.” Science 314 (2006): 940–941. Peigné, J., et al. “Earthworm populations under different tillage systems in organic farming.” Soil and Tillage Research 104 (2009): 207–214. Power, Brian, and Carolyn Goossens. “Hallucinations arising in the context of torn attachment, traumatic childhood, and tapeworms.” Australasian Psychiatry 17 (2009): 240–242. Skelly, Patrick. “Fighting killer worms.” Scientific American, May 2008, 94–99. Wilson, Christopher G., and Paul W. Sherman. “Anciently asexual bdelloid rotifers escape lethal fungal parasites by drying up and blowing away.” Science 327 (2010): 574–576. Zimmer, Carl. Parasite Rex: Inside the Bizarre World of Nature’s Most Dangerous Creatures. New York: Free Press, 2001. ———. “How smart is the octopus? Bright enough to do the moving-rock trick.” Slate, June 23, 2008. Available online. URL: http://www.slate.com/id/2192211. Accessed May 11, 2011.

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32 32 archaea 

first entry

archaea  Formerly known as archaebacteria, the

archaea, or archeans, are single-celled bacteria-like organisms, most of which live in extreme conditions of temperature, salt, or acidity. Most of them have been discovered only recently, because they live in conditions in which scientists did not expect to find any organisms. Their superficial resemblance to bacteria also contributed to their uniqueness being overlooked for many decades. Among their similarities to bacteria are the following: ●● ●●

●● ●● ●● ●●

Like bacteria, archaeans have simple shapes, usually spheres, rods, or spirals. Like most bacteria, most archaeans have cell walls. In both bacteria and archaeans, there are some types that lack cell walls (Mycoplasma in bacteria, Thermoplasma in archaeans) and have irregular shapes. Like bacteria, archaeans have DNA but no nucleus; both are prokaryotes. Like many bacteria, many archaeans can form colonies. Both bacteria and archaeans are very small, often 10 times smaller than eukaryotic cells. Bacteria can be aerobic (grow in the presence of oxygen gas) or anaerobic. Most archaeans are anaerobic, although some Sulfolobus archaeans can tolerate oxygen.

However, archaeans are distinct from bacteria in some fundamental ways, such as the following: ●● ●●

●●

●●

●●

●●

Bacterial cell walls consist largely of peptidoglycan; archaean cell walls do not. Cell membranes of all cells consist largely of phospholipids, but these are different in bacteria and archaeans. In bacteria, the phospholipids have ester linkages, while archaean cell membranes have phospholipids with ether linkages instead. The fatty chain of the bacterial phospholipid is a fatty acid, while in archaeans it is an isoprene. Eukaryotic cell membrane phospholipids are similar to those of bacteria, not archaeans. Cell membranes in bacteria (and eukaryotes) are double layered, while in some archaeans they form a single layer. Some archaeans have shapes not found in bacteria, such as flat, square forms and extremely narrow, needlelike forms. Archaean DNA is associated with histone proteins, like the chromosomes of eukaryotic cells; the DNA of bacteria is not. Archaeans have enzymes associated with the transcription of RNA and translation of

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●●

●●

proteins that more closely resemble those of eukaryotic cells than of bacteria. Both bacteria and archaeans often have flagella, whiplike structures that allow them to swim, but the flagella of bacteria and archaeans appear to have evolved separately, the former from secretory proteins, the latter from hairlike extensions called pili. Both bacteria and archaeans have many of the same ways of obtaining metabolic energy (see table on page 33). For example, some species in both groups obtain energy from sunlight or obtain carbon from inorganic sources such as carbon dioxide. Some bacteria (such as cyanobacteria) can do both, but there are no archaeans that can do both. Some types of metabolism, such as the production of methane gas, are unique to archaeans.

These differences, plus the fact that archaeans have very different DNA sequences from those of bacteria (up to 15 percent of archaean genes encode proteins not known in bacteria), justify the classification of the Archaea as one of the three principal domains of life, equally distinct from bacteria and Eucarya (eukaryotes). Many of the organisms that live in extreme conditions are archaeans. Most of them live in conditions of extreme acidity, temperature, salinity, or pressure that biologists at one time considered impossible for organisms to endure. Pyrolobus fumarii, for example, lives in deep ocean vents where the water reaches 235°F (113°C). Water boils at 212°F (100°C) at the air pressure of sea level, but the pressure at the bottom of the ocean allows superheated water to exist, in which this archaean lives. However, the most primitive lineages of bacteria, represented by Aquifex and Thermotoga, thrive under extreme conditions as well. The earliest bacteria, like the earliest archaeans, must therefore have evolved under extreme conditions on the early Earth. The extreme conditions in which most archaeans live are not necessarily distant from the places where most eukaryotes reside. Many archaeans live in animal intestines (under extreme anoxic, basic, or acidic conditions), where they digest cellulose and other molecules. Some intestinal archaeans are commensalistic, neither beneficial nor harmful. An example is Methanobrevibacter smithii, a methaneproducing archaean that lives in human intestines. Not all archaeans, however, live in extreme conditions. For example, archaeans are a major component of marine plankton. No archaeans are known to cause diseases in eukaryotes. The evolutionary scientist Carl Woese began making nucleic acid comparisons among many dif-

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archaea 

33

Types of Archaean Metabolism Metabolism

Source of Energy

Source of Carbon

Example

Organotrophs

Organic molecules

Organic or inorganic

Sulfolobus

Phototrophs

Light

Organic

Halobacteria

Lithotrophs

Inorganic molecules

Organic or inorganic

Methanobacteria

ferent species in the 1970s. At that time, all bacteria were lumped together into one category. Woese found that certain bacteria that lived in extreme conditions had nucleic acid sequences as different from those of other bacteria as they were from those of eukaryotes. It was from this discovery that evolutionary scientists began distinguishing the archaebacteria (as they were then known) as a distinct branch of life from the eukaryotes and the eubacteria. DNA studies since the time of Woese’s original work have continued to confirm the uniqueness of archaeans. The complete genome of Methanococcus janaschii was published in 1996. Only 11 to 17 percent of its genome matched that of known eubacteria, and more than half of its genes are unknown in either bacteria or eukaryotes. Moreover, some of the DNA similarity between archaeans and bacteria may be due to horizontal gene transfer, in which bacteria exchange small segments of DNA. Although most horizontal gene transfer occurs between bacteria closely related to one another, exchange between archaeans and bacteria has occurred frequently during the history of life. The major groups of archaebacteria are recognized by many evolutionary scientists on the basis of DNA sequences: ●●

Euryarcheota include the methanogens and the halophiles. Methanogens convert hydrogen gas (H 2) and carbon dioxide gas (CO2) into methane gas (CH4). They live in marshes and in the intestinal tracts of animals such as cows and humans. They are a principal source of methane in the atmosphere. Halophiles live in extremely salty conditions such as the Dead Sea and the Great Salt Lake. Halophiles may have evolved more recently than other archaebacteria. First, they obtain their carbon from organic molecules produced by the decay of other organisms, which implies that they evolved after these other organisms were already in existence. Second, they use a molecule that resembles the rhodopsin visual pigment in the vertebrate eye in order to produce energy from sunlight. Third, DNA analyses place halo-

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●●

●●

philes outward toward the branches of the archaebacterial lineage, rather than near the primitive base of the lineage. Crenarcheota include thermophiles that live in very hot environments, but some crenarcheotes live in soil and water at moderate temperatures. Korarcheota, Nanoarcheota, and Thaumarcheota have been identified mainly by their DNA sequences, and little is yet known about them.

The earliest cell fossils, such as those found in the 3.5 billion-year-old Apex chert, were of types that, if they lived today, would be classified as bacteria or archaeans. Throughout the Archaean era, the entire world was prokaryotic. Throughout the Proterozoic, the world was mostly microbial, shared between prokaryotes and eukaryotes. Only in the last 540 million years (the last 14 percent of Earth history since the beginning of the Archaean era) have multicellular organisms been numerous. The evolutionary biologist Stephen Jay Gould pointed out that in every age of Earth history, bacteria and archaeans have been the modal type of organism. As an examination of the differences between bacteria and archaeans reveals (see above), the modern eukaryotic cell (such as a human cell) resembles bacteria, while the modern eukaryotic nucleus resembles archaeans. This constitutes evidence for the theory, increasingly accepted among evolutionary scientists, that the eukaryotic cell came into existence when a small archaean penetrated a larger bacterium and formed a mutualistic association, followed by the uptake of bacterial DNA by the archaean, which became the nucleus. If this is true, then archaeans are not an evolutionary sideshow or mere leftover from the distant past, but are the partial ancestors of all complex life on Earth, including humans. See also bacteria. Further Reading Baker, B. J., et al. “Lineages of acidophilic Archaea revealed by community genomic analysis.” Science 314 (2006): 1,933–1,935.

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34 34 arthropods  Barns, S. M., et al. “Perspectives on archaeal diversity, thermophily and monophyly from environmental rRNA sequences.” Proceedings of the National Academy of Sciences USA 93 (1996): 9,188–9,193. Brocks, J. J., et al. “Archean molecular fossils and the early rise of eukaryotes.” Science 285 (1999): 1,033– 1,036. Cox, C. J., et al. “The archaebacterial origin of eukaryotes.” Proceedings of the National Academy of Sciences USA 105 (2008): 20,356–20,361. DeLong, E. F. “Archaea in coastal marine environments.” Proceedings of the National Academy of Sciences USA 89 (1992): 5,685–5,689. Eppley, J. M., et al. “Genetic exchange across a species boundary in the archaeal genus Ferroplasma.” Genetics 177 (2007): 407–416. Friend, Tim. The Third Domain: The Untold Story of Archaea and the Future of Biotechnology. Washington, D.C.: Joseph Henry Press, 2007. Howland, John L. The Surprising Archaea: Discovering Another Domain of Life. Oxford: Oxford University Press, 2000. Huber, H., et al. “A new phylum of Archaea represented by a nanosized hyperthermophilic symbiont.” Nature 417 (2002): 63–67. Nelson, K. E., et al. “Evidence for lateral gene transfer between Archaea and bacteria from genome sequence of Thermotoga maritima.” Nature 399 (1999): 323–329. Rappé, M. S., and S. J. Giovannoni. “The uncultured microbial majority.” Annual Reviews of Microbiology 57 (2003): 369–394. Thauer, R. K. “A fifth pathway of carbon fixation.” Science 318 (2007): 1,732–1,733. Walsby, A. E. “A square bacterium.” Nature 283 (1980): 69–71. Whitman, W. B., et al. “Prokaryotes: The unseen majority.” Proceedings of the National Academy of Sciences USA 95 (1998): 6,578–6,583. Woese, Carl R., and George E. Fox. “Phylogenetic structure of the prokaryotic domain: The primary kingdoms.” Proceedings of the National Academy of Sciences USA 74 (1977): 5,088–5,090. ———, O. Kandler, and M. L. Wheelis. “Towards a natural system of organisms: Proposal for the domains Archaea, Bacteria, and Eucarya.” Proceedings of the National Academy of Sciences USA 87 (1990): 4,576–4,579.

arthropods  Arthropods (phylum Arthropoda) are animals that have jointed appendages and an exoskeleton. The most abundant arthropods are the crustaceans, spiders, and insects. They are the most diverse and numerous of animals—truly the quiet majority (see table).

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first entry Estimated Number of Species of Major Arthropod Groups Group

Number of Species

Chelicerates

77,000

Crustaceans

35,000

Insects Myriapods Total

1,120,000 13,000 1,245,000

Arthropods live in practically every aquatic and terrestrial habitat. Arthropods were the first animals to live on land, about 420 million years ago. At that time, they had the terrestrial world to themselves and began an explosion of evolutionary diversity that continues today. One secret of arthropod success has been their external skeleton, or exoskeleton. This hard outer covering, composed mostly of chitin (a molecule related to carbohydrates), provides a shield that helps protect all arthropods from attack and prevents terrestrial arthropods from drying out. Because the exoskeleton cannot expand once it hardens, arthropods must periodically molt (shed) their exoskeletons as they grow. Another secret of arthropod success has been their jointed appendages. Appendages include legs and other structures that develop in a manner similar to legs in the embryo. The joints of legs allow strength and flexibility of movement at the same time. A large measure of arthropod success, however, has resulted from appendages other than the legs they use for walking. Many aquatic arthropods, for example, have special swimming appendages. Spiders and their relatives seize, poison, and consume their prey with appendages called chelicerae. Insects do not have jaws. Instead, they use appendages called mandibles to chew their food. Even the antennae with which many arthropods can touch objects and detect chemicals are appendages. Arthropods have segmented bodies. The segments are often fused together (for example, no segmentation is visible in mites). Many of the same organs are repeated in each segment. For example, a pair of nerve cords runs down the ventral (lower) surface of the arthropod body, and there is a ganglion (bundle of nerves) in each segment. Many of the segments have pairs of appendages. Arthropods have open circulatory systems, in which blood is pumped through vessels that have open ends; the blood therefore bathes the internal organs. Aquatic arthropods use gills to exchange

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arthropods  oxygen with their environments. Insects breathe by means of tracheae, breathing tubes that penetrate throughout their bodies. This is a very efficient system for a small animal. Tracheae would not, however, provide enough surface area to provide sufficient oxygen to the tissues of a very large insect. Therefore, one of the reasons that insects are mostly small is that huge, “monster,” insects would be unable to breathe. Spiders have simple lungs. Arthropods have two kinds of eyes. The ocelli are usually little more than pits with visual pigments and allow the animal to detect the direction from which danger may be approaching. The ocelli of spiders, however, can form images. The compound eyes of arthropods form simple images because each facet is a pixel of light, darkness, and, in many cases, color. All terrestrial and many aquatic arthropods have internal fertilization. This is true even of adult barnacles, which cannot move. The male barnacle extends a lengthy penis to fertilize a nearby female. Many arthropods have appendages specialized for sexual reproduction. Some arthropods can reproduce asexually. Aphids (insects that consume sap from plants) may have many generations during a single summer in which new aphids hatch from unfertilized eggs laid by female parents that have not mated. In many arthropods, the larval phase (such as a caterpillar) has a structure and function very different from the adult phase (such as a butterfly).

Myriapods Myriapods are the centipedes, millipedes, and related groups. Their name refers to their large number of legs: Most have a pair of legs on nearly every one of their many segments. Most live in moist forests. They have simple eyes. They breathe with tracheae; myriapod tracheae evolved separately from those of insects. Myriapods were among the earliest land animals, beginning in the late Silurian period. Myriapods include the following. ●●

●●

●●

Centipedes (Chilopoda) have venom claws on their heads and are predators. “Centipede” means “hundred legs” in Latin, but none have quite this many. Millipedes (Diplopoda) consume decaying plant material. They appear to have two pairs of legs per segment rather than one due to the fusion of segment pairs during development. They defend themselves by curling into a coil. Pauropods (Pauropoda) and symphylans (Symphyla) resemble tiny, pale millipedes. They live primarily in the pore spaces of soil.

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35

Crustaceans Crustaceans, nearly all aquatic, include crayfish, lobsters, crabs, shrimp, barnacles, and many microscopic plankton. They are very abundant and important members of aquatic ecosystems around the world and have their own entry in this encyclopedia. Some isopods, such as pill bugs, live on land in moist soil mostly underneath rocks. The largest group of crustaceans, the decapods (from the Latin for “ten legs”), have five pairs of walking legs on the thorax. They manipulate food with the front appendages of the thorax, which are sometimes modified into big pincers. The appendages of their abdomens are often modified for swimming.

Chelicerates Chelicerates include spiders, scorpions, ticks, mites, and their relatives. They often have two body parts: the cephalothorax (head and thorax fused), with appendages, and the abdomen, without appendages. The first pair of appendages on the cephalothorax is the chelicerae, which are paired mouthparts used to seize and pierce prey. In spiders, the chelicerae insert venom into the prey. Behind the chelicerae are the pedipalps. If the chelicerae are large, the pedipalps may be used primarily for walking or as sensory structures. Otherwise, they grasp and manipulate the prey. The largest group of chelicerates is the arachnids. They lack antennae and have four pairs of walking legs. Sexual reproduction in arachnids such as spiders is a touchy and dangerous operation. After the final molt, the adult male stops eating. The male spider puts sperm on one of his front appendages and goes searching for a female. He uses special approach signals so that he is not mistaken for prey. The male inserts the appendage with sperm into a pore in the female’s abdomen. Mating in scorpions is even more risky than in spiders and involves complex dances and the transfer of sperm into the female’s abdomen by one of the male’s legs. In some species, the female spider or scorpion eats the male after mating. The largest group of arachnids is the spiders, described in a separate entry. Among the groups of arachnids that resemble spiders are the following. ●●

●●

Harvestmen (“daddy longlegs”) resemble spiders, but their body segments are largely fused into a single structure. They have extremely long legs. Unlike spiders but like insects, they breathe through tracheae. They are not known to produce venom or silk. Also unlike spiders, they can eat, not just suck. They are harmless to humans. Sunscorpions (solifugids), unlike spiders, have a segmented abdomen. Because their

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36 36 arthropods 

●●

front legs are small and sensory, they walk primarily on six legs. Like harvestmen and insects, they breathe through tracheae. Their pedipalps produce an adhesive that captures prey. They produce no venom. The chelicerae cut up the prey. Enzymes liquefy the internal organs of the prey. Sunscorpions must suck because they cannot eat. They also differ from true scorpions (see below). Hooded tickspiders are small and blind and have a hood with which they can cover their heads.

Scorpions are nocturnal predators with big clawlike chelicerae and a stinging tail that they hold over their bodies (see figure). Unlike other arthropods, they bear live young. Like spiders, they cannot eat food items but must liquefy the internal organs of their victims with enzymes. They are associated with deserts, although scorpions live in a wide range of terrestrial environments. Many people greatly fear scorpions not because scorpions seek out and attack people, but because an accidental encounter with a scorpion hiding in a shoe or a corner can result in a painful and possibly deadly sting. Only about 20 of the 2,000 species are lethal to humans, but these cause 10 times as many human deaths as do snakebites, mostly in the Middle East and North Africa. The only deadly species in the United States is the Arizona bark scorpion (Centruroides exilicauda). Its sting, if untreated, kills fewer than 1 percent of adults but up to a quarter of children. Adult scorpions are fluorescent in ultraviolet light; blacklights are used to locate scorpions at night.

first entry Among the groups that resemble scorpions are the following. ●●

●●

The other major group of arachnids is the mites and ticks. Mites and ticks are small and have little visible segmentation. They often have eight legs, but some, such as the follicle mite, Demodex folliculorum, and the larva of the deer tick, Ixodes damminnii, have fewer. Ticks and mites have mouthparts that can bite, sting, saw, or suck. Herbivorous mites can be major agricultural pests. Follicle mites are harmless and live in the follicles of human eyelashes, although under some conditions they can cause an immune response. Mites can also be predators or parasites. Chiggers (genus Trombicula) are immature mites that dig into human skin by mistake, where they die, as they cannot complete their development on a human host—small comfort to the host. Some mites live in carpet dust or pillows, where they consume dead cells. They are harmless except when they cause allergic reactions in humans. Most ticks are small external parasites that feed on the blood of vertebrates. The first immature stage hatches in the spring and waits on branches and leaves to encounter a host. After feeding until enormously swollen, the immature tick falls off, molts into a second immature stage, and finds another host. After it feeds this second time, it falls off, molts into adulthood, and finds its final host. Ticks and mites can sometimes be harmful to humans, mainly because they transmit microbial diseases such as Lyme disease. Two of the lesser-known groups of nonarachnid chelicerates are the following. ●●

An emperor scorpion  (Reptile Apartment)

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Pseudoscorpions are not scorpions. Although they have large pincers with venom, they do not have stinging tails. Whip scorpions are also not true scorpions. Their tails may appear whiplike. There are several groups of whip scorpions. The tailless whip scorpions have front sensory legs that can be very large relative to their bodies, up to 10 inches (25 cm) long. Microwhip scorpions use their pedipalps for walking and their front legs as sensory structures. The vinegaroons also use their front legs as sensory structures and have long tails without stingers. The split-middle whipscorpions appear to have three body parts because the thorax has two plates.

Sea spiders (Pycnogonida) are usually small, and their muscles often consist of just one muscle cell. Some Antarctic species can be

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arthropods 

●●

almost three feet (90 cm) in diameter, which includes the legs. Most have eight legs, though the number can vary. Only four species of horseshoe crabs (Xyphosura) survive from a group that was abundant in the Paleozoic era. Largely unchanged in anatomy since that time, they have been considered one of the best examples of “living fossils.” They are not true crabs. Atlantic horseshoe crabs (Limulus polyphemus), about a foot (less than half a meter) in length, can be very abundant when they come ashore to breed during spring high tides of full and new moons. The female can lay 20,000 eggs. A large carapace covers the cephalothorax. They have five pairs of walking legs, the first four of which are also used to process food. As in many arthropods, the blood of horseshoe crabs contains blue, copper-based hemocyanin rather than red, iron-based hemoglobin.

Insects and their Relatives Insects and their relatives are by far the most numerous and diverse arthropods. The world could not function without more than 1 million species of insects. At any given moment, there are a billion billion (1018) insects on the planet. As herbivores, carnivores, pollinators, and decomposers, they play a greater role in the flow of energy and matter through Earth’s ecosystem than any other group. About 800 species of insects have become pests of agricultural crops. On the other hand, three-quarters of all commercial crops depend on bees for pollination. Flight has allowed insects to evolve many different pollination relationships with plants; the evolution of pollination relationships may have been the most important factor that contributed to the evolution of insect diversity. Because of their ecological and evolutionary importance, the insects have their own encyclopedia entry. Insects have three body parts and six legs. The abdomen contains digestive and reproductive organs. Their six legs emerge from the thorax. The head has many appendages, including antennae and many mouthparts. Instead of jaws and tongues, insects have appendages that are modified into structures that fulfill the same roles. Many adult insects have a proboscis mouthpart with which they can penetrate the tissues of plants or animals. Some tiny arthropods that live in soil have six legs but do not have three body parts. Therefore, most scientists classify them separately from the insects. The evolution of wings, unique among arthropods, is one of the insects’ most important terrestrial adaptations. Wings allow some insects to travel at

xviii+598_Biodiversity_F.indd 37

37

great speeds. The sphinx moth can fly at 1,000 body lengths per second. A jet flying at three times the speed of sound travels only 100 body lengths per second. In addition to speed, wings allow insects tremendous maneuverability. Most modern insects are either amphibious (living first in water, then on land) or entirely terrestrial. The first insects lived partly or wholly on land; a few modern insects have returned to an entirely aquatic existence. Insects develop from juvenile to adult by passing through a series of molts, or instars. Some insects, such as grasshoppers, have relatively simple life cycles, in which the juvenile insect that hatches from the egg closely resembles the adult. Wings may develop only on the final instar. Other insects undergo metamorphosis. They have a larval stage that looks almost completely different from the adult, as “grubs” bear little resemblance to adult beetles or bees, nor caterpillars to butterflies. The larvae are almost always adapted as “eating machines,” while the adults, which devote themselves to reproduction, eat much less, if anything at all. In amphibious insects, such as the dragonfly, the juvenile stage lives underwater, but the adult lives on land and in the air. Examples of ecologically and economically important groups of insects are the following. Coleopterans. There are more species of beetles (order Coleoptera, sheath-winged) than of any other group of organisms in the world—at least 300,000 species, which is a quarter of all the species of organisms that are known in the world! With such diversity, beetles fill almost every ecological role. Some, such as the potato beetle and the boll weevil, are crop pests, while others, such as the ladybird beetle, eat crop pests. “Lightning bugs” are actually beetles. Their grubs pupate before developing into adults. Lepidopterans. Adult butterflies and moths have four usually colorful scaly wings. Moths often have brushy antennae, dusky wings, and nocturnal habits. The brushy antennae allow the male moths to detect even a few molecules of female sex attractant, which guide the male many kilometers to a mate. Butterflies are often diurnal and have more wirelike antennae and colorful wings. The larvae of this order are caterpillars, with three pairs of jointed legs in front, followed by numerous pairs of prolegs, which are stubby projections with bristles. Like beetle grubs, caterpillars are specialized to do mostly one thing: eat. The larva pupates as a cocoon (in moths) or a chrysalis (in butterflies), allowing a striking metamorphosis to occur, including the development of wings and a change of mouthparts from chewing mandibles to hollow sucking mouthparts. Caterpillars can devastate large areas of cropland or forest.

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38 38 arthropods  Many adults, however, are important pollinators of wild and domesticated plants. Hymenopterans. Ants, bees, and wasps often have complex social systems. Many species live in colonies of individuals that hatch from eggs all laid by the same large, fertile female, the queen. The fertilized eggs develop only into females, while unfertilized eggs develop into male drones. Female honeybee larvae that receive regular food develop into workers, which perform many different jobs. Worker honeybees do not lay eggs, as their egg duct is modified into a stinger. Some hymenopterans, especially wasps, are important to agriculture because they either hunt or parasitize the caterpillars that cause much crop damage and loss. Dipterans. Adult flies and mosquitoes can be pollinators but are often parasites that spread disease. An adult mosquito eats little, if anything, but the female requires blood for the production of eggs. She seeks warm-blooded vertebrates by flying toward heat and carbon dioxide. Mosquitoes spread several diseases, such as malaria and various viral fevers. Eradication of certain species of mosquitoes has been a major focus of public health efforts. Fly larvae can be parasitic (for example, the bot flies in cattle), but most maggots are decomposers. Orthopterans. Since ancient times, grasshoppers and locusts have been major insect pests. Even today, plagues of locusts can occur on the same level as those described in ancient biblical records. Isopterans. Termites are also social insects. Members of their colonies all hatch from eggs fertilized by a male king and laid by a large, fertile queen. Some of the eggs develop into males, some into females. Termites eat wood and other plant materials. Many termites, however, cannot digest wood. They rely on microbes in their guts to digest cellulose. Although many termites damage human structures, they are very important decomposers, especially in semiarid regions, and make a major contribution to the carbon cycle. Homopterans. Insects in the order Homoptera, especially the aphids, also damage crop plants. Aphids have piercing mouthparts that insert into the plant cells that carry sap. Because plant sap is pressurized, the aphids do not even need to drink; they let the plant pump the food through them faster than they can digest it. As a result, aphid excrement is mostly sap, which can drip on many things, such as a car that stands beneath an aphid-infested tree. Ants may tend aphids as cowboys tend cattle, eating some of the sap that the aphids have funneled out. A homopteran, besides sucking sap, can spread microbial diseases from one plant to another by its proboscis. Aphid infestations can be controlled by ladybird beetle larvae or adults or by spraying them with soap.

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first entry Siphonapterans. Fleas spread several diseases, most notably bubonic plague. They are flattened vertically, which allows them to cling closely to the skin and hair of hosts. The human flea, Pulex irritans, does not spread plague; plague bacteria are not spread from one human to another by flea bites. The rat flea, Xenopsylla cheopsis, prefers to bite rats. When the rats die from plague or the fleas’ throats are blocked by the plague bacteria, fleas may bite humans, thereby spreading plague from rats to the humans. Anoplurans. Lice can be distinguished from fleas by their horizontal, rather than vertical, flattening. The flat bodies of lice, like those of fleas, are not easily scratched off. Lice spread such diseases as typhus from one human to another under unsanitary conditions. Many insects become pests when their populations get out of control. Massive use of pesticides has not only failed to control them but has resulted in the evolution of superpests. Modern agricultural researchers now realize that the best and only permanent control of insect pests is to release diseases, predators, or parasites to kill the pests or release sterilized adults of the pest species that will mix with the pest population and reduce its reproductive success. In addition, if humans try to spray all insect pests, they will also kill the many insects that are not only beneficial but also essential, especially the pollinators. Insects may provide great medical benefits. Medicines may be ineffective against some infected wounds, but doctors can sometimes use maggots— yes, the larvae of flies—for debridement, which is cleaning out decaying flesh from a wound! Scientists have wondered why some insects, such as ants, can live in dense populations without having outbreaks of disease. It appears to be because these insects produce antibiotics that protect them. In the continual search for new antibiotics, researchers may have to turn to insects. See also crustaceans; insects; living fossils; spiders. Further Reading Beccaloni, Jan. Arachnids. Berkeley: University of California Press, 2009. Berenbaum, May. Bugs in the System: Insects and Their Impact on Human Affairs. Upper Saddle River, N.J.: Addison-Wesley, 1996. ———. Buzzwords: A Scientist Muses on Sex, Bugs, and Rock ‘n’ Roll. Washington, D.C.: National Academies Press, 2000. Eisner, Thomas. For Love of Insects. Cambridge, Mass.: Harvard University Press, 2003. ———, and Jerrold Meinwald. “Defensive secretions of arthropods.” Science 153 (1966): 1,341–1,350.

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arthropods  Farinós, Gema P., et al. “Diversity and seasonal phenology of aboveground arthropods in conventional and transgenic maize crops in Central Spain.” Biological Control 44 (2008): 362–371. Farmer, Edward E., and Lucie Dubugnon. “Detritivorous crustaceans become herbivores on jasmonate-deficient plants.” Proceedings of the National Academy of Sciences USA 106 (2009): 935–940. Fountain, Henry. “Competing for food, beetle becomes a killer.” Available online. New York Times, January 27, 2009. URL: http://www.nytimes.com/2009/01/27/ science/27obdung.html. Accessed May 12, 2011. Franks, N. R. “Army ants: A collective intelligence.” American Scientist 77 (1989): 139–145. Hillyard, Paul. The Private Life of Spiders. Princeton, N.J.: Princeton University Press, 2008. Hölldobler, Bert, and Edward O. Wilson. The Ants. Cambridge, Mass.: Harvard University Press, 1990. Richmond, Sonya, and David C. Lasenby. “The behavioural response of mayfly nymphs (Stenonema sp.) to chemical cues from crayfish (Orconectes rusticus). Hydrobiologia 560 (2006): 335–343. Sargent, William. Crab Wars: A Tale of Horseshoe Crabs, Bioterrorism, and Human Health. Lebanon, N.H.: University Press of New England, 2006. Sharley, David J., et al. “The effects of soil tillage on beneficial invertebrates within the vineyard.” Agricultural and Forest Entomology 10 (2008): 233–243.

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Shuster, Carl N., et al., eds. The American Horseshoe Crab. Cambridge, Mass.: Harvard University Press, 2004. Snyder, Bruce A., and Paul F. Hendrix. “Current and potential roles of soil macroinvertebrates (earthworms, millipedes, and isopods) in ecological restoration.” Restoration Ecology 16 (2008): 629–636. ———, et al. “Competition between invasive earthworms (Amynthas corticis, Megascolecidae) and native North American millipedes (Pseudopolydesmus erasus, Polydesmidae): Effects on carbon cycling and soil structure.” Soil Biology and Biochemistry 41 (2009): 1,442–1,449. Thomas, Richard H. “Wingless insects and plucked chickens.” Science 299 (2003): 1,854–1,855. University of Delaware Sea Grant Program. “Horseshoe crab.” Available online. URL: http://www.ceoe.udel. edu/horseshoecrab. Accessed July 16, 2009. Weeks, Andrew R., et al. “A mite species that consists entirely of haploid females.” Science 292 (2001): 2,479–2,482. Willemart, Rodrigo H., et al. “Sexually dimorphic legs in a neotropical harvestman (Arachnida, Opiliones): Ornament or weapon?” Behavioural Processes 80 (2009): 51–59. Wu, Yanling, et al. “Anti-atherogenic effects of centipede acidic protein in rats fed an atherogenic diet.” Journal of Ethnopharmacology 12 (2009): 509–516.

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B bacteria  Of all the organisms in the world, bacteria are among the (1) smallest, (2) simplest, (3) most numerous, (4) most metabolically diverse, and (5) oldest. the bacteria share these distinctions with the morphologically similar archaea, which were once considered to be bacteria. Smallest. the typical bacterial cell is about 10 times smaller than the typical cell of complex organisms in each dimension. therefore, the typical bacterium has a volume 1,000 times smaller than that of a typical complex cell, although there are exceptions. the largest known bacterium is Thiomargarita namibiensis, which is 1/25th of an inch (1 mm) in diameter. this is larger than many eukaryotic cells. Simplest. Bacteria are prokaryotic, which means they do not have a nucleus (Greek, karyo). Human, plant, fungus, and protist cells are eukaryotic because they have a nucleus. Most bacteria have: ●









a cell wall, which consists mostly of a combination of protein and polysaccharide called peptidoglycan. Because Gram’s stain indicates the presence of peptidoglycan, the gram-positive bacteria are those with a thick cell wall, and the gram-negative bacteria have thinner cell walls. Some bacteria have a capsule covering outside the cell wall. a cell membrane, which regulates the molecules that can enter and leave the cell. all cells have cell membranes, although the chemical composition of archaea membranes is different from that of bacteria and of all other cells. cytoplasm, the liquid portion in which the molecules are dissolved.

ribosomes, which make proteins. Bacteria have smaller ribosomes than those of eukaryotic cells. a circular molecule of Dna. Bacterial Dna, in contrast to the Dna in eukaryotic chromosomes, is very efficiently used for genetic storage. that is, there is very little noncoding Dna. in some cases, bacterial genes are so compressed that they overlap. Bacteria also have small fragments of Dna called plasmids that can move from one bacterium to another, even of a different species. Bacterial Dna has sometimes been incorporated into eukaryotic chromosomes, a process called horizontal gene transfer. Few bacteria produce cholesterol; the ones that do may have obtained the gene from eukaryotic cells. the Dna can have as few as 160,000 base pairs (as in some degenerate bacteria that live inside eukaryotic cells) to as many as 12 million base pairs. Some bacteria, such as Borrelia burgdorferi, the germ that causes lyme disease, have a linear rather than circular Dna molecule.

Many bacteria also have fl agella (singular fl agellum), a whiplike structure that can move and propel the bacteria through a liquid medium. it is propelled by a protein-based rotor mechanism. the bacterial flagellum is different from the flagella and cilia of eukaryotic cells. the shapes of bacteria are relatively simple. Small, spherical bacteria are cocci (singular coccus), rod-shaped bacteria are bacilli (singular bacillus), and spiral bacteria are spirilla (singular spirillum). Spirochetes are tightly coiled around a central axis. 40

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bacteria  Many bacteria, particularly cocci, cluster in recognizable ways. Diplococci form pairs, streptococci form chains, and staphylococci form small clusters. Although most bacteria function as single cells, they can sometimes form long filaments, particularly the cyanobacteria and actinobacteria. Some of these filaments can be branched and resemble strands of fungi. Many bacteria grow in thick mats called biofilms. They can sometimes be a foot and a half (half a meter) thick and consist of several species of bacteria, archaeans, and protists. Biofilms are not merely mats of microbes. They can form complex channels. The bacteria release molecules (many of them with antibiotic properties when in higher concentrations) that influence one another’s gene expression. This allows quorum sensing, which informs the bacteria of how many other bacteria are in their immediate vicinity. Therefore, bacteria in different parts of the biofilm carry out different aspects of metabolism. Quorum sensing allows Vibrio fisheri to produce light, but only at high densities. (These bacteria are the source of bioluminescence for many marine animals.) Quorum sensing also allows the bacteria in the outer layers of Pseudomonas aeruginosa colonies to disperse to new locations more readily than bacteria in the inner layers. Some multispecies biofilms are mutualistic. Anaerobic bacteria may produce hydrogen, which methanogenic archaeans consume within the same biofilm. Under certain conditions, the soil bacterium Myxococcus xanthus can form multicellular reproductive structures. Most numerous. Bacteria and archaeans are the most numerous cells in the world. A typical spoonful of soil can contain billions of bacteria. According to one estimate, there are 5 × 1030 bacteria and archaeans on Earth. One of the reasons they are so numerous is that they can reproduce rapidly under optimal

41

conditions. One bacterial cell divides into two identical bacterial cells by binary fission. In some species, this process can take less than 10 minutes. Most metabolically diverse. Bacteria are the most diverse cells in the world in terms of the metabolic reactions they perform. Even bacteria that have similar appearances can have very different types of metabolisms (see table): ●●

●●

●●

Many bacteria obtain energy the same way that animal cells do: by digesting organic molecules. Some of them live in the presence of oxygen and release energy through aerobic respiration, like most animal cells; some live in the absence of oxygen and rely on fermentation. Some bacteria (in particular, the cyanobacteria) use sunlight energy to make food molecules in the same way that plants do. Some bacteria obtain energy using processes of which no eukaryotic cell is capable. Some photosynthetic bacteria use hydrogen sulfide (H 2S) rather than water (H 2O) as an electron source and release sulfur atoms instead of oxygen gas. Chemosynthetic bacteria obtain energy from inorganic chemical reactions. Some chemosynthetic sulfur bacteria oxidize hydrogen sulfide. Other chemosynthetic bacteria oxidize ions, such as ferrous (Fe2+) into ferric (Fe3+), ammonia (NH4+) into nitrite (NO2-), and nitrite into nitrate (NO3 -). The hydrogen sulfide bacteria are often found at deep sea vents that spew out water that contains this gas. In such places, chemosynthetic bacteria are the basis of the entire food chain. Bacterial metabolism has been important in the production of mineral

Diversity of Bacterial Metabolism Source of Energy or Electrons

Metabolism

Category

Heterotrophic

Aerobic

Obtain food from organic molecules

Live in presence of oxygen gas

Anaerobic

Obtain food from organic molecules

Live in absence of oxygen gas

Cyanobacteria Sulfur bacteria

Split H2O molecules Split H2S molecules

Live in aerated water Live in anaerobic water, low light

Energy from H2S Energy from metals Energy from NH3

Deep ocean vents Rocks Anaerobic soil

Autotrophic photosynthetic (energy from sunlight) Autotrophic chemosynthetic (energy from inorganic molecules)

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Habitat

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42 42 bacteria  deposits. Although bacteria do not metabolize gold, they filter it from seawater and produce gold deposits. Bacteria can carry out such a wide range of chemical activities that they are used for many economically and environmentally important processes. Many bacteria play essential roles in food processing, especially of dairy products such as butter, cheese, and yogurt. Bacteria, especially those that have been genetically engineered, produce important industrial chemicals. Many pharmaceutical chemicals are most effective if only one mirror-image form of the molecule is produced. It is difficult for inorganic industrial processes to produce just one mirror image, but bacterial enzymes do it easily and consistently. There are bacteria that can break down crude oil; these bacteria have already proven useful in helping to clean up oil spills. There are bacteria that can break down almost any toxic compound, and it is just a matter of finding them. Searching for technologically useful bacteria is an important part of bioprospecting, which is the search for wild species of organisms that do or produce something useful in the human economy. It is especially in bioprospecting that the importance of bacterial biodiversity can be seen. Oldest. Bacteria and archaeans were the first life forms on Earth. They probably existed 3.5 billion years ago, and it was nearly 2 billion years later that the first eukaryotic cells evolved. The earliest cell fossils, such as those found in the 3.5 billion-year-old Apex chert, are of types that, if they lived today, would be classified as bacteria. Throughout the Archaean era, the entire world was bacterial. Throughout the Proterozoic, the world was mostly microbial, shared between prokaryotes and eukaryotes. Only in the last 540 million years (the last 14 percent of Earth history since the beginning of the Archaean era) have multicellular organisms been numerous. The evolutionary biologist Stephen Jay Gould points out that in every age of Earth’s history, bacteria have been the modal type of organism. Bacteria have a bad reputation. Many people look upon them as agents of disease. There are hundreds of examples of diseases caused by bacteria, particularly in animals, but for every kind of bacteria that causes a disease, there are many that are harmless or beneficial to humans. Bacteria are essential to the survival of all organisms and to the function of all ecosystems on Earth. According to the ecologist Paul Falkowski, bacteria and other microbes are the foundation of all metabolism on Earth. All aerobic respiration depends on mitochondria, which are the degener-

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first entry ate evolutionary descendants of proteobacteria, and photosynthesis occurs in chloroplasts, which are the descendants of cyanobacteria. The bacterial ancestors of chloroplasts and bacteria took up residence inside ancestral eukaryotic cells, a process called symbiogenesis, but even ignoring the symbiogenetic descendants of bacteria in eukaryotic cells, bacteria perform essential functions, such as the following. ●●

●●

●●

●●

Bacteria, along with fungi, are the principal decomposers. Without them, carbon would not become available for photosynthesis and the food chain. Actinobacteria are decomposers that produce the “smell of rain,” the refreshing scent that comes from dry soil when it first becomes wet. Bacteria perform some unique chemical reactions that are important and perhaps necessary for the ecosystems of Earth. In particular, some bacteria carry out nitrogen fixation, by which they transform atmospheric nitrogen gas (N2) into ammonia (NH3), which can then be oxidized into other forms, such as nitrite (NO2-) and nitrate (NO3 -). Ammonia, nitrite, and nitrate are essential soil nutrients upon which the entire food chain depends. Many nitrogen-fixing bacteria live in the root nodules of plants, such as the Rhizobium bacteria in leguminous plants and the Frankia bacteria in the roots of alder trees. They obtain N2 from the air that penetrates into the soil. Another unique chemical reaction carried out by some bacteria is denitrification, which transforms nitrogen-containing molecules back into N2 . There are many independently living photosynthetic bacteria. Bacteria exhibit several different forms of photosynthesis. Cyanobacteria (previously known as blue-green algae) have the same kind of photosynthesis as the chloroplasts that evolved from them. A large amount of energy that enters aquatic food chains does so through cyanobacterial photosynthesis. Prochlorococcus, a genus of cyanobacteria discovered in 1988, is found in oceans throughout the world and may be the most abundant kind of cell on Earth. Bacteria live on and in the bodies of every organism, including humans. A human body consists of about 70 trillion human cells and about 700 trillion bacterial cells. That is, only one 10th of a person’s cells are human. Bacteria live all over the skin and consume dead skin cells and oils. They are particularly abundant in warm, moist areas.

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bacteria  They also live in the mouth and digestive tract, particularly the intestines, which have about 15 billion bacteria per cubic inch (1 billion per cubic centimeter). Perhaps the best known is Escherichia coli, or E. coli, which is one of the most common bacteria of research and teaching laboratories. Many of them are harmless and cause no more inconvenience than odors or gas. Other bacteria of the human body are mutualistic. Each part of the human body has a unique community of bacteria. The bacteria that live on the inside of the elbow, for example, are different from those that live on the outside. Harmless bacteria on the skin and in the intestines can depress the growth of dangerous bacteria that might otherwise grow there. Some bacteria that live in human intestines produce vitamins. Bacteria of the genus Lactobacillus are particularly beneficial in human intestines. Digestive bacteria in ruminant mammals break down otherwise indigestible cellulose, which is an abundant component of plant material, allowing these mammals to obtain much more food value from the plant material they have eaten. Bacteria, therefore, are major components not only of the external environments but also the internal environments of organisms. The total number of bacterial species is impossible to calculate. Some studies suggest that a spoonful of soil contains thousands of kinds of bacteria, while a different spoonful of soil from a different location contains thousands of other kinds of bacteria. Because they have simple structures, they can be distinguished mainly by their metabolisms, but scientists have to know what that metabolism is in order to grow them and study them. There are many kinds of bacteria whose presence researchers overlook because they cannot grow them properly. Recently, biotechnology has provided new ways of identifying bacteria on the basis of their DNA without having to grow them in a laboratory. These methods have revealed that a quart (liter) of seawater can have 12,000 species of bacteria. Many bacteria have been identified only, and scientists do not understand how they live or what role they may play in ecosystems. For example, Nitrospira moscoviensis was discovered in 1995 in a corroded heating pipe in Moscow; it is genetically distinctive enough to be classified into its own division, but there is little else to distinguish this division from others. Bacteria have been classified, on the basis of DNA and metabolism, into 17 divisions (see table on page 44).

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Many scientists speculate that there is more life under Earth than on top of it and that this life consists of bacteria and archaeans. They obtain energy from minerals and live in the wet cracks in rocks up to two miles (almost 4 km) below the surface, metabolizing very slowly (dividing perhaps once a century). Some scientists estimate that the bacteria of these “subsurface lithoautotrophic microbial ecosystems” (abbreviated SliME) would cover the surface of the Earth to a depth of five feet (almost 2 m) if they were concentrated. Many kinds of bacteria can tolerate extreme environmental conditions. Some bacilli, such as Bacillus and Clostridium, form endospores in which the DNA and a small amount of cytoplasm are protected inside an impervious coat. Endospores have no detectable metabolism and can survive ultraviolet and gamma irradiation, chemicals, pressure, heat, and desiccation. Boiling water is not enough to destroy endospores; it is principally to destroy the endospores of toxic bacteria such as botulism (Clostridium botulinum) that high-pressure canning methods must be used to store moist food. Some bacteria can not only survive but also grow under extreme conditions: high temperatures, strong acid, or concentrated salt, all conditions that would kill eukaryotic cells. For example, Thiobacillus concretivorans grows in sulfuric acid at concentrations that would dissolve metal. Acidithiobacillus ferooxidans makes food by using energy from iron and sulfur while living in sulfuric acid. Other bacteria can tolerate extremely basic conditions. Deinococcus radiodurans can live in the water tanks of nuclear reactors. It resists nuclear radiation because it has a unique ability to reform its DNA after damage by radiation. Streptococcus mitis was found inside the lens of a camera that was left on the Moon for two years. Bacteria live even in deep ocean vents so hot that the temperature probes start to melt. Thermus aquaticus (shortened to Taq), which lives in hot springs, is the source of an enzyme that copies DNA at high temperatures and is therefore very useful in genetic engineering. Some bacteria have been reported to survive in suspended animation for up to 250 million years. The ability of bacteria to exchange fragments of DNA confers upon them the ability to evolve rapidly. Rather than having to wait for a new mutation to arise, a bacterium might be lucky enough to obtain a new gene from another bacterium, even of a different species. This is the principal reason that pathogenic bacteria can evolve resistance to antibiotics so rapidly. For example, the green sulfur bacteria (which use hydrogen sulfide as an electron source in photosynthesis) have only one set of reactions for absorbing and using light energy. The ­cyanobacteria,

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44 44 bacteria 

first entry Examples of Bacterial Divisions

Division

Description

Example

Acidobacteria

Bacteria in acidic conditions

Acidobacterium

Actinobacteria

Filamentous decomposers

Streptomyces

Aquificae

Bacteria of hot water vents

Aquifex

Bacteroidetes

Bacteria of soil, water, and guts

Bacteroides

Chlamydiae

Intracellular pathogens

Chlamydia

Chlorobi

Green sulfur bacteria

Chlorobium

Chloroflexi

Green nonsulfur bacteria

Chloroflexus

Chrysogenetes

A bacterium that reduces arsenic

Chrysogenes

Cyanobacteria

Most photosynthetic bacteria

Prochlorococcus

Deinococcus-Thermus

Bacteria that resist radiation and heat

Deinococcus

Dictyoglomi

Extremely heat-resistant bacterium

Dictyoglomus

Fibrobacteres

Digests cellulose in ruminants

Fibrobacter

Firmicutes

Gram-positive bacteria

Bacillus Clostridium Lactobacillus Staphylococcus

Planctomycetes

Aquatic bacteria

Planctomyces

Proteobacteria

Pathogens, nitrogen fixers, and purple photosynthetic bacteria

Escherichia Rhizobium Rhodospirillum

Spirochaetes

Spirochetes

Treponema

Thermotogae

Hot water bacteria with outer coat

Thermotoga

on the other hand, have two; one of them is very similar to that of the green sulfur bacteria, and that is the source from which it may have come. The ability of bacteria to exchange DNA has also made it very difficult to reconstruct evolutionary lineages of bacteria. The membrane of a modern eukaryotic cell (such as a human cell) resembles that of bacteria, while the nucleus of a modern eukaryotic cell contains histones, such as those associated with the DNA of archaeans. This constitutes evidence for the theory, increasingly accepted among evolutionary scientists, that the eukaryotic cell came into existence when a small archaean penetrated a larger bacterium and formed a mutualistic association, followed by the uptake of bacterial DNA by the archaean, which became the nucleus. If this is true, then bacteria and archaeans are not evolutionary sideshows left over from the distant past but are

xviii+598_Biodiversity_F.indd 44

the partial ancestors of all complex life on Earth, including humans. See also archaea; biodiversity, resources for medicine; commensalism; eukaryotes; mutualism; parasitism; symbiogenesis. Further Reading Branda, S., et al. “Biofilms: The matrix revisited.” Trends in Microbiology 13 (2005): 20–26. Cano, R., and M. Borucki. “Revival and identification of bacterial spores in 25- to 40-million-year-old Dominican amber.” Science 268 (1995): 1,060–1,064. Chattopadhyay, A., et al. “Bacterial insecticidal toxins.” Critical Reviews in Microbiology 30 (2004): 33–54. Chivian, Dylan, et al. “Environmental genomics reveals a single-species ecosystem deep within Earth.” Science 322 (2008): 275–278. Cohen, Y. “Bioremediation of oil by marine microbial mats.” International Microbiology 5 (2002): 189–193.

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Bates, Henry Walter Curtis, T., et al. “Estimating prokaryotic diversity and its limits.” Proceedings of the National Academy of Sciences USA 99 (2002): 10,494–10,499. DasSarma, Shiladitya. “Extreme microbes.” American Scientist 95 (2007): 224–231. DeLong, E., and N. Pace. “Environmental diversity of bacteria and archaea.” Systematic Biology 50 (2001): 470–478. Dexter-Dyer, Betsey. A Field Guide to Bacteria. Ithaca, N.Y.: Cornell University Press, 2003. DiGiulio, M. “The universal ancestor and the ancestor of bacteria were hyperthermophiles.” Journal of Molecular Evolution 57 (2003): 721–730. Eagon, R. “Pseudomonas natriegens, a marine bacterium with a generation time of less than 10 minutes.” Journal of Bacteriology 83 (1962): 736–737. Falkowski, Paul G., et al. “The microbial engines that drive Earth’s biogeochemical cycles.” Science 320 (2008): 1,034–1,039. Fraser, Christophe, et al. “The bacterial species challenge: Making sense of genetic and ecological diversity.” Science 323 (2009): 741–746. Gorbach, S. “Lactic acid bacteria and human health.” Annals of Medicine 22 (1990): 37–41. Guerrero, R., et al. “Predatory prokaryotes: Predation and primary consumption evolved in bacteria.” Proceedings of the National Academy of Sciences USA 83 (1986): 2,138–2,142. Hinnebusch, J., and K. Tilly. “Linear plasmids and chromosomes in bacteria.” Molecular Microbiology 10 (1993): 917–922. Horner-Devine, M. C., et al. “An ecological perspective on bacterial biodiversity.” Proceedings of the Royal Society of London B (Biological Sciences) 271 (2004): 113–122. Johnson, Zackary I., et al. “Niche partitioning among Prochlorococcus ecotypes along ocean-scale environmental gradients.” Science 311 (2006): 1,737–1,740. Summary by Pennisi, Elizabeth, “How a marine bacterium adapts to multiple environments.” Science 311 (2006): 1,697. Ley, R., et al. “Obesity alters gut microbial ecology.” Proceedings of the National Academy of Sciences USA 102 (2005): 11,070–11,075. Mehta, Mausmi P., and John A. Baross. “Nitrogen fixation at 92 C by a hydrothermal vent archaeon.” Science 314 (2006): 1,783–1,786. Nakabachi, A., et al. “The 160-kilobase genome of the bacterial endosymbiont Carsonella.” Science 314 (2006): 267. Nicholson, W., et al. “Resistance of Bacillus endospores to extreme terrestrial and extraterrestrial environments.” Microbiology and Molecular Biology Review 64 (2000): 548–572. ———, et al. “The solar UV environment and bacterial spore UV resistance: Considerations for Earth-to-Mars

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transport by natural processes and human spaceflight.” Mutation and Resistance 571 (2005): 249–264. Reith, Frank, et al. “Biomineralization of gold: Biofilms on bacterioform gold.” Science 313 (2006): 233–236. Schulz, H., and B. Jorgensen. “Big bacteria.” Annual Review of Microbiology 55 (2001): 105–137. Stevens T. O., and J. P. McKinley. “Lithoautotrophic microbial ecosystems in deep basalt aquifers.” Science 270 (1995): 450–454. Velicer, G. J., and K. L. Stredwick. “Experimental social evolution with Myxococcus xanthus.” Antonie Van Leeuwenhoek 81 (2002): 155–164. Vreeland, R., et al. “Isolation of a 250 million-year-old halotolerant bacterium from a primary salt crystal.” Nature 407 (2000): 897–900. Whitman, W., et al. “Prokaryotes: The unseen majority.” Proceedings of the National Academy of Sciences USA 95 (1998): 6,578–6,583. Zimmer, Carl. Microcosm: E. coli and the New Science of Life. New York: Pantheon, 2009. Zoetendal, E., et al. “A microbial world within us.” Molecular Microbiology 59 (2006): 1,639–1,650.

Bates, Henry Walter  (1825–1892)  British  Naturalist  Born on February 8, 1825, Henry Walter Bates was a British naturalist who specialized in collecting and studying insects. His insights were very important to the modern understanding of biodiversity and coevolution. Bates befriended another British naturalist, Alfred Russel Wallace. In 1848, Bates and Wallace traveled together to the Amazon rain forest of South America, where both of them extensively collected insects and other animals. Wallace returned to England and then traveled to Indonesia, but Bates remained in the Amazon rain forest for 14 years. While studying Amazonian insects, Bates discovered that certain nonpoisonous species of heliconid butterflies had wing coloration patterns that resembled those of poisonous heliconid butterfly species. Bates considered this to be mimicry, which afforded protection to the nonpoisonous butterflies without the cost of producing the poison. Since Bates’s initial discovery, numerous other examples of mimicry have been found. This type of mimicry is now called Batesian mimicry, in contrast to Mullerian mimicry, in which numerous prey species converge upon a common set of warning coloration patterns. Bates’s discovery of mimicry contributed significantly to Charles Darwin’s work on evolution. Darwin cited Bates’s discovery in later editions of The Origin of Species. Bates and Darwin both maintained that such mimicry could not have resulted from the use and disuse of the structures involved and must have resulted from natural selection.

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46 46 Berenbaum, May Bates returned to England in 1862. He published an account of his work in the rain forest, The Naturalist on the River Amazons, in 1863. Bates continued scientific research and was elected a fellow of the Royal Society in 1881. He died on February 16, 1892. See also biodiversity, concept of; camouflage and mimicry; coevolution; Darwin, Charles; natural selection; Wallace, Alfred Russel. Further Reading Beddall, Barbara G. Wallace and Bates in the Tropics: An Introduction to the Theory of Natural Selection, Based on the Writings of Alfred Russel Wallace and Henry Walter Bates. London: Macmillan, 1969.

Berenbaum, May  See insects. biodiversity, concept of  Biodiversity is the

diversity of life. It is frequently defined as the number of species in a defined location (a forest, a country, or the Earth), but the concept of biodiversity incorporates other levels of diversity as well, including the following. Genetic diversity within populations. The preservation of biodiversity cannot be considered successful if a species is merely saved from extinction, for example as a single pair in a zoo. Natural selection works upon genetic diversity; if a species is to persist, it must be able to evolve, and a lack of genetic diversity prevents evolutionary adjustments. Moreover, harmful mutations show up more often in small populations than in larger ones. A species usually does not begin to lose genetic diversity until it has been driven close to extinction, but from that point forward, the loss of genetic diversity pushes the species ever closer to extinction, despite the best efforts of conservationists. Genetic diversity among populations. Different populations of a species have unique sets of alleles, either because natural selection has operated differently in the separate populations or due to genetic drift. If one population becomes extinct, this is considered a loss of biodiversity, even if the species survives. All wolves are in the species Canis lupus. However, there are different populations of wolves (different enough to be considered subspecies). The visible differences in coat color among these subspecies is only the most visible characteristic that makes them distinct. Diversity of ecological functions. It is misleading to think that the loss of one species from an ecological community with a hundred species is merely

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first entry a 1 percent loss of biodiversity in any meaningful sense, because different species can rarely substitute for one another. For example, if one member of a symbiotic relationship becomes extinct, the other may likewise become extinct. Of particular importance are keystone species, the disappearance of which may produce profound changes in an ecological community. One recently discovered example is that large herbivorous mammals were keystone species in the tundra and boreal forests that covered much of what is now the United States during the most recent ice age. The largest of these mammals became extinct at the end of that ice age, an event known as the Pleistocene extinction. Various reasons have been proposed for this extinction event, including changes in climate that altered the vegetation upon which these animals depended. A more careful study of the sequence of events during the Pleistocene extinction revealed that the populations of large mammals began to decline rapidly before there were changes in vegetation. That is, the vegetation changed because the mammals became rare, not the other way around. The huge amount of grazing for which these animals were responsible had kept forests from spreading and encouraged the growth of grasslands. With the extinction of these animals, the forests spread, and the accumulation of dead wood enhanced the frequency of fires. The extinction of mammoths and mastodons from a Pleistocene forest edge community is small when calculated on the basis of the number of species, but its effect was considerable. Diversity of higher taxonomic levels. Most ecologists consider a grassland plant community that consists of 100 species, all of which are grasses, to be less diverse than a grassland plant community that consists of 100 species, some of which are grasses and some of which are dicot wildflowers. The greater the number of genera, families, orders, classes, phyla, kingdoms, and domains, the more diverse an ecological community is considered to be. The Atlantic horseshoe crab (Limulus polyphemus) is but one species of many in the Atlantic Ocean, but its loss would be noticed more than the loss of just one of the many species of dinoflagellates in the same waters because it is (along with Tachypleus gigas and Carcinoscorpus rotundicaudatus) one of the last survivors of its evolutionary lineage, the xiphosuran arthropods. Nobody knows how many species there are. It is certain that many species remain unidentified, but it is impossible even to make a good estimate of the percentage of species that have not yet been identified. Nobody even knows how many species have been identified, as the accounts have been published in thousands of different scientific journals;

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biodiversity, patterns of  Minimum Estimates of Species Diversity in Eukaryotes Taxonomic Group

Estimated Number of Species

Protists (including algae)

80,000

Plants

270,000

Fungi

70,000

Nematodes

15,000

Mollusks

70,000

Vertebrates

45,000

Arthropods:

855,000

Crustaceans

40,000

Arachnids

75,000

Insects

720,000

Other animals

95,000

Total

About 1.5 million

Note: From Chivian and Bernstein

nobody looks at all of them. All the scientists who study biodiversity are specialists in some relatively narrow group of organisms. It has proven difficult even to establish an Internet database of known species. One such ongoing effort is the Encyclopedia of Life. The numbers in the table, taken from a recent book, are minimum estimates and not accepted by all experts. Most species on Earth are microbes. There may be 5 × 1030 individual microbes on Earth—more than the number of stars in the universe. Nobody knows how many species are represented in this total. There are at least 700 species of bacteria and archaeans in the human mouth. Scientists most readily identify species on the basis of their visible characteristics, of which microbes have few. The table does not even attempt to list the number of bacterial and archaean species. The few prokaryotic species that can be grown in a laboratory cannot readily be distinguished by physical or metabolic characteristics. Analysis of DNA is necessary for the identification of microbe species and is increasingly being used to identify plants and animals as well. See also biodiversity, quantification of; communities, ecological; DNA studies of biodiversity; extinction; founder effect and genetic drift; keystone species; mutualism; natural selection; Pleistocene extinction; population genetics.

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Further Reading Chivian, Eric, and Aaron Bernstein. Sustaining Life: How Human Health Depends on Biodiversity. New York: Oxford University Press, 2008. Encyclopedia of Life. “Encyclopedia of Life.” Available online. URL: http://www.eol.org. Accessed June 25, 2010. Gill, Jacquelyn L., et al. “Pleistocene megafaunal collapse, novel plant communities, and enhanced fire regimes in North America.” Science 326 (2009): 1,100–1,103. Summarized by Johnson, Christopher. “Megafaunal decline and fall.” Science 326 (2009): 1,072–1,073. Wilson, Edward O. The Diversity of Life. Cambridge, Mass.: Harvard University Press, 1992.

biodiversity, patterns of  Some parts of Earth have more species than do others. In particular, tropical latitudes (and to a certain extent low elevations at all latitudes) are home to more species than are temperate or polar latitudes. This pattern holds true when all species are considered and also within ecological or evolutionary groups of species, such as trees, mammals, or insects. There are a few exceptions: Parasites, aquatic plants, and aquatic mammals, such as seals, have no greater diversity in the Tropics than away from them. Ever since Alexander von Humboldt in the early 19th century, scientists have attempted to explain why some parts of Earth have more species than do others—and have yet to answer this deceptively simple question. Von Humboldt suggested that tropical forests had more plant species because the only plant or animal species that can live outside the Tropics are those that can avoid or resist damage from cold temperatures. A related observation is that deserts have fewer plant or animal species because they must have adaptations that allow them to avoid drought or to resist it by means of enhanced water absorption or reduced water loss. For many species, life appears to be easier in tropical climates. Nevertheless, why have more species not evolved adaptations to resist cold or dry conditions? While the adaptations that allow organisms to live in cold or dry conditions may be complex and costly, there is a benefit also: The species that are adapted to cold or dry conditions escape from competition with organisms not so adapted. These costly adaptations confer a survival advantage. It is generally true that, for most species, the edge of the distribution range toward higher resource concentrations (e.g., the equatorial edge) is determined by competition with other species, while the edge of the range toward lower resource concentrations (e.g., the poleward edge) is determined by tolerance of the climatic conditions. That is, most temperate animals and plants

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48 48 biodiversity, patterns of  could survive in the Tropics if they were sheltered from competition. Even so, why should it be easier for a species to compete with, or be eaten or parasitized by, other species in a jungle than to live in harsh conditions? It is even difficult to define what “harsh conditions” are—archaebacteria live in extremely hot, salty, or acidic conditions and cannot even survive in what most species would regard as benign conditions. More than 30 hypotheses have been proposed to explain global biodiversity patterns. Some of them are here examined, with a focus on terrestrial species.

Are Biodiversity Patterns an Illusion? Null models describe biodiversity patterns that would result even if species were randomly distributed on Earth’s dry land surface. One of them is called the mid-domain effect. It claims that if the ranges of species are distributed randomly, the ranges of most of them would overlap in the middle of a continent or island. The middle of a continent (the mid-domain) would therefore have the greatest species richness. One reason that the Tropics have so many species may be that they are the mid-domain of large continents. There are several other reasons why one might expect more species to evolve in the middle of a continent than near the edge, regardless of the climatic conditions on the continent. Large areas allow more opportunities for evolution in ways such as the following. They allow larger populations, thus enhancing the chances for evolution as well as reducing the chance of extinction; they contain more microhabitat diversity; and they may have fewer restrictions to gene flow between populations. In almost every case, a larger area contains more species. This is known as the species-area relationship. However, the relationship is not constant: Doubling a small area adds more species than doubling a large area. This occurs because both within-habitat and between-habitat diversity contribute to species richness in small areas, while only between-habitat diversity contributes to species richness in large areas. At first glance, the mid-domain effect cannot be true. All one has to do is look at the vast expanses of the northern continents, where relatively few species live in the tundra and northern forests. In North America, the tropical zone has relatively little landmass and yet has the most species. There is an important sense, however, in which the mid-domain effect may help explain tropical diversity. All the tropical regions within a continental region are in one place—the equator. The temperate regions, however, are divided between the Northern and Southern Hemispheres. Accord-

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first entry ing to this null model, temperate forests might have as many species as do tropical forests if all of them were in one place, but this explanation also does not go very far. Most of the temperate land surface of Earth is already in one place: the Northern Hemisphere. The Southern Hemisphere is mostly ocean. Large-scale measurements of biodiversity may disguise underlying biodiversity patterns. This, however, does not nullify the reality of the patterns. The greater number of mammal species in the Tropics is due mainly to the greater number of tropical bat species; other mammalian orders (such as dogs, cats, and ungulates) may not have a greater species richness in the Tropics. The greater diversity of the bats may have resulted from evolutionary events specific to them rather than from a general process that applies to all mammals. This explanation is not convincing, because there is a huge number of examples of evolutionary lineages that have diversified in the Tropics and far fewer that have diversified in the temperate or polar regions; bats are not an isolated example. The null models indicate that, in the absence of other factors, there would still be more species in some parts of the world than in others, but they do not appear to explain the patterns that actually exist.

Processes That May Explain Biodiversity Patterns Since the null models are not entirely adequate, what are some processes that could explain why some parts of Earth, particularly the Tropics, have more species than do other parts? Climate. On a worldwide scale, tropical rain forests have greater species diversity than any other ecological community. Some researchers attribute this to the great amount of energy (in the forms of temperature and of light) and water in rain forests. Bright sunlight and abundant moisture allow rain forests to have the world’s highest levels of productivity (growth of organisms), starting with photosynthesis and continuing up the food chain. If there is more energy flowing through the food chain, there can be more trophic levels and thus more species. The ecologist Bradford Hawkins and his associates analyzed 85 data sets of species; climate was the strongest predictor of species richness in 83 of the 85 data sets. Neither energy nor water can be considered alone; ecologists usually combine them into a variable known as potential evapotranspiration, which is the amount of water that could be removed from an area of land by evaporation and by transpiration of plants. Both low temperatures and low rainfall contribute to low evapotranspiration; both high temperatures and high rainfall contribute to high

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biodiversity, patterns of  evapotranspiration. Populations can grow faster, and fewer individuals die, in warmer, wetter conditions than in colder or drier conditions. Warmth and moisture enhance the growth of plants and animals, which promotes species diversity. On a smaller scale, however, the highest productivity is not always associated with the greatest number of species, especially if the high productivity results from abundant soil nutrients. Within tropical and temperate forests and grasslands, species richness is highest at intermediate levels of productivity. When productivity is very high, competition is strong, and rare species may be driven to extinction. In grasslands, for example, adding nutrients to the soil causes the dominant species to grow and cast shade on the less common species, often eliminating them. The ecologist Yann Hautier and his associates counteracted this process by experimentally providing supplemental light underneath the grass canopy along with extra nutrients in the soil. Similar patterns are found in aquatic habitats. On a worldwide scale, the most productive and diverse marine habitats are those that receive the most sunlight—that is, shallow tropical seas and coral reefs. Continental shelves also have more nutrients than do the open oceans, and this further stimulates the productivity of the food web. However, as on land, an overabundance of nutrients (for example, with eutrophication) results in a few species dominating the community. Rate of evolution. Evolution itself may run faster and produce more species under warm, wet conditions than under cool, dry conditions. One reason is that plants and cold-blooded animals have more generations per year in tropical forests, not only due to warmer temperatures but because there is no winter in these forests. Another reason is that mutations can occur more often under conditions of higher productivity. Both of these processes may allow natural selection to occur more rapidly in the tropics than in cooler or drier regions. This is apparently true not only of cold-blooded species but of warm-blooded species as well. The ecologist Shane Wright and his associates demonstrated that tropical mammals have 50 percent faster mutations than do related temperate mammals. Once biodiversity has begun to increase in a region, it feeds upon itself. As the ecologist Andrew Forbes wrote, “A major cause for biodiversity may be biodiversity itself. As new species form, they may create . . . a chain reaction of speciation events across trophic levels.” This process can continue all year long in a tropical forest, while in a temperate deciduous forest, it slows down or stops during the winter. Time for evolution. Another reason the Tropics contain so many species is that they have persisted

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49

for a long time. Particularly since the beginning of the Pleistocene epoch, the temperate zones in northern continents have experienced glaciations that have disrupted entire ecological communities. Glaciations also indirectly affected tropical forests as well: Periods of glaciation in the north resulted in drier conditions in the tropical zone. During these dry periods, however, the tropical forests contracted but were not totally displaced. Intense evolution has been going on without interruption in some tropical areas for hundreds of millions of years. The western Amazon has greater species richness than does the central Amazon, and this may be because the western Amazon remained forested throughout the Pleistocene droughts that turned central Amazonia into a savanna. Even within temperate zones, the regions most affected by glaciation in the past have fewer species today. For example, compare Europe, North America, and China. The temperate forests of China were little disturbed by the ice ages. North American deciduous forests recovered from the most recent ice age relatively quickly, as the north-south mountain ranges did not block the migration of species. European forests did not recover from the most recent Ice Age so well, because east-west mountain ranges and the Mediterranean Sea blocked the migration of some species. This may explain why Chinese forests have more species than do North American forests, which have more species than do European forests. Range of tolerance. Species that live in temperate, boreal, or arctic zones must tolerate a large (sometimes very large) annual range of temperature conditions. Without going anywhere, members of a temperate species experience conditions that correspond to a wide geographical range. In many cases, temperate species have wider geographical ranges, since they are already adapted to a wide range of temperature and moisture conditions. Tropical species experience relatively constant conditions and may specialize on a small geographical range. Despite the intuitive appeal of this hypothesis, there are many exceptions to it. Tree species in the New World Tropics, for example, may be exceedingly rare in any one location but have a wide geographical range. Many other factors contribute to species richness, such as a moderate level of disturbance. However, these factors do not differ consistently from one part of the world to another.

Why Are There So Many Tropical Species? Any combination of the foregoing processes may explain why tropical zones have more species than do temperate or polar zones, but they seem insufficient to explain the breathtaking species richness of (continues on page 52)

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50 50 biodiversity, patterns of 

first entry

“Why Are There So Many Species?” As explained in many entries in this encyclopedia, the number of species on Earth is literally incalculable. Scientists have described more than a million species, and many other species have recently or will soon become extinct as a result of human activity before they could or can be documented. There will probably never be a complete answer to the question of why there are so many species. Many pre-Darwinian scholars believed that God’s creation consisted of many levels, from rock to worm to plant to animal to man to angel, and that God had created something to fill in each of the gaps in the great fabric of being. This idea, known as the scala naturae, or great chain of being, was their explanation of why all levels of complexity existed in the natural world. It also led these scholars to believe in intermediate forms, such as half-human half-apes, even though they did not have any concept of evolution. To answer the question of why there are so many species by simply saying that God made the scala naturae was not satisfying even to theologians, who wanted to believe in something more than the Creator’s whim. Some pre-Darwinian scholars attempted to explain why some parts of Earth had more species than others, even though they could not explain why there were so many species or where they had come from. Alexander von Humboldt extensively explored the Tropics and observed their tremendous species diversity. He speculated that the warm, moist conditions of the Tropics allowed more species to survive than did the colder and drier regions of Earth. There were more species in the places where life was easier. Once Charles Darwin had presented evidence for evolution and explained how it could happen, scientists could investigate the origin of Earth’s astounding biodiversity. After life had begun, new species would evolve as they progressively adapted to new climates. Even before Darwin, geologists had known that the earliest life forms all lived in the oceans and that life on land existed only in

xviii+598_Biodiversity_F.indd 50

more recent geological ages, but this did not seem adequate to explain the sheer number of species, since there were not that many different climatic or geographical habitats to which organisms could adapt. Why were there so many species of beetles in the Tropics, a fact revealed by Darwin’s friends Henry Walter Bates and Alfred Russel Wallace, when they all appeared to be doing more or less the same things in the same places? Why would not the “struggle for existence” wipe many of them out, leaving only the species best adapted? Darwin expanded his concept of natural selection to include species evolving in response to one another (which scientists today call coevolution), and he explained the process of sexual selection. Coevolution and sexual selection could explain what natural selection in response to climate could not: New species could evolve in response to previous species by parasitizing them, eating them, or helping them, and even newer species could then evolve in the same fashion. New species could evolve that recognized different mating signals or decorations, of which there is a potentially limitless variety. Species diversity prompted the evolution of greater species diversity. Once biodiversity has begun to increase, it feeds upon itself. As ecologist Andrew Forbes wrote, “A major cause for biodiversity may be biodiversity itself. As new species form, they may create .  .  . a chain reaction of speciation events across trophic levels.” Furthermore, biodiversity could be propagated up the food chain. If there are more species of plants in one area than another, there can be more species of leaf-eating insects—a pattern confirmed by the ecologist Vojtek Novotny and his associates in the tropical forests. Still, scientists have not been happy with simply saying there are so many species because they evolved, any more than they would have been happy with the idea of God’s whim. Hence, rather than simply document each new species and speculate about how it might have

come into existence, each species an isolated story of evolution, they looked for general patterns. A 1959 article by the ecologist G. Evelyn Hutchinson (based on his presidential address to the American Society of Naturalists) claimed to address directly the question of why there were so many species of animals. Actually, Hutchinson turned the question around and laid the foundation for the modern scientific understanding of why there are not more species in the world than there are. Among his suggestions were the following.

• Food



chains. Hutchinson noted that, at each level of the food chain, the consumers were larger and rarer than the organisms they consumed. Many ecologists today refer to the “ten percent law,” indicating that each level of the food chain contains only about 10 percent as much energy and matter as the level below it. However, 10 percent is just an average figure; Hutchinson used 20 percent and calculated that if the oceans were full of single-celled algae and there were 50 links in the food chain, there would not be enough room in all the oceans to feed even one of those top predators. Natural selection, which operates within physical limits, cannot keep producing predators that eat predators that eat predators. Limiting similarity. Hutchinson also noted that two species that are too similar to each other cannot both survive in the same place. He noted that food-gathering structures of related animals living in the same location tended to differ by a factor of 1.3— that is, two species of similar animals could exist in the same place if one of them was larger by a factor of approximately 1.3. It was and is far from certain that this pattern and others like it are not simply random.

Hutchinson and many ecologists after him have pointed out ecological pro-

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51

biodiversity, patterns of 

cesses that could allow species to avoid driving one another to extinction. They include the following:

• Predator switching. Predators seldom







specialize entirely on one prey species. As a result, there is no predator species that will drive its single species of prey into extinction and then suffer extinction itself. Disturbance. Species differ in their life histories—that is, in how long they live and how much they reproduce. Some species grow slowly, live a long time, and produce few offspring; others grow quickly, have short lives, and produce many offspring. Species form a continuum between these two extremes. The short-lived, fecund species often live in areas recently disturbed by, for example, a forest fire. The fire clears away the dominant plants and makes resources such as light and nutrients available. The quickly growing plant species require the abundant resources made available by the fire. They grow quickly in the disturbed areas, which soon become thick with plants. The quickly growing species can no longer survive, nor can their seedlings grow, in the habitat that they have helped to make crowded. With animals as with plants, species with different life histories can live in the same place at the same time by living differently. Microhabitat specialization. A habitat may appear uniform to a human observer but actually consists of a great variety of small-scale conditions. To small organisms, the overall habitat is actually a collection of microhabitats. While this is undeniably true, it has only limited usefulness in explaining biodiversity. The ecologist Stephen Hubbell found that the trees of Barro Colorado Island in Panama appeared to be randomly distributed with respect to small disturbances and differences in slope and the direction the slope faced. Foraging specialization. The ecologist Robert MacArthur studied the foraging of warblers in trees. He found that different species of warblers specialized

xviii+598_Biodiversity_F.indd 51

on different portions of the trees— some near the top, some lower, some inside the branches, some on the outside. To birds, a tree is no more of a single habitat than is a whole forest. These and other processes allow large numbers of species to persist, once evolution has produced them—and evolution can produce a lot of species. One of the most obvious patterns of biodiversity is that it has increased over evolutionary time. Although more than 99 percent of all species that have ever lived are now extinct, more species have evolved than have become extinct. Ecological communities are therefore not just nurseries of new species but museums of old ones. It is not uncommon for newly discovered species to be “living fossils” that were presumed to have become extinct millions of years ago. This was the case with the dawn redwood (Metasequoia glyptostroboides) and the Wollemi pine (Wollemia nobilis). Part of the evolutionary explanation for why there are so many species may be historical contingency or evolutionary accident. Today there are a quarter of a million species of flowering plants (angiosperms). Since they came into existence about 120 million years ago, they have coevolved with insect pollinators as well as with other animals that disperse their seeds. Since insect diversity began to explode about the same time as the origin of flowering plants, it is likely that insects and flowering plants contributed to each other’s diversity. Coevolution is no accident, but the origin of the first flowering plants may have been. For about 290 million years after the first terrestrial life forms had evolved, the oceans had greater biodiversity than did the land. This changed quickly after the origin of the flowering plants, and now terrestrial species outnumber marine species 10 to one. Still, none of these explanations, singly or in combination, seems to do justice to the prodigious number of species in the world, particularly in tropical forests, where two and a half acres (a hectare) can have 250 species of trees, compared to 20 species in a North American decid-

uous forest of the same size. About 0.2 square miles (half a square kilometer) of tropical rain forest can contain more tree species than all of the temperate forests of Europe, North America, and Asia combined. In a Venezuelan rain forest, 978 species of beetles were found on just six trees. The mystery of why there are so many species is not simply that tropical rain forests are warm and wet or that coevolution produces incredible species diversity, but that the biodiversity of the Tropics compared to that of temperate zones seems wildly disproportionate. See also Bates, Henry Walter; biodiversity, concept of; biodiversity, patterns of biodiversity, quantification of; biogeography; coevolution; Darwin, Charles; disturbances, ecological; ecosystems; life history, diversity of; living fossils; natural selection; sexual selection; Wallace, A lfred Russel.

Further Reading Forbes, Andrew A., et al. “Sequential sympatric speciation across trophic levels.” Science 323 (2009): 776–779. Gilbert, Benjamin, and Martin J. Lechowicz. “Neutrality, niches, and dispersal in a temperate forest understory.” Proceedings of the National Academy of Sciences USA 101 (2004): 7,651–7,656. Hubbell, Stephen P. The Unified Neutral Theory of Biodiversity and Biogeography. Princeton, N.J.: Princeton University Press, 2001. Hutchinson, G. Evelyn. “Homage to Santa Rosalia or why are there so many kinds of animals?” American Naturalist 93 (1959): 145–159. Jablonski, David, et al. “Out of the tropics: Evolutionary dynamics of the latitudinal diversity gradient.” Science 314 (2006): 102–106. MacArthur, Robert H. “Population ecology of some warblers of northeastern coniferous forests.” Ecology 39 (1958): 599–619. Novotny, Vojtek, et al. “Why are there so many species of herbivorous insects in tropical rain forests?” Science 313 (2006): 1,115–1,118. Summary by Kitching, R. L. “Crafting the pieces of the diversity jigsaw puzzle.” Science 313 (2006): 1,055–1,057.

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52 52 biodiversity, patterns of  (continued from page 49) tropical rain forests. Two and a half acres (a hectare) of tropical forest can have 250 species of trees, compared to 20 species in a North American deciduous forest. About 0.2 square miles (half a square kilometer) of tropical rain forest can contain more tree species than all the temperate forests of Europe, North America, and Asia combined. Astonishing diversity also occurs within evolutionary groups in the tropics: One forest on Sarawak in Indonesia contains 27 species of hemiparasitic figs, and a forest in Ecuador has 34 species of palms. One reason (aside from reasons presented previously) that tropical rain forests have such a disproportionately large number of plant species may be that each one is attacked by specialized herbivores and parasites, as pointed out by the ecologist Dan Janzen. In temperate forests, a young acorn can grow into a mature oak tree in close proximity to its parent, though not in the parent’s shade. In tropical forests, a young tree that grows near its parent would quickly be killed by the herbivores and pests on the parent tree. This may be the reason that the individual trees of each species are often so widely separated from one another. Since no single tree species can usually dominate a canopy, there is literally room for many tree species to grow. This process occurs during the seedling stage. The ecologist Liza Comita and her colleagues, working with the ecologist Stephen Hubbell, found that seedlings of rare tropical forest tree species (which is to say, most of them) grow poorly near other members of the same species, while seedlings of common tree species grow well near other members of their species. Along with tree species diversity goes the diversity of small animals that specialize upon them. Trees defend their leaves with poisonous chemicals, each species using its own special toxic mix, and each tree species has herbivores that can detoxify that species’ particular mix of poisons. In contrast, tropical aphids do not have as much diversity as the tropical insects that eat leaves, since aphids drink nonpoisonous sap. Another reason may be that tropical forests have entire ways of living that are not readily available in other regions. In particular, much of the diversity of plant and animal species in tropical forests occurs in the epiphytic plants that live in the upper branches of the trees. Bromeliad plants capture pools of water, and orchids absorb water through aerial roots. Both create habitats for whole communities of animals. In temperate forests, it does not rain enough for many plant and animal species to live up in the branches, totally disconnected from the soil. If these explanations are the most important ones, it would follow that tropical forest species do not specialize upon particular microclimates. That

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first entry is, a small plot of tropical rain forest does not contain 250 tree species because it contains 250 distinguishable microclimates. The ecologist Stephen Hubbell found that the trees of Barro Colorado Island in Panama appeared to be randomly distributed with respect to small disturbances and differences in slope and the direction the slope faced. These large-scale ecological patterns may not apply to the more limited scale of biodiversity hotspots. Even though the Tropics contain the greatest number of species, most biodiversity hotspots are not tropical.

Why Are Most Species Terrestrial? About 90 percent of nonmicrobial species are terrestrial. In 1994, Robert M. May estimated 85 percent, and in 2009, Michael Benton estimated 95 percent, of species to be terrestrial. This pattern is true even of biodiversity hotspots: Less than half an acre (a hectare) of rain forest may have 475 tree species and 25,000 insect species, but the same area of coral reef (often called “rain forests of the oceans”) may have only 300 coral species, 600 fish species, and 200 algae species. One explanation proposed for lower marine biodiversity is the tremendous contribution of flowering plants to the evolution of terrestrial biodiversity. Sessile organisms (in which the adults do not move) have to disperse their eggs, sperm, seeds, or spores to new locations. In the oceans, water provides enough buoyant force to fulfill this role very well. Air is not as buoyant a medium for dispersal. On land, therefore, sessile organisms (mostly plants) usually rely on animals for dispersal. A tremendous burst of coevolution occurred when the flowering plants evolved on land about 120 million years ago. Moreover, the ecologists Rick Grosberg and Geerat Vermeij indicate that flowering plants have three to 10 times as much water supply per unit leaf surface area as do conifers. This simply allows them to grow more. Therefore, the greater biodiversity of terrestrial than of marine regions may be the direct and indirect result of the evolution of flowering plants. For about 290 million years, until flowering plants evolved, there were more species in the oceans than on land. The oceans, however, remain very poorly explored—not just the seafloors but also the intermediate depths—compared to land. It seems unlikely that a large enough trove of newly discovered marine species will be found to alter the assessment that most species are terrestrial. Of course, who knows for sure? Although shallow tropical seas may generally have the highest marine species diversity, there are exceptions. According to the ecologist Andrew Barton, phytoplankton hotspots do not form a tropical band but are found off the coasts of Japan, Baja

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biodiversity, patterns of  California, Newfoundland, and Argentina and are due mostly to the upwelling of deep ocean nutrients by marine currents.

Summary Tropical areas on land and in the oceans usually have more species than other regions because warmth and moisture on land and direct sunlight in water strongly promote the growth of plants and animals and evolution within their populations. However, in habitats with very high nutrient availability, a few dominant species may take over, which results in lower biodiversity. In addition, tropical regions have high biodiversity for historical reasons, such as less disruption during the ice ages. The main reason there are so many species of tropical trees may be that the trees cannot survive near their parents; hundreds of tree species are often spread out over the landscape. There are also more known species of organisms on land than in the oceans perhaps because of the explosion of coevolution that began 120 million years ago with the origin of the flowering plants. None of these reasons, individually or together, seems satisfactory to explain the breathtaking diversity of tropical forests. See also Essay: “Why Are There So Many Species?”; communities, ecological; deep oceans, biodiversity in; disturbances, ecological; Janzen, Daniel H.; population genetics; tropical rain forests and deforestation. Further Reading Adams, J. M., and F. Ian Woodward. “Patterns in tree species richness as a test of the glacial extinction hypothesis.” Nature 339 (1989): 699–701. Allen, A. P., et al. “Global biodiversity, biochemical kinetics, and the energetic-equivalence rule.” Science 297 (2002): 1,545–1,548. Barton, Andrew D., et al. “Patterns of diversity in marine phytoplankton.” Science 327 (2010): 1,509–1,511. Brown, J. H. “Two decades of homage to Santa Rosalia: Toward a general theory of diversity.” American Zoologist 21 (1981): 877–888. Clark, James S. “Individuals and the variation needed for high species diversity in forest trees.” Science 327 (2010): 1,129–1,132. Colwell, Rita K., and D. C. Lees. “The mid-domain effect: Geometric constraints on the geography of species richness.” Trends in Ecology and Evolution 15 (2000): 70–76. Comita, Liza S., et al. “Asymmetric density dependence shapes species abundances in a tropical tree community.” Science 329 (2010): 330–332. Connell, Joseph H. “Diversity in tropical rain forests and coral reefs.” Science 199 (1978): 1,302–1,310.

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53

———, and Eduardo Orias. “The ecological regulation of species diversity.” American Naturalist 98 (1964): 399–414. Crutsinger, Gregory M., et al. “Plant genotypic diversity predicts community structure and governs an ecosystem process.” Science 313 (2006): 966–968. Currie, D. J. “Energy and large-scale patterns of animaland plant-species richness.” American Naturalist 137 (1991): 27–49. ———, and V. Paquin. “Large-scale biogeographical patterns of species richness of trees.” Nature 329 (1987): 326–327. Forbes, Andrew A., et al. “Sequential sympatric speciation across trophic levels.” Science 323 (2009): 776–779. Gentry, Alwyn H. “Patterns of neotropical plant-species diversity.” Evolutionary Biology 15 (1982): 1–85. ———. “Tree species richness of upper Amazon forests.” Proceedings of the National Academy of Sciences USA 85 (1988): 156–159. Givnish, Thomas J. “On the causes of gradients in tropical tree diversity.” Journal of Ecology 87 (1999): 193–210. Grassle, J. F., and N. J. Maciolek. “Deep-sea species richness: Regional and local diversity estimates from quantitative bottom samples.” American Naturalist 139 (1992): 313–341. Hautier, Yann, et al. “Competition for light causes plant biodiversity loss after eutrophication.” Science 324 (2009): 636–638. Hawkins, Bradford A., et al. “Energy, water, and broadscale geographic patterns of species richness.” Ecology 84 (2003): 3,105–3,117. Hodgson, J. G. “Why do so few plant species exploit productive habitats? An investigation into cytology, plant strategies and abundance within a local flora.” Functional Ecology 1 (1987): 243–250. Hubbell, Stephen P. The Unified Neutral Theory of Biodiversity and Biogeography. Princeton, N.J.: Princeton University Press, 2001. Huston, M. “A general hypothesis of species diversity.” American Naturalist 113 (1979): 81–101. Hutchinson, G. Evelyn. “Homage to Santa Rosalia or why are there so many kinds of animals?” American Naturalist 93 (1959): 145–159. Janzen, Daniel H. “Why mountain passes are higher in the tropics.” American Naturalist 101 (1967): 233–249. ———. “Herbivores and the number of tree species in tropical forests.” American Naturalist 104 (1970): 501–528. Latham, R. E., and Robert E. Ricklefs. “Global patterns of tree species richness in moist forests: Energy-diversity theory does not account for variation in species richness.” Oikos 67 (1993): 325–333. Leigh, Egbert Giles, Jr., et al. “Why do some tropical forests have so many species of trees?” Biotropica 36 (2004): 447–473.

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54 54 biodiversity, quantification of  McKenna, Duane D., and Brian D. Farrell. “Tropical forests are both evolutionary cradles and museums of leaf beetle diversity.” Proceedings of the National Academy of Sciences USA 103 (2006): 10,947–10,951. Mittelbach, Gary G., et al. “What is the observed relationship between species richness and productivity?” Ecology 82 (2001): 2,381–2,396. Pärtel, Meelis, et al. “Contrasting plant productivity-diversity relationships across latitude: The role of evolutionary history.” Ecology 88 (2007): 1,091–1,097. Pennisi, Elizabeth. “On rarity and richness: Two scientists take a stab at explaining why oceans have far fewer species than terrestrial habitats.” Science 327 (2010): 1,318–1,319. Prance, Ghillean T., ed. Biological Diversification in the Tropics. New York: Columbia University Press, 1982. Ritchie, M. E., and H. Olff. “Spatial scaling laws yield a synthetic theory of biodiversity.” Nature 400 (1999): 557–560. Rohde, K. “Latitudinal gradients in species diversity: The search for the primary cause.” Oikos 65 (1992): 514–527. Rosenzweig, M. L. Species Diversity in Space and Time. Cambridge: Cambridge University Press, 1995. Snelgrove, P. V. R. “Getting to the bottom of marine biodiversity: Sedimentary habitats. BioScience 49 (1999): 129–138. Waide, R. B., et al. “The relationship between productivity and species richness.” Annual Review of Ecology and Systematics 30 (1999): 257–300. Willig, M. R., et al. “Latitudinal gradients of biodiversity: Pattern, process, scale, and synthesis.” Annual Review of Ecology and Systematics 34 (2003): 273–309. Willis, K. J., and R. J. Whittaker. “Species diversity: Scale matters.” Science 295 (2002): 1,245–1,248. Wright, Shane, et al. “The road from Santa Rosalia: A faster tempo of evolution in tropical climates.” Proceedings of the National Academy of Sciences USA 103 (2006): 7,718–7,722.

biodiversity, quantification of  Biodiversity

is usually considered to be the total number of species that exist in a defined area, although the concept also includes genetic diversity within species and the diversity of habitats and ecological communities. The quantification of biodiversity involves three problems: counting the species that exist in a defined area, calculating indices that reflect the relative importance of each species to the others, and determining how many of those species are “new to science,” that is, recognized as a distinct species by scientists.

Counting Species It would seem to be easy to determine how many species exist in a particular location: Go out, find

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first entry all the species, and write down their names. This was the approach used by early European scientific explorers, such as Joseph Banks, who accompanied Captain James Cook on his Polynesian expeditions, and Charles Darwin, who accompanied Captain Robert FitzRoy on his expedition to South America. The number of species in an area is known as species richness. In reality, it can be very difficult to do this. For example, the insect species in a tropical rain forest can be so numerous and so well hidden that they can be only indirectly counted. The ecologist Terry Irwin estimated insect species richness in a rain forest by choosing trees of different species, gassing them with insecticide, and catching and identifying the insects that fell from the trees. Not only did he find that a single tropical tree could contain as many insect species as some European countries, but that each species of tree had many of its own unique species of insects. Vast expertise is required to distinguish one species from another. Scientists typically work in teams, each scientist being an expert on a different group of organisms. For microbes, the look-and-count system is practically impossible. Scientists use DNA methods to quantify the species richness of microbes.

Biodiversity Indices The use of species richness as the only measurement of biodiversity conceals a great deal of information about the ecological community. In ecological and evolutionary terms, scientists distinguish between a community that contains, say, 50 equally abundant species and one that contains 50 species, 49 of which are rare. The first of these communities would be considered more diverse than the second, which is overwhelmingly dominated by a single species. Ecologists have, accordingly, devised different diversity indices (symbolized by H), rather than to rely simply on species richness. In order to calculate a diversity index, it is first necessary to determine the importance of the species in the community. This must be a numerical calculation rather than a value judgment by the investigator. Different investigators use different methods to calculate the relative importance of each species within a community. (Usually, these investigators focus on one group of organisms within an ecological community, such as a plant community or an insect community.) Ecologists such as John T. Curtis distinguished three factors that contributed to the importance of a species in a community, concepts that he developed for deciduous forest trees: ●●

Relative frequency. How many samples within the sampling area contain the species of interest? A common tree species may be

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biodiversity, quantification of 

●●

●●

found in all of them, a rare species in only one. Relative density. How many individuals of the species of interest are found in the sampling area? A common tree species will be represented by more individuals than will a rare species. Relative dominance. How much area does each tree species use within the sampling area? An important tree species, for example, will cover more area of ground than will a rare tree species. Sometimes, the relative dominance of a species of tree is calculated from its crown area, the area of ground shaded directly by its branches, and sometimes by its basal area, the cross-sectional area of its trunk.

Curtis and others calculated an importance value (IV) by adding all three (expressed as percentages) into a total, in which all species summed to 300. Importance values can be converted to proportions that add up to 1. Importance values can, in this way, be measured quickly in the field. Ecologists such as Robert Whittaker preferred the more laborious but much more informative measurement of net production, which is the net growth of each species. In the case of a plant species, this would be its total photosynthetic production minus the biomass lost through cellular respiration. By this measure, the most important species is the one that grows the most. In each of these indices, there are s species, and the proportional importance of the ith species is represented by pi. If one simply adds up all of these proportions, the result is 1. The indices are calculated by adding up mathematical derivatives of the proportions. One of these indices, Simpson’s diversity index, emphasizes the dominant species because it adds up the squares of the proportions:

a few dominant species, and the rest are rare. Equitability (E) is the diversity divided by the natural logarithm of the number of species: E = H/ln s Within the United States, Appalachian cove forests not only have many plant species, but these species are equitable. In contrast, a boreal forest has few species and low equitability. This can be illustrated by dominance-diversity curves. In these curves, the relative importance of each species (as a percent) is graphed against the species sequence (ranging from the most important to the least important species). The relative importances (on the vertical axis) are usually displayed on a logarithmic scale. While an infinite number of patterns is possible in a dominance-diversity curve, three general patterns are usually recognized: ●●

●●

●● s

H = ∑ pi 2 i =1

The other, the Shannon-Wiener diversity index, which is based upon information theory developed by the mathematicians Claude Shannon and Norbert Wiener, emphasizes the rare species because it multiplies each proportion by its natural logarithm: s

H = − ∑ pi ln pi i =1

Besides diversity, scientists can also quantify equitability. In a community of species with high equitability, the species are all about equally important; in a community with low equitability, there are

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55

The geometric series assumes that the community is divided among its component species by a constant proportion. For example, if the most important species has an importance of 50 percent, the second-most-important will have 25 percent importance, the next will have 12.5 percent importance, and so on. The resulting logarithmic dominancediversity curve is steep and straight. The MacArthur distribution assumes that the community is divided among its component species in a random fashion. As a result, there will be a few species that are very important, a few that are very rare, but most will be of intermediate importance. The dominance-diversity curve will display a gentle downward slope. It was proposed by the ecologist Robert MacArthur in the middle of the 20th century. The log-normal distribution assumes that the importance values have a normal, or bell-shaped, distribution. This, too, produces a gently sloping dominance-diversity curve, with few rare and few common species.

In general, communities that live in recently disturbed or extreme environments and have few species display a geometric series of importance values. An example is the vascular plants of the subalpine forest of the Great Smoky Mountains in Tennessee (see figure on page 56), based upon net production of each plant species. In communities that have more species, such as the vascular plants of a cove forest of the Great Smoky Mountains, the species divide up the resources more equably (see figure).

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56 56 biodiversity, quantification of

first entry

dISCovErING NEw SpECIES in nearly every habitat, researchers are discovering new species. this happens in two general ways. First, scientists can explore remote areas where few, if any, scientists have previously visited. Sir Joseph Banks, when he was the botanist on captain cook’s voyages, increased the number of plant species known to Western science by a quarter. today, most new animal discoveries are of reptiles, amphibians, and invertebrates, although a few new species of birds and mammals are occasionally found. a new species of deer was discovered recently in Vietnam. there are 30,000 okapis (relatives of giraffes) in the jungles of Zaire, but they were unknown to Western science until the 20th century. Riwoche horses in tibet were known only from cave drawings and were assumed to be extinct until some explorers who got lost found them in a remote valley in 1995. Whole new phyla of animals have been Dominance-diversity curves for plant species in two forests: The vertical found in recent decades in places axis is the percentage dominance by each species; if there were only one such as the deep ocean sediments. species present, it would have 100-percent dominance, whereas the horiMany of the 2,350 new flowering zontal axis is the species ranked from most (left) to least (right) common. plant species discovered each year The subalpine forest of the Great Smoky Mountains has few species. The are found in locations not easily most dominant species is very common, and each of the others is much accessible. more dominant than the next. This forest has low equitability. The deciduSecond, scientists can fi nd ous cove forest of the Great Smoky Mountains has a much higher number that new species have been hidof species. No species is strongly dominant, and most of them are almost equally rare. This forest has high equitability. ing in plain sight. Plant ecologists at Barro colorado island, a nature reserve in the Panama canal region, had Measurements of species richness, importance, walked past a certain tree many times before anyand equability can be very important for evaluating one thought to identify it—only to discover that it the impact of human activities on natural commuwas a species new to science. Scientists discovered nities. Disturbances, many of which are caused by a new tree species (Acacia fumosa) in ethiopia in human activity, can turn a species-rich, log-nor2006. a dominant plant in an area the size of crete, mal community into a species-poor, geometric one. it was not rare. Many previously undiscovered bacthese measurements of biodiversity can serve as a terial species live on and in the human body, and warning of an upcoming collapse of an ecological even more in the soil. community. When a researcher finds a species that may be in many cases, there is not enough time to calpreviously undiscovered, he or she must consult a culate diversity indices. Biologists are often fully defi nitive list of species that are known from the area. occupied simply identifying all the species in a given this is usually difficult because species identifications location. Biodiversity “hotspots” are defi ned simply are published in many different places, often obscure: in terms of species richness. Marine biodiversity is not well enough known that diversity indices can be ● new species are described in scientific artiapplied to it, and marine scientists are still largely cles published in journals. the journals, determining the species richness of oceanic regions.

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biodiversity, resources for agriculture 

●●

particularly older issues or journals that have ceased publication, may be very difficult to locate. Lists of all the species (for example, a flora is a compilation of all the plant species of a defined location) are usually organized into keys that allow identification. They may be equally difficult to locate.

Keeping track of even the known species is a difficult task. Sometimes, new species turn out to have been already described, although this occurs only about 20 percent of the time. Some scientists estimate that there may be 100 million species on Earth. At current rates, it would take biologists 14,000 years to catalog them. The modern answer to this difficulty is computer databases. The evolutionary biologist Edward O. Wilson said, “Imagine an electronic page for each species of organism on Earth .  .  .” The result was the Encyclopedia of Life. It is a database that may eventually include all species and to which people can submit information. Although it circumvents the ultimately necessary but slow process of scientific review, information is accepted only from people who have expertise in the relevant group of organisms. Each species has its own Web page. All the information (except genetic sequences) that someone may need in order to identify a specimen can be downloaded in the field and used on the spot. The Encyclopedia of Life or similar databases will not identify a specimen for a researcher, but just allow the researcher to tentatively confirm an identification already made or to confirm that the species has not been previously discovered. The online information is available by satellite in remote and little-explored regions. Similar online repositories of species information include the Catalogue of Life and, for North America, the Integrated Taxonomic Information System, although these databases focus mainly on the list of species names that are accepted by experts. Even with advanced databases, it may not be possible to recognize a new species. In some cases, populations of birds that had been considered a single species turn out to be more than one. According to the biological species concept, populations are of the same species if they can potentially interbreed in the wild. In some cases, birds of one population do not recognize the mating call of another and may therefore qualify as two different species. In some cases, species might be recognized only on the basis of DNA dissimilarity. Because of the difficulties just cited, there is not and probably never will be a definitive list of the species that live on Earth.

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57

See also communities, ecological; DNA studies of biodiversity; speciation. Further Reading Biodiversity Heritage Library. “BHLwiki.” Available online. URL: http://biodivlib.wikispaces.com/about. Accessed June 21, 2010. Encyclopedia of Life. “Encyclopedia of Life.” Available online. URL: http://www.eol.org. Accessed June 21, 2010. Ertter, Barbara. “Floristic surprises in North America north of Mexico.” Annals of the Missouri Botanical Garden 87 (2000): 81–109. Available online. URL: http:// ucjeps.berkeley.edu/floristic_surprises.html. Accessed June 22, 2010. Integrated Taxonomic Information System. “Integrated Taxonomic Information System.” Available online. URL: http://www.itis.gov. Accessed July 2, 2010. ———. “Species 2000.” Available online. URL: http:// www.catalogueoflife.org. Accessed July 2, 2010. Mabberley, David J. “Exploring terra incognita.” Science 324 (2009): 472. Rodrigues, Ana S. L., and Thomas M. Brooks. “Shortcuts for biodiversity conservation planning: The effectiveness of surrogates.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 713–737. Scholes, R. J., et al. “Toward a global biodiversity observing system.” Science 321 (2008): 104–105. Simons, Marlise. “A stone-age horse still roams a Tibetan plateau.” Available online. New York Times, November 12, 1995. URL: http://www.nytimes.com/1995/11/12/ world/a-stone-age-horse-still-roams-a-tibetan-plateau. html ?pagewanted=1. Accessed May 12, 2011. Whittaker, Robert H. Communities and Ecosystems, 2nd ed. New York: Macmillan, 1975.

biodiversity, resources for agriculture  Every species of organism plays an important, if not essential, role in local and global ecosystems. However, the diversity of species, and genetic diversity within species, has provided and will continue to provide direct and important benefits to human welfare and the world economy. These benefits are often the ones that most easily convince people that species—as many as possible—need to be rescued from extinction. This entry explains the essential role of wild species in maintaining agriculture. Other entries provide examples of wild species that have made dramatic differences in human health and of new ideas for inventions and processes that have come from the study of wild species.

Wild Plant Species for Food and Agriculture When humans lived as hunters and gatherers, which was the case for more than 90 percent of the time

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58 58 biodiversity, resources for agriculture  that Homo sapiens has existed, they ate a great diversity of foods, including wild seeds and fruits. The physiology of human bodies evolved a dependence on this diversity of food sources. For example, some mammals can synthesize ascorbic acid, a molecule that is necessary in the formation of certain tissues in their bodies, but the ancestors of modern humans lost this ability. This was not a problem, however, as ascorbic acid (also known as vitamin C) was abundant in the wild fruits that primitive humans ate. A diversity of plants has always been important in the human diet. Vitamin C deficiency became a problem after the advent of civilization as many of the poorest humans had to survive on a bland diet of grains. They suffered the symptoms of scurvy as a result. Fortunately, agriculture supplies humans not with just the basic staples, such as wheat, but with a large number of other foods, such as apples and oranges, that supply nutrients such as vitamin C that the staples cannot provide. Agriculture can meet the full range of human nutritional needs, not just the need for calories. The database of the United Nations Food and Agriculture Organization (FAO) lists 152 different major crops produced in the world. Even though only a dozen or so crops constitute the lion’s share of agricultural production, human health and economy would suffer substantially without the others. Human health continues to depend on plant diversity—the diversity of crop species. The new science of evolutionary medicine has revealed that human health may be best served by a diet that most closely resembles what primitive hunter-gatherers ate. In particular, disorders such as diabetes appear to be stimulated by a reliance on modern, processed foods. If everyone were to go back to a traditional, diverse diet, it would seem that 152 kinds of crops would provide sufficient variety without the need to gather wild foods or domesticate new kinds of crops. However, as the botanist Gary Paul Nabhan has explained, there is no single primitive diet to which all humans have adapted. He notes that certain genetic lineages of people, such as Native Americans, native Hawaiians, and native Australians, suffer the most from diseases such as diabetes when they depart from traditional cuisines and adopt modern culinary uniformity. He proposed that, during the course of the past few thousand years, cultural groups have biologically adapted to consuming local foods. The wild succulent plants consumed by desert peoples, he points out, not only have less of the quickly metabolized starches that contribute to diabetes, but also contain more of the molecules that help them resist diabetes. If a close coevolution has occurred between local peoples and their local crops and wild plants, then 152 kinds of

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first entry plant-based foods may not be enough for the optimal health of all humans. However, the story of diversity does not stop with plant species diversity. Humans need not only a great diversity of crop plant species, but also a great genetic diversity of breeds or varieties within each crop species. There are scores or hundreds of breeds of each species of crop plant. Plant breeders have traditionally produced new breeds of crop plants by cross-breeding existing varieties of crops to produce new combinations of characteristics. More recently, the techniques of biotechnology have allowed plant breeders to move the DNA from one breed of plant to another. Because the DNA of all species is chemically the same, biotechnologists can move genes from one species of plant to another or even insert a viral, bacterial, or animal gene into plant DNA. Thousands of acres are now devoted to crops that contain viral or bacterial genes. The importance of maintaining a diversity of crop breeds is not immediately apparent to most people. Although it is appealing to have different breeds of apples from which to choose, just how important is it? After all, these breeds do not differ greatly in their nutritional values to humans. The importance of having a great diversity of crop breeds is not so much for everyone’s pleasure in eating as it is for farmers’ success in growing them. It is necessary to preserve a great diversity of crop breeds because they each have adaptations to different climates and to different biological environments. Some breeds of wheat tolerate cold winters or droughts better than others, and some breeds of corn can complete their life cycle in a shorter period of time than others, which allows them to grow farther north, where the growing season is shorter. These are examples of adaptations to different climates. Adaptations to various biological environments, which consist of the other plants, the viruses, the fungi, and the insects that the crop encounters, are even more important. Some crop breeds are better than others at growing in the crowded conditions of modern agricultural fields. Some can resist viruses, fungi, or insect pests that others cannot. Plant breeders have to keep producing new breeds, because once an established breed has been grown for a long time, viruses or bacteria or fungi will evolve the ability to infect it. It is an evolutionary race between the natural evolution of the pests and the artificial evolution carried out by plant breeders. Breeders keep reshuffling the alleles of different crop varieties to produce new adaptations to changing climate and to new pests. Neither traditional plant breeders nor modern biotechnologists create new genetic variation—they

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biodiversity, resources for agriculture  just move it around. They have to obtain the alleles from existing populations of organisms, and if those organisms become extinct, the alleles they contain vanish and are no longer available for the production of new breeds of crops. Wild species have also proven to be good sources of natural pesticides. The Bt toxin, from the bacterium Bacillus thuringiensis, kills insects by disrupting the lining of their digestive tracts. Pyrethrin insecticides (now modified into the safer and more stable pyrethroids) were discovered in a species of chrysanthemum. Four compounds that prevent insects from feeding as well as their ability to reach maturity have been found in the leaves of the neem tree (Azadirachta indica). The bacterium Streptomyces avermitilis produces avermectins, which kill roaches and fire ants. A new group of antifungal compounds, the strobilurins, were discovered in Strobilurus tenacellus, a mushroom.

Three Threats to Plant Diversity in Agriculture There are three kinds of extinction that threaten the future of agriculture as well as the development of new commercial products: extinction of traditional varieties, extinction of wild relatives of existing crops, and extinction of wild species that may serve as future crops. Genetic extinction of traditional crop varieties. Traditional crop varieties are often called “heirloom” varieties. Around the world, subsistence farmers and gardeners have developed numerous breeds of crop that are well suited to their local conditions and the preferences of their cultures. They pass the seeds of these varieties from one generation to another. This is why the world contains hundreds of varieties of major crops such as wheat and minor ones such as chili peppers and eggplants. Nevertheless, often these heirloom varieties have inferior yields in comparison to the varieties sold by the large seed companies of Europe and North America. Subsistence farmers may, if they can afford to do so, choose to eat their old seeds rather than save them for planting the next year and buy the varieties that they perceive are superior. The old varieties and the benefit that they may offer to the future of plant breeding may be lost as a result. By consuming the last seeds of the old varieties, they are literally eating the future. Plant breeders do not want these traditional varieties of crops to become extinct, and some governments are trying to rescue them before they vanish. The U.S. Department of Agriculture (USDA), for example, has cold-temperature storage facilities for major crops, such as the one for potato varieties in Sturgeon Bay, Wisconsin. Such facilities are expensive, and they are used only to save the varieties of

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the crops that earn the most money for large-scale agriculture. Because cold-temperature storage in warm countries is expensive, five northern countries (led by Norway) established a seed vault in the arctic Svalbard Islands in 2006. The facility will eventually have 3 million seeds and store more varieties of more crops than any previous project. But these measures by themselves are not enough. Seeds will die after being stored for a few decades, so they must be planted and grown, to produce new seeds, which are then stored again. There is, however, a dark side to the Svalbard seed vault. Although the actual seeds in the vault are not available to them, large agricultural corporations have free access to the genetic varieties represented by those seeds. These corporations can use genetic engineering to modify the varieties and then patent them. This would give the corporations ownership over the crop varieties, and no one can then use these varieties without paying the corporations. Families, communities, and tribes have for millennia planted their traditional varieties of garden plants, passing the seeds down from one generation to the next. Since many of these varieties are threatened with extinction, nongovernmental organizations, such as Seed Savers Exchange, have rescued thousands of crop varieties from oblivion by storing and growing them. Such organizations have aspired to help tribes and communities, which freely donated their traditional and often sacred seeds, to keep their food plant genetic variation alive. Large corporations, however, may now be able to patent these very same varieties and charge farmers for the privilege of planting their own traditional seeds. Many conservationists consider this to be corporate profit based on a freely donated public resource and consider the Svalbard seed vault, however lofty its purpose may appear to be, to constitute corporate acquisition of genetic resources for which they have not paid. Seed Savers Exchange is one of the organizations that has agreed to these conditions, thus making them a conduit of traditional varieties from families, tribes, and communities to the control of large agricultural corporations. Often, people save varieties not just for their usefulness but for pleasure. In addition to the regular kind of basil with which most aficionados of Italian cuisine are familiar, there are many other varieties, which have flavors similar to everything from cinnamon to lemon. There is also a garden variety of “chocolate mint” whose raw leaves live up to their name. Diversity within major and minor crop species is important for both practical reasons and for sheer enjoyment. Genetic extinction of wild relatives of crop plants. Wild breeds or species of plants that can

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60 60 biodiversity, resources for agriculture  cross-breed with crop plants can provide even more genetic variety than the heirloom crop varieties. For example, there are at least 212 species of cultivated plants from the Tropics alone that have wild populations closely related to them. Chocolate, the health benefits of which are now being revealed, is Theobroma cacao. The genus Theobroma has 21 wild species that can be useful in producing new breeds of cocoa. There is at least one famous example of a wild species that rescued a cultivated one from danger. When phylloxera bug (Daktulosphaira vitifoliae) infestations threatened European grapevines (Vitis vinifera) and the wine industry in the late 19th century by infecting vines with a mildew, the botanist T. V. Munson found that wild grapes (Vitis rotundifolia) from Oklahoma and Texas could resist this insect. He shipped thousands of wild grape rootstocks to France, and French grapevines were grafted to these roots. This action is reputed to have saved the European wine industry. However, like the traditional garden varieties, the wild relatives of crops are vanishing, mostly because the natural habitats in which they live are being destroyed. The wild ancestors of wheat, for instance, persist in the hills of the Middle East, where war and land degradation endanger them. Some species of teosinte, the wild ancestor of maize, barely survive in the foothills of Mexico. In some cases, traditional garden varieties have avoided extinction by escaping into the wild. For example, wild coffee trees live in the forests of Ethiopia adjacent to the fields of cultivated coffee, but these forests, like most others, are shrinking under human influence. For a few crops, such as mangoes and papayas, the wild relatives thrive in disturbed areas and are therefore in no danger of extinction. Such examples, however, are in the minority, and for even these species, at least some of the wild relatives are threatened with oblivion. Extinction of possible new crops. There are many wild species of plants that offer the promise of future development as crops. Given that there are already so many kinds of crops (even more than the 152 major categories listed by the FAO), why would it be necessary to develop new ones? This is a good question, especially because the development of a new crop is a protracted and difficult process, but there are definite economic and ecological benefits to the development of new crops from wild species. Wild plants are not only important for individual survival in an emergency—the U.S. Army Survival Manual describes 74 of them—but for the future of agriculture. New crops may offer significant market possibilities if their taste or usefulness is unique. For example, most persimmons sold in the United States

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first entry are Japanese persimmons (Diospyros kaki), but the wild American persimmon (Diospyros virginiana) provides a fruit whose wonderful flavor differs not only from all others in the supermarket but from the Japanese species as well. Likewise, there is no other fruit with a flavor quite like that of the mulberry, Morus alba. A significant amount of work would be necessary to prepare these two wild species for orchard cultivation. The American persimmon fruit is small and full of large seeds, and mulberries typically lose their flavor if frozen. Wild fruits usually ripen over a prolonged period that would make simultaneous harvest impractical. Still, someday we may find that there is a market niche for them. Other wild plants, such as dandelions and violets and even (after cooking) nettles, are eminently edible and nutritious. Perhaps more important, new crops may offer significant ecological advantages. Some might, for example, be able to grow exceptionally well in degraded or dry soils otherwise unsuitable for agriculture. The spread of soil degradation through erosion and salinization creates an incentive to develop new crops that can live in degraded soil. There are three ecological circumstances for which new crops might offer a partial solution. ●●

New crops for saline soils. Around the world, irrigated land in warm, dry regions is the most productive. Irrigation, however, causes salt to build up in the soil. According to the United Nations Food and Agriculture Organization (FAO), of the more than 500 million acres (230 million hectares) of agricultural land that are irrigated, almost 20 percent have been salinized. Relatively few crop plants can grow in salty soil (beets and barley are among the few exceptions), and even these cannot tolerate very much salt. However, some wild plants can tolerate high levels of salt. Wildwheat (Distichlis palmeri), a wild grass native to the southwestern United States, produces an edible grain, and the oil-rich seeds of the pickleweed Salicornia can be added to animal feed. S. bigelovii can produce 0.8 tons per acre (2.0 metric tons per hectare) of seed. In contrast, the average sunflower oil crop produces only 60 percent as much. In theory, genetic engineering could be used to produce salt-tolerant crops, but salt tolerance turns out to be a complex set of traits that have not yet been successfully introduced into existing crops. If humans are to raise crops in salinized soil, finding wild plants may be the only option.

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biodiversity, resources for agriculture  ●●

●●

New crops for dry soils. Some wild plants that thrive under desert conditions might prove useful for agriculture in the future. The jojoba (Simmondsia chinensis), a bush from the North American southwestern desert, produces a liquid wax that can be useful in industrial processes because it is stable under high temperature and pressure. Many acres of jojoba have been raised in irrigated lands in the desert Southwest. Although the bush does not need irrigation, water supplementation boosts its growth and yields. Unfortunately, this bush became a victim of its own success. Irrigation raised the land values so much that jojoba plantations, which yield only a moderate profit, have been converted to lucrative subdivisions. Other arid land plants, however, grow well without irrigation. Prickly pear cactus (Opuntia ficus-indica) produces edible fruits (tuna in Spanish) and edible pads or stems (nopalitos in Spanish). Buffalo gourds (Cucurbita foetidissima) grow well on roadsides of the deserts and high plains. As its Latin name suggests, it is inedible. However, its massive root can yield starch for ethanol production. Its seeds can produce more oil than some cultivated oil crops, with no irrigation. New crops for polluted areas. Wild cattails can grow in water contaminated by sewage. The bacteria that grow around their stems and roots break down the sewage, and the cattail plants absorb the released nutrients. Arcata, California, uses cattail marshes for its municipal sewage treatment. The underground stems of the plants produce a great deal of starch, which can be harvested for the production of fuel ethanol.

Plant breeders can also produce new crops that cause less environmental degradation in the first place. Perhaps the best example of this is natural systems agriculture (NSA), which is the focus of research at the Land Institute in Salina, Kansas. NSA uses perennial crops rather than annual crops and therefore requires less energy and less fertilizer, as well as minimizing soil erosion. Only a few of today’s main agricultural crops, among them potatoes and alfalfa, are perennials. In order to promote an agriculture based on perennials, Land Institute scientists have to develop new crops, and to do so, they draw from the resources of wild plant species. For example, wild wheatgrass (Thinopyrum intermedium) is a perennial relative of wheat that could be used as a source of grains. Maximilian sunflower

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(Helianthus maximiliani) and rosinweed (Silphium integrifolium) are perennials that could be used as a source of oilseeds. Bundleflower (Desmanthus illinoensis) is a perennial legume that produces seeds similar to those of soybean, only smaller. The main work of plant breeders at the Land Institute is to cross wild perennial plants with annual crop species. This is a quicker and more promising route to the development of perennial replacements for annual crops than is the direct breeding of wild perennials. The researchers cross perennial wheatgrass with annual wheat, Maximilian sunflower with annual sunflower, and perennial Johnson grass (Sorghum halepense) with annual sorghum (S. bicolor). They then cross these hybrids with the annual parents (see figure on below), thus producing plants that more closely resemble the annual crops, except that they may be perennials.

Plant breeders at the Land Institute in Salina, Kansas, are cross-breeding domesticated annual sunflowers and wild perennial sunflowers, hoping to obtain a perennial breed of sunflower that has commercially valuable properties, such as high seed-oil content. The outer (ray) florets, which do not produce pollen, have been removed from each of the sunflowers. Breeding new crops is one of the economic benefits of wild plant species.  (Stanley A. Rice)

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62 62 biodiversity, resources for agriculture  They plant thousands of cross-bred specimens and then see which ones grow for more than a year. From among these survivors, they choose the plants with the best characteristics. The best characteristics are usually the same ones that the earliest farmers selected: breeds that have large seeds, do not shatter the mature seeds, have no seed dormancy, have a high harvest index, and do not collapse under the weight of their own seeds. If successful, perennial crops will allow farmers to produce grains, oilseeds, and legumes that have characteristics desirable to humans, that minimize soil erosion, and that promote fertility of the soil and its ability to hold water. Saving old crops can be as useful as finding new ones. Native Americans of Mexico and South America grew large amounts of amaranth and quinoa, the seeds of which can be used as grains even though they are not grasses. The conquistadores tried to stamp out the cultivation of these crops, ostensibly because of their association with paganism. Fortunately, they were not entirely successful. Although they are not major crops, amaranth and quinoa are still grown and eaten in the places where they once flourished and available for purchase in some American supermarkets. Many of the traditional grains of Africa, such as an African species of rice, finger and pearl millets, fonio, sorghum, and tef, are still grown in rural areas.

Plant and Animal Diversity Down on the Farm The importance of plant diversity is perhaps most obvious not in what is grown on farms but in the way it is grown. Modern agriculture is overwhelmingly based on monoculture, in which farmers plant large expanses of just a single breed of a single species of crop plant. Monoculture invites many kinds of problems. For example, pests and diseases can spread rapidly through a monoculture of crops because their preferred food plant is always just a few inches away. If a whole field consists of one species or even one variety of crop, all of them are competing for the same nutrients in the same soil level and the same sunlight at the same height above the ground. Despite these problems, farmers in industrialized nations usually grow their crops in monocultures, because a huge, genetically uniform field is easier to manage by means of machinery and chemicals. If a field contains nothing but corn and all the ears of corn are exactly the same height above the ground, a mechanical harvester can get all of the corn by just driving back and forth across the field. One of the worst examples of monoculture is the modern banana. Thousands of square miles of land in Latin America are a monoculture of just

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first entry one kind of banana: the Cavendish. Because domesticated bananas do not produce seeds, they must be propagated by cuttings, all of which are genetically identical. A genetically uniform monoculture is an invitation for the spread of disease. This is precisely what has happened: Panama disease, caused by a fungus, Fusarium oxysporum, has devastated banana plantations in Southeast Asia, and it is only a matter of time before it spreads to Latin America. Fruit companies first marketed the Cavendish banana because the previously popular variety, the Gros Michel, had been devastated by a different strain of Panama disease. Planting more than one kind of crop in the same field, a practice called polyculture, can greatly reduce these problems. Because each of the crop species is at a lower density in a polyculture than it would be in a monoculture, pests spread much more slowly through fields that consist of more than one crop species. Some tomato fields in California are interrupted with rows of sunflowers. The sunflowers can impede the movement of sphinx moths through tomato fields, causing them to lay fewer eggs, which hatch into voracious tomato hornworms. Even planting different breeds of the same crop together in a large field can confer some polyculture benefits. Interplanting disease-resistant with disease-susceptible crops can help protect the susceptible ones. Planting rice varieties that grow to different heights together in the same field creates pockets of temperature variation that reduce the spread of fungus disease. Polyculture is an essential component of natural systems agriculture. By using perennial plants in polyculture, NSA is following the lead of the geneticist Wes Jackson, founder of the Land Institute, who takes the tallgrass prairie as his inspiration and model. A mixture of perennial species has made the prairie a successful natural habitat; the same system should work for agricultural lands. His vision is to make agriculture incorporate natural processes that have been perfected by millions of years of evolution. If the crops in the mixture are of different sizes, they might be able to use the sunlight and the different soil depths more efficiently than could a monoculture. The gardens of tribal peoples almost always contained mixtures of species growing side by side. Native American gardens were centered on the “three sisters”—maize, beans, and squash (see figure on page 63). The beans and squash grew near the ground and used the tall corn as a trellis. Other examples include growing rows of papaya trees in pineapple fields in the Philippines and growing orange trees beneath date palms in southeastern California. The papaya trees do not shade the

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up, only to die the next year when a different kind of crop is planted. A leguminous crop one year can enrich the soil with nitrogen that the next year’s crop can use. Crop rotation can be considered a temporal polyculture that alternates in time rather than in space. Farmers have known about crop rotation for many centuries, though they did not understand how it worked. The Roman poet Virgil wrote about legume-grain crop rotation: Sow in the golden grain where previously You raised a crop of beans that gaily shook Within their pods, or a tiny brood of vetch . . . Thus will the land find rest in its change of crop, And earth left unploughed show you gratitude.

Native American agriculture (for example, as at New Echota, a reconstructed Cherokee town in Georgia) used polycultures, in which several crop species grow together. Polyculture reduces the density and therefore the pest load of each crop species. Hollow gourds allow swallows, which eat insect pests, a place to nest.  (Stanley A. Rice)

pineapples nor do the date palms shade the oranges enough to impede their growth. In fact, some crops such as coffee bushes grow better in moderate shade. Another way in which polyculture can enhance the efficiency of agricultural production is that a farmer can benefit from raising more than one product. Although this may not particularly matter in the market economies of industrialized countries, it can be very important in rural areas of the developing world. For example, farmers who plant the fastgrowing tropical tree leucaena (Leucaena leucocephala) along with their primary crop can harvest the crop as well as the leucaena. Because the trees are leguminous, they have nitrogen-fixing bacteria in their roots. This allows their pods and leaves to be nutritious food for livestock and even means that they can enrich the soil with nitrogen fertilizer. In addition, the trees can help prevent soil erosion. In crop rotation, a farmer plants different crops in a field each year. Pests of the first crop may build

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There is no reason that polyculture cannot be integrated into modern mechanized agriculture. Instead of having a square mile of corn and another square mile of soybeans, a farmer can plant alternating swaths of corn and soybeans that are still wide enough to allow farm equipment to maneuver. Such fields used to be a rare sight but are increasingly common in the midwestern United States. Is it possible that all the wild plants that could be domesticated have already been brought under cultivation? This is probably not the case. Once agriculture evolved, it was easier for farmers who moved to new locations to bring crops with them than to develop crops from wild plants in the new location. The success of the early crop plants therefore preempted the development of equally promising or even superior new crop plants. The great diversity of wild plant species therefore still represents a cornucopia of possible new resources for agriculture. There is a parallel decline in the diversity of livestock breeds. In the last 150 years, 190 breeds of livestock have become extinct, 60 of them in just the last five years. While the remaining breeds are very productive, the extinction of “inferior” breeds has reduced the ability to breed for disease resistance, just as is the case with crops. Holsteins are 90 percent of dairy cattle, and leghorn chickens produce almost all eggs. See also biodiversity, resources for medicine; biomimicry; Jackson, Wes; natural systems agriculture. Further Reading Chivian, Eric, and Aaron Bernstein, eds. Sustaining Life: How Human Health Depends on Biodiversity. New York: Oxford University Press, 2008. Collins, W. W., and C. O. Quaslet, eds. Biodiversity in Agroecosystems. New York: Lewis, 1998. Cox, T. S., et al. “Breeding perennial grain crops.” Critical Reviews in Plant Sciences 21 (2002): 59–91.

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64 64 biodiversity, resources for medicine  Donia, Mohamed S., et al. “A global assembly line for cyanobactins.” Nature Chemical Biology 4 (2008): 341–343. Elias, Thomas, and Peter Dykeman. Edible Wild Plants: A North American Field Guide. New York: Sterling, 1990. Farnham, Timothy J. Saving Nature’s Legacy: Origins of the Idea of Biological Diversity. New Haven, Conn.: Yale University Press, 2007. Fischbach, Michael A., and Christopher T. Walsh. “Antibiotics for emerging pathogens.” Science 325 (2009): 1,089–1,093. Glover, Jerry D., Cindy M. Cox, and John P. Reganold. “Future farming: A return to roots?” Scientific American, August 2007, 82–89. Hinman, C. Wiley, and Jack W. Hinman. The Plight and Promise of Arid Land Agriculture. New York: Columbia University Press, 1992. Jackson, Wes. New Roots for Agriculture. Lincoln, Neb.: University of Nebraska Press, 1980. Kalka, Margareta B., et al. “Bats limit arthropods and herbivory in a tropical forest.” Science 320 (2008): 71. Koeppel, Dan. Banana: The Fate of the Fruit That Changed the World. New York: Hudson Street Press, 2007. Maxwell, Nicole. Witch-Doctor’s Apprentice: Hunting for Medicinal Plants in the Amazon. New York: Citadel, 1961. Nabhan, Gary Paul. Why Some Like It Hot: Food, Genes, and Cultural Diversity. Washington, D.C.: Island Press, 2004. National Research Council, Board on Science and Technology for International Development. Lost Crops of Africa. Vol. 1: Grains. Washington, D.C.: National Academy Press, 1996. Partida-Martinez, Laila P., and Christian Hertweck. “Pathogenic fungus harbours endosymbiotic bacteria for toxin production.” Nature 437 (2005): 884–888. Piel, Jörn. “Metabolites from endosymbiotic bacteria.” Natural Product Reports 26 (2009): 338–362. Plotkin, Mark. Tales of a Shaman’s Apprentice: An Ethnobotanist Searches for New Medicines in the Amazon Rain Forest. New York: Viking, 1993. Rice, Stanley A. Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Rosenthal, Elizabeth. “Near Arctic, seed vault is a Fort Knox of food.” Available online. New York Times, February 29, 2008. URL: http://www.nytimes.com/2008/02/29/ world/europe/29seeds.html?ei=5124&en=006cb7 68718869ca&ex=1362027600&exprod=permalink &pagewanted=print. Accessed May 12, 2011. Rozema, Jelte, and Timothy Flowers. “Crops for a salinized world.” Science 322 (2008): 1,478–1,481. Schiebinger, Londa. Plants and Empire: Colonial Bioprospecting in the Atlantic World. Cambridge, Mass.: Harvard University Press, 2004.

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first entry Smith, Nigel J. H., et al. Tropical Forests and Their Crops. Ithaca, N.Y.: Cornell University Press, 1992. Southern Exposure Seed Exchange. “Southern Exposure Seed Exchange.” Available online. URL: http://www. southernexposure.com. Accessed July 2, 2010. United Nations Food and Agriculture Organization. “Biodiversity for a World Without Hunger.” Available online. URL: http://www.fao.org/biodiversity/en/. Accessed August 8, 2011. Williams-Guillén, Kimberly, Ivette Perfecto, and John Vandermeer. “Bats limit insects in a neotropical agroforestry system.” Science 320 (2008): 70. Wilson, Edward O. The Future of Life. New York: Vintage, 2003. Wolfe, M. S. “Crop strength through diversity.” Nature 405 (2000): 681–682. Zhu, Y. Y., et al. “Genetic diversity and disease control in rice.” Nature 406 (2000): 18–722.

biodiversity, resources for medicine  The diversity of species and genetic diversity within species has provided and will continue to provide direct and important benefits to human welfare and the world economy. These benefits are often the ones that most easily convince people that species—as many as possible—need to be rescued from extinction. Biodiversity has been and will continue to be crucial to the improvement of human health in two general ways. First, many wild species produce molecules that have medicinal value to humans. Second, some wild species have provided valuable insights in medical research. Other entries in this encyclopedia are devoted to the importance of biodiversity to agriculture and to technological progress. Wild Species as Sources of Medicinal Compounds Humans already owe a tremendous debt of gratitude to wild species, which have provided nearly all medicinal compounds. New compounds continue to be found. Nearly always, the medicinal compound is discovered in a species that seemed to have little importance to human activities and whose extinction would not have been noticed by many people. The following is an overview of examples. Medicinal compounds from microorganisms. The most famous medicinal compounds are those produced by fungi and bacteria (see table on page 65). They produce antibiotic compounds that are, in effect, chemical warfare against other microorganisms with which they compete for food supplies. Sometimes the compounds serve other functions, such as signaling between microbial cells. Because of their short generation times, microbes can evolve

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Some Wild Microbes, Plants, and Animals in Which Pharmaceutical Compounds Have Been Discovered Source

Active Compound

Medical Use

Amycolatopsis orientalis

vancomycin

glycopeptide antibiotic

Aspergillus terreus

lovasatin

cholesterol control

Cephalosporium acremonium

cephalosporin

beta-lactam antibiotic

Penicillium fungus

penicillin

beta-lactam antibiotic

Penicillium citrinum

mevastatin

cholesterol control

Streptomyces griseus

streptomycin

aminoglycoside antibiotic

Streptococcus aureofaciens

tetracycline

tetracycline antibiotic

Streptomyces hygroscopicus

rapamycin

immunosuppressive, anticancer

Streptomyces avermitilis

avermectin

kills intestinal worms

Tolypocladium inflatum

cyclosporine

immunosuppressive

Artemisia annua

artemisinin

malaria

Catharantheus roseus

vincristine

childhood leukemia

vinblastine

Hodgkin’s disease

quinine

malaria

Microorganisms

Plants

Cinchona officinalis

boosts immune system*

Echinacea angustifolia Ginkgo biloba

ginkgolides

antidepressant*

Hypericum perforatum Pilocarpus jaborandi

prevents damage to hippocampus*

pilocarpine

glaucoma

Prunus africana

prostate cancer

Serenoa repens

reduces prostate enlargement*

Tabebuia avellanedae

beta-lapachone

tumors

Taxus brevifolia

taxol

ovarian cancer arthritis

Uncaria tomentosa

Animals Bothrops jararaca snake

teprotide

blood pressure reducer

Bugula neritina bryozoan

bryostatin

cholesterol reduction

Conus mollusks

toxic peptides

pain relief

Cryptotethya crypta sponge

spongouridine

helped in development of AZT

Diazona sea squirt

diazonamides

anticancer

Discodermia dissoluta sponge

discodermolide

prevention of cancer mitosis

Ecteinascidia sea squirt

trabectedin

inhibition of cancer DNA repair

Hirudo medicinalis leech

hirudin

anticoagulant

Luffarriella viariabilis sponge

anti-inflammatory

Pseudopterogorgia coral

pseudopterosin

anti-inflammatory

Sharks

squalamine

antitumor*

*Medicines of unproven efficacy

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66 66 biodiversity, resources for medicine  quickly, and pathogenic bacteria can evolve resistance against antibiotics within a very short period. There are scores of antibiotics, but for each of them, there is a population of bacteria somewhere in the world that is resistant to it. A random sample of soil microbes contains bacteria that can resist antibiotics. Bacteria can exchange DNA, even between species, with the result that antibiotic resistance can spread from one species of bacterium to another within a habitat, such as a human body. Some fungi produce compounds that have anticancer and antiviral effects. The fungus Tolypocladium inflatum produces cyclosporine, a compound that happens to suppress the human immune system and is therefore extremely valuable in controlling the rejection of transplanted organs. Many microbial compounds are produced by species that are not known except from the analysis of their DNA. Medicinal compounds from plants. Wild plants have been and will continue to be important sources of medicines (see table on page 65). The leaves of wild plants produce toxins that deter fungi and herbivorous animals from damaging them. Many of these toxins, when used in small quantities, have medicinal effects on humans. Indeed, most medicines began as natural plant extracts. For example, aspirin, though today synthesized artificially as acetylsalicylic acid, was once extracted from willow bark and received its name because it was first discovered in a wild spiraea bush (Spiraea ulmaria). The plants of the tropical forest are an especially rich source of medicines because their leaves must be very toxic to protect themselves from year-round attack by insects and other animals. Wild plant communities, particularly tropical forests, are rich laboratories for the production of medicinal compounds, as millions of plants in thousands of species produce new genetic variations of chemicals. Pharmaceutical research corporations often base their research on plant extracts. Because each kind of plant has a unique combination of protective chemicals, we need to save all of them. The extinction of any wild plant species might mean the loss of a yet-undiscovered medicinal compound. Moreover, these compounds are not randomly produced molecules but molecules whose biological potency has been confirmed by natural selection: The plants that produce them have resisted the attacks of organisms. Medicinal compounds from animals. Many animals also produce compounds that have proven to be of medicinal value. Some amphibians, for example, have poisonous skin. The poison has its effect by relaxing the muscles or reducing the heart rate of the predator. In small quantities, such a compound can be used as a muscle relaxant. Recently, sponges have been found to produce medicinal compounds.

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first entry Sponges live in close mutualism with bacteria, and these compounds may help them prevent the bacteria from growing and killing them. The anticoagulant lepirudin was originally known from leeches, which also produce a related compound, hirudin. Lepirudin is now produced commercially, but the leeches themselves are still sometimes used in medical treatments, for example, to drain fluid from reattached body parts while the veins are still growing back. Cone snails (genus Conus) have up to 140,000 different toxic peptides. Some of these molecules may function as pain relievers and anticonvulsants by blocking membrane channels. Each kind of peptide blocks a specific kind of channel. Squalamine from sharks, after initial hopes that it would function as an effective antibiotic, may instead be developed into an antitumor drug and an appetite suppressant that does not lower metabolism, as most appetite suppressants do. There is no way to predict, beforehand, which wild species might be “worth saving” for medicine or for some other useful product or to what use they might be put. Who would ever have guessed that a compound that could suppress the human immune system and control the growth of tumors would be found in a soil bacterium from Easter Island? Even so, that is where rapamycin came from (named after Rapa Nui, the Polynesian name of the island). Who could ever have guessed that certain forms of leukemia could be treated with vincristine and vinblastine found in the leaves of Catharanthus roseus, the rosy periwinkle, a small pink wildflower that lives in the vanishing rain forests of Madagascar (see figure on page 67)? Or that prostate cancer could be treated with a compound from the African cherry (Prunus africana)? Or that ovarian cancer could be treated by taxol from the bark of the Pacific yew, Taxus brevifolia? Who would have guessed that the bile of bears contained ursodeoxycholic acid, which may be useful in treating gall bladder conditions in humans? Who would have expected to find a new kind of glue in a frog? The frog Notaden bennetti lies dormant in desert mud for nine months each year encased in a kind of glue that is strong and yet, unlike other strong adhesives, allows molecules to diffuse through it, which is how they breathe. One promising way of seeking natural pharmaceuticals is to listen to the lore of tribal peoples who have had millennia of experience with medicinal plants. They can, at least, point the way toward finding plant species that have potent properties worthy of investigation. They can also indicate which species of frogs have poison skin, which the native people use for hunting darts. Ethnobotanists are scientists who visit tribal peoples and ask them about their native traditions concerning medicinal plants.

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biodiversity, resources for medicine 

The rosy periwinkle (Catharanthus roseus) is a wildflower that lives in Madagascar. The leaves of this plant just happened to contain compounds, such as vincristine and vinblastine, that help control leukemia.  (Wikimedia)

Occasionally, naturally occurring compounds may reveal new modes of therapy. Epibatidine, an alkaloid from the Ecuadorean frog Epipedobates tricolor, is a painkiller 200 times as potent as morphine, and the human body does not build up tolerance to it as it does to morphine. Not just new antimicrobials but new chemical families of antimicrobials have been discovered in amphibian skins. This is not unexpected, since amphibians have soft skin that is vulnerable to infection. Amphibian antimicrobials include some that are useful against the fungi that infect AIDS victims and against mycoplasmas, which are bacteria that are difficult to control. The sponge Cryptotethya crypta produces compounds such as spongouridine, which at the time of its discovery was a mere curiosity. The compound used the sugar arabinose in its nucleotides instead of the usual ribose (of RNA) or deoxyribose (of DNA). This discovery eventually allowed the development of therapies that used alternative nucleotides to inhibit the growth of retroviruses, such as HIV. The Atlantic horseshoe crab (Limulus polyphemus) has blue blood, which contains antimicrobial and antiviral compounds. Lysates from horseshoe crabs are used as extremely sensitive detectors of the presence of gram-negative bacterial toxins. It may turn out that hibernating bears have something to teach medical researchers. (Bears do not actually hibernate; their winter sleep is more properly called denning.) They are inactive for five months, yet they do not suffer bone loss during that time. They do not urinate during that time; their bodies recycle urea into amino acids. They do not develop diabetes, even though they have high blood levels of fat and sugar and low levels of insulin. Solv-

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ing the mysteries of how they do this may lead to major medical breakthroughs for humans. The medicinal compounds are sometimes the result of an ecological relationship between species. Wild dendrobatid frogs make medicinally useful alkaloids in their skins, but they do not do so in captivity. The toxin may actually come from insects that they eat. Sometimes frogs will make the chemicals in their food more toxic by concentrating it. An anticancer compound that was found in a marine mollusk turned out to have been produced by seaweeds eaten by the mollusks—or perhaps even by symbiotic bacteria associated with the seaweeds. Gathering wild plants, especially rare ones, for pharmaceutical extraction can easily deplete wild populations. Three responses to this problem are possible. ●●

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First, researchers may grow the wild plants in plantations or greenhouses, which is now being done on a small scale for the rosy periwinkle, for Pilocarpus jaborandi (source of pilocarpine, a medicine that reduces glaucoma pressure), for Artemisia annua (source of the antimalarial drug artemisinin), and for the African cherry. Second, researchers may find a close relative of a plant that is not rare and that may contain the same or a related active compound (a European yew now substitutes for the Pacific yew as a source of taxol). Third, researchers may artificially synthesize an active compound. Artificial synthesis is now the main source of vincristine and vinblastine. Salicylic acid, found in many wild plants, is modified into acetylsalicylic acid as the basis for aspirin.

The same problem arises with animals that produce pharmaceutical compounds. The soft coral Pseudopterogorgia elisabethae (or a symbiont that lives inside it) produces an anti-inflammatory compound. With careful management, this coral can rapidly regrow after harvesting to produce a sustainable source of this compound. The search for medically potent natural compounds is particularly important for the discovery of new antibiotics. According to the medical biologists Michael Fischbach and Christopher Walsh, most new antibiotics developed between about 1962 and 2000 have been modifications of old classes of antibiotics (penicillins, cephalosporins, quinolones, macrolids, and tetracyclines). Bacterial populations evolved resistance to older penicillins but were not resistant to modified penicillins. However, the bacteria quickly evolve resistance to the new ones because

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68 68 biodiversity, resources for medicine  they are structurally similar to the old ones. The authors call for the development of whole new chemical categories of antibiotics, something that was not done during the “innovation gap” of 1962 to 2000. One of the ways that the authors suggested as a source of whole new categories of antibiotics was previously unexplored artificial and natural products, including products that may appear to have a function unrelated to killing bacteria. They mention examples such as: ●● ●●

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The first sulfa drug, Prontosil, was originally developed as a dye by Bayer. The first quinolone was nalidixic acid, an intermediate in the production of chloroquine (synthetic quinine). The antibacterial action of oxazolidinones was discovered by DuPont, but they were originally developed to treat plant diseases.

For a while, the development of new antibiotics from natural sources seemed to be an outmoded approach. As the entire genomes of bacteria were deciphered, researchers believed they could use this information to identify proteins that the bacteria needed to survive and design compounds that would block them. However, noted Fischbach and Walsh, this approach has not yet yielded any new antibiotics. Furthermore, most existing antibiotics are broad-spectrum, that is, they kill many kinds of bacteria. This would appear to be a good thing, since the physician may not know what kind of bacterium is causing an infection, but broad-spectrum antibiotics kill so many kinds of bacteria that they can leave a patient open to opportunistic infections by otherwise harmless bacteria. This is the most frequent cause of Clostridium dificile infections. It appears that the door remains wide open to the discovery of new antibiotics, including narrow-spectrum antibiotics, from wild organisms—even (as in the oxazolidinone example) from plants. Some medicinally useful compounds have been found in organisms just before they were about to become extinct. Epibatidine is a relaxant that has fewer side effects than opiates. Scientists discovered it in the skins of a species of poison frog in Ecuador. This species survived in only one forest; the surrounding forests had all been made into banana plantations. Calanolide A is a powerful inhibitor of reverse transcriptase, an enzyme unique to retroviruses such as HIV and therefore a promising anti-AIDS drug. It is known only from one variety of Calophyllum lanigerum (var. austrocoriaceum); other subspecies are not known to produce the compound. The last wild member of this subspecies was cut down in Borneo before researchers could return

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first entry to it. Luckily, living specimens were alive in a tropical botanical garden. Meanwhile, as tribal peoples are incorporated into modern civilization, they begin to depend more and more on the products of modern agriculture and industry. Tribal children in rural areas can identify hundreds of wild plants and know what they are useful for; tribal children in urban areas, like most children in highly industrial countries, know very few plants. Tribal knowledge is vanishing much more rapidly than are tribes themselves.

Wild Species that Yield Medical Insights Adaptations of wild species have proven to be valuable in medical research aside from their production of medicinal compounds. Many have done so by serving as experimental organisms. The use of laboratory nematodes, fruit flies, mice, rats, and primates has proven indispensible in medical research to benefit humans. Mice and rats are mammals that have most of the same physiological responses to pharmaceutical compounds that humans do and have been inbred to produce genetic uniformity. Scientists can also produce “knockout mice” in which one version of a gene can knock out another version of the same gene to allow the physiological effects of just that one gene to be studied. Nematodes (Caenorhabditis elegans) and fruit flies (Drosophila melanogaster) are much simpler than mammals, but they have many of the same physiological processes. For example, humans have a much more complex nervous system than do fruit flies, but the nerve cells are largely the same. There are mutants of Drosophila that correspond closely to human mutations that contribute to problems with circadian rhythms, aggression, addiction, premature aging (Werner syndrome), Parkinson’s disease, Alzheimer’s disease, and Huntington’s disease, to name a few. The genetic basis of these diseases can be studied more easily in fruit flies (which are simple, have rapid generation times, and present no ethical problems for experimentation) than in humans. Some politicians do not realize this. In 2009, the former Alaska governor and vice presidential candidate Sarah Palin made a statement in which she ridiculed the use of government funds for fruit fly research (“I kid you not,” she said). Who can say what new experimental species may be in the wild, its usefulness not yet discovered? One example of an animal that might prove useful in experimentation is the gastric brooding frogs (Rheobatrachus silus and R. vitellinus). The tadpoles of this species develop while they are protected inside the stomachs of the parents and emerge as small adult frogs. In order to do this, the parents must keep from digesting the offspring, which means that the produc-

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biogeochemical cycles  tion of pepsin and acid is blocked while the young are brooding. If scientists discover how the frogs do this, they may be able to develop better treatments for some stomach diseases in humans. These frogs were unknown until the 1980s because they are rare and, therefore, in danger of extinction. Hagfishes and lampreys are useful in the study of the vertebrate immune system, since they are the only vertebrates that have only innate immunity. The ability of nerve cells to regenerate (neurogenesis) was discovered in chickadees (Parus atricapillus) when scientists studied the enlargement of their brains that occurred when the breeding season began and the birds began to sing. Biotechnology research has been revolutionized by the discovery of useful genes in wild species. The GFP (green fluorescent protein) gene, linked to another gene, produces a pigment whenever the gene to which it is linked is activated. A researcher can determine which tissues have the activated gene by shining ultraviolet light on the organism and looking for a green glow. This gene was found in the sponge Aequorea victoria. Biotechnology has been revolutionized by the use of a special kind of DNA polymerase that can resist high temperatures. This Taq polymerase was first discovered in Thermus aquatilis, a bacterium that lives in hot springs. Most of the newly discovered wild species that produce medicinal compounds live in tropical rain forests. Many tropical countries are poor. The United Nations Convention on Biological Diversity recognizes the economic interest these countries have in the development of medicinal compounds from the plants within their borders. Pharmaceutical prospectors and the companies for which they work now operate within strict guidelines that guarantee profit-sharing with the country in which the compound was discovered and the native peoples who called attention to it. See also biodiversity, resources for agriculture; biomimicry; resistance, evolution of.

Engel, S., et al. “Antimicrobial activities of extracts from Atlantic marine plants against marine pathogens and saprophytes.” Marine Biology 49 (2006): 991–1,002. Fenical, W., et al. “New anticancer drugs from cultured and collected marine organisms.” Pharmaceutical Biology 41 (2003): 6–14. Fischbach, Michael A., and Christopher T. Walsh. “Antibiotics for emerging pathogens.” Science 325 (2009): 1,089–1,093. Maxwell, Nicole. Witch-Doctor’s Apprentice: Hunting for Medicinal Plants in the Amazon. New York: Citadel, 1961. Moore, K. S., et al. “Squalamine—an aminosterol antibiotic from the shark.” Proceedings of the National Academy of Sciences USA 90 (1993): 1,354–1,358. Partida-Martinez, Laila P., and Christian Hertweck. “Pathogenic fungus harbours endosymbiotic bacteria for toxin production.” Nature 437 (2005): 884–888. Piel, Jörn. “Bacterial symbionts: Prospects for the sustainable production of invertebrate-derived pharmaceuticals.” Current Medicinal Chemistry 13 (2006): 39–50. ———. “Metabolites from endosymbiotic bacteria.” Natural Product Reports 26 (2009): 338–362. Plotkin, Mark. Tales of a Shaman’s Apprentice: An Ethnobotanist Searches for New Medicines in the Amazon Rain Forest. New York: Viking, 1993. Saporito, R. A., et al. “Formicine ants: An arthropod source for the pumiliotoxin alkaloids of dendrobatid poison frogs.” Proceedings of the National Academy of Sciences USA 101 (2004): 8,045–8,050. Schaeffer, D. J., and V. S. Krylov. “Anti-HIV activity of extracts and compounds from algae and cyanobacteria.” Ecotoxicology and Environmental Safety 45 (2000): 208–227. Stewart, K. M. “The African cherry (Prunus africana): Can lessons be learned from an overexploited medicinal tree?” Journal of Ethnopharmacology 89 (2003): 3–13. Wilson, E. O. The Future of Life. New York: Vintage, 2003.

Further Reading

biogeochemical cycles  Atoms and mol-

Chivian, Eric, and Aaron Bernstein. Sustaining Life: How Human Health Depends on Biodiversity. New York: Oxford University Press, 2008. Cragg, G. M., and D. J. Newman. “Biodiversity: A continuing source of novel drug leads.” Pure and Applied Chemistry 77 (2005): 7–24. Donia, Mohamed S., et al. “A global assembly line for cyanobactins.” Nature Chemical Biology 4 (2008): 341–343. Dumbacher, J. P., et al. “Melyrid beetles (Choresine): A putative source for the batrachotoxin alkaloids found in poison-dart frogs and toxic passerine birds.” Proceedings of the National Academy of Sciences USA 101 (2004): 15,857–15,860.

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ecules circulate endlessly through the ecosystems of Earth. These cycles are called biogeochemical because the driving forces are biological processes such as photosynthesis (and, ultimately, evolution), geological processes such as erosion (and, ultimately, continental drift), and chemical processes such as oxidation. The entire concept of biogeochemical cycles is based on the insight that organisms live and populations evolve not as actors on an environmental stage but as participants in the “nonliving” Earth itself. Organisms have altered Earth into a form very different from what it would have been if life had not evolved or had evolved differently. For example, nearly all the oxygen gas in the atmosphere has come

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70 70 biogeochemical cycles  from photosynthesis, and many carbonate deposits are biological in origin. For this reason, some scientists prefer to view Earth as a single living entity, figuratively referred to as Gaia, rather than as living and nonliving components. Some of these cycles are complex enough that they have their own entries in this encyclopedia: ●●

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Water molecules change state but remain intact as they circulate through the hydrological cycle. Water evaporates, primarily from the oceans, condenses in clouds, and precipitates onto land and ocean. A small amount of the water remains on land in lakes and aquifers. Organisms, primarily plants, play a crucial role in preventing runoff of water from snow and rain, allowing water to percolate into aquifers, and also release much water vapor back into the air during transpiration. Carbon atoms in atmospheric carbon dioxide gas enter the food web by photosynthesis, then return to the atmosphere by respiration and decomposition, mostly over the course of tens to hundreds of years. Organisms use carbon atoms to build virtually all their molecules. Carbon atoms also enter and are removed from rocks by chemical reactions, mostly over the course of thousands of years (see figure on page 71). Carbon dioxide in the atmosphere is an important cause of the greenhouse effect. Oxygen atoms circulate through ecosystems in two ways. Some remain associated with carbon atoms throughout the carbon cycle. Others enter the atmosphere as oxygen molecules when photosynthesis splits water molecules and return to the atmosphere when respiration puts those oxygen atoms back into water molecules. Oxygen also reacts with minerals in rocks. Nitrogen atoms in the form of largely inert nitrogen gas in the atmosphere are made into compounds such as ammonia by some bacteria. The ammonia and other molecules derived from it remain in the soil until plant roots remove them, and the nitrogen atoms enter the food web. Organisms use nitrogen atoms primarily in their proteins and nucleic acids. Some bacteria release nitrogen gas back into the atmosphere from decomposing organic material (see figure on page 71).

Sulfur atoms also participate in biogeochemical cycles with both soil and atmospheric components.

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first entry Plant roots absorb sulfate ions (SO42-) from the soil, and from there the sulfur atoms pass through the food chain, primarily as a component of proteins. Decomposers release sulfate back into the soil. Under anaerobic conditions, decomposers may produce hydrogen sulfide gas (H 2S) instead, which enters the atmosphere. Hydrogen sulfide reacts with oxygen to form sulfate, which returns to the ground as sulfuric acid dissolved in rain. All the previously mentioned cycles have both gaseous and atmospheric components. In contrast, most minerals cycle through ecosystems in solid or dissolved form (see figure on page 71). Plant roots absorb minerals that are dissolved in soil water. Plant cells use these minerals, which then travel through the food web, where they are used in animal cells and released back into the soil by decomposers. This is a short-term mineral cycle, in which a mineral atom or molecule may complete the cycle in as short a time as a few weeks. Most of the minerals that function in organisms circulate in short-term cycles. The most common of these minerals are as follows: ●●

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Potassium (K+) ions function primarily in the salt balance of cells, which do not synthesize them into larger molecules. Calcium (Ca2+) ions function primarily in assisting the operation of enzymes and are major components of bones (calcium phosphate), shells (usually calcium carbonate), and plant cell walls. Phosphorus atoms are usually found in phosphate ions such as HPO42- in the soil. Organisms use phosphorus as a component of nucleic acids as well as in the calcium phosphate of bones. Magnesium (Mg 2+) ions are found in the center of every chlorophyll molecule. Iron atoms primarily exist as ferrous (Fe2+) and ferric (Fe3+) ions in the soil. Every hemoglobin molecule contains an iron atom in its center, as do proteins that conduct electrons in photosynthesis and respiration.

Minerals may also undergo a long-term mineral cycle, in which a mineral atom or molecule may accumulate in sediment at the bottom of a shallow sea. The sediment is transformed into rock, which, when uplifted above sea level, can erode back into sediments. All the minerals found in short-term cycles can also participate in long-term cycles. Calcium accumulates along with carbonate in limestone deposits. Under anaerobic conditions, sulfur and iron atoms can form pyrite (FeS2) molecules, which accumulate in crystals. When exposed to

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All of the biogeochemical cycles operate through the food chain. The carbon cycle is shown in solid lines. Plants absorb carbon dioxide and produce organic molecules, which pass through the food chain; decomposers release carbon dioxide back into the atmosphere. The nitrogen cycle is shown in dashed lines. Nitrogen-fixing bacteria, most of which live in the roots of leguminous plants, transform nitrogen gas into fertilizers, which the leguminous plants use to make their proteins. Decomposers release the fertilizers from dead leguminous plants. Other plants absorb nitrogen fertilizers from the soil amd make their own proteins. Animals make their proteins from the proteins in the plants that they eat. The cycle of minerals (such as calcium or potassium) is shown in dotted lines. Plants obtain minerals from the soil, animals obtain minerals by eating plants, and decomposers release minerals from dead plants and animals into the soil.

oxygen gas, pyrite degrades into iron and sulfate ions (sulfuric acid). Sulfate can be ejected into the atmosphere by volcanic explosions. in both of these ways, sulfur atoms can reenter short-term cycles. Organisms play important roles in long-term mineral cycles. For example, Acidothiobacillus bacteria considerably speed up the oxidation of pyrite into sulfuric acid. Minerals that do not play a significant role in most biological systems generally travel through long-term mineral cycles. Silicon atoms exist primarily in the form of quartz (SiO2). although some organisms use SiO2 (for example, in the cell walls of grasses), for the most part, silicon remains in the soil until, eventually, that soil is transformed into rock.

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in addition to the minerals mentioned, many relatively rare minerals circulate through short- and long-term cycles. Many of these, such as aluminum, zinc, manganese, molybdenum, nickel, and copper, are required in very small quantities to assist some enzyme reactions in cells. (iron also functions in this role.) copper, like iron, is also a common component of proteins that conduct electrons in photosynthesis and respiration. animals require a small quantity of iodine in order for their thyroid glands to work properly. Because they are required in such small quantities, they are called micronutrients. in most cases, soils contain enough micronutrients, although this is not always the case. Humans can get enough iodine by eating seafood or even by breathing sea spray. certain inland locations, however, are deficient in iodine.

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72 72 biogeography  Micronutrients are generally poisonous at high concentrations. In addition, there are some minerals, such as arsenic and mercury, that are poisonous at low concentration and have no positive biological function. Some soils, generally of very limited geographical extent, contain high concentrations of these minerals. An example is serpentine soils (named after the mineral from which they form), which cover about 1 percent of California and much less of the Appalachians. These soils have a low ratio of calcium to magnesium. This is important because the same proteins allow plant roots to absorb both calcium and magnesium. As a result, in serpentine soils, the plants absorb too much magnesium and too little calcium. Serpentine soils are also deficient in phosphorus and contain high levels of heavy metals such as nickel and chromium. As a result, the plants that live in serpentine soils grow slowly and are sometimes of species or varieties (such as the oak Quercus durata and the wildflower Phlox hirsuta) that are specifically adapted to these conditions. In some cases, biological processes can bring toxic minerals into the food chain and enhance their biogeochemical cycling. Mercury atoms enter the air and water from the erosion of mineral deposits or the burning of coal. Most of the mercury contamination in the food chain, however, occurs in the form of methyl mercury, a biological derivative of elemental mercury that is produced by some bacteria. Plant roots also absorb strontium-90, a dangerous product of nuclear fission, because the proteins that absorb calcium cannot distinguish between it and strontium. This is how strontium-90, once it enters the food web, accumulates in the bones of animals. Strontium-90 entered ecosystems as a result of atmospheric testing of nuclear weapons. Intact ecosystems with high levels of biodiversity are essential to biogeochemical cycles. In some cases, only certain species can transform molecules from one form to another. In particular, only certain bacteria carry out nitrogen fixation, which brings nitrogen atoms into the food chain. As mentioned, only certain plant species can survive in serpentine soils. Without these species, serpentine deposits would experience high rates of erosion, thus introducing contaminants into nearby ecosystems. As the ecologist Peter Vitousek and associates (including Jane Lubchenco, head of the National Oceanic and Atmospheric Administration) explain, human activities have greatly altered biogeochemical cycling. This includes not only human impacts on soil erosion and global warming but also on the spread of invasive species. See also carbon cycle; ecosystems; Gaia; greenhouse effect; hydrological cycle; invasive species; nitrogen cycle.

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first entry Further Reading Asner, Gregory P., and Peter M. Vitousek. “Remote analysis of biological invasion and biogeochemical change.” Proceedings of the National Academy of Sciences USA 102 (2005): 4,383–4,386. Barrett, J. E., et al. “Co-variation in soil biodiversity and biogeochemistry in northern and southern Victoria Land, Antarctica.” Antarctic Science 18 (2006): 535–548. Beare, M. H., et al. “A hierarchical approach to evaluating the significance of soil biodiversity to biogeochemical cycling.” Plant and Soil 170 (1995): 5–22. DeGraaf, Maaike C. C., et al. “Biodiversity, vegetation gradients and key biogeochemical processes in the heathland landscape.” Biological Conservation 142 (2009): 2,191–2,201. Gadd, G. M., ed. Fungi in Biogeochemical Cycles. New York: Cambridge University Press, 2006. Turner, T. L., et al. “Population resequencing reveals local adaptation of Arabidopsis lyrata to serpentine soils.” Nature Genetics 42 (2010): 260–263. Vitousek, Peter M., Harold A. Mooney, Jane Lubchenco, and Jerry M. Melillo. “Human domination of Earth’s ecosystems.” Science 277 (1997): 494–499.

biogeography  Biogeography is the study of

where organisms live and how they got there. It is an essential part of understanding biodiversity. Biogeography is also inseparable from evolutionary science. In fact, biogeography allowed some initial insights into the fact that evolution had occurred. In The Origin of Species, Darwin noted that major groups of animals lived on certain continents and not on others that had similar climates because they had evolved on those continents. This insight from biogeography was also valuable to Darwin’s friend Alfred Russel Wallace, who also discovered natural selection. Wallace noticed that the (primarily placental) mammals of Asia were very different from the (primarily marsupial) mammals of New Guinea and Australia. This is still one of the best examples of evolutionary biogeography. Probably the biggest process that has affected biogeography over the history of life on Earth has been continental drift. Continents have moved, coalesced into supercontinents, then split apart in different clusters. Continental coalescence brought different species into contact for the first time and allowed new species to evolve in response to one another. Subsequent splitting isolated them and allowed them to follow separate evolutionary directions. Continental movements are the major explanation for the biogeographic realms, which have largely separate sets of species. Using the classification system of the biogeographer E. C. Pielou, these realms are:

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biogeography  ●● ●● ●● ●● ●● ●● ●● ●●

Nearctic (North America) Neotropical (Central and South America) Palaearctic (Europe and western Asia including the Mediterranean region) Ethiopian (Africa south of the Mediterranean region) Oriental (eastern Asia) Australasian (Australia and nearby islands) Oceanian (Pacific islands) Antarctic (Antarctica)

Not only have the continents moved, but mountains have arisen and subsequently eroded away. Climatic changes have also created barriers such as deserts between populations that were once in contact with one another. Mountains and deserts can separate a population into two or more populations as surely as can an ocean. When populations are separated, one species can become many, a process known as adaptive radiation, and different species can evolve similar adaptations independently of one another in each isolated region, a process known as convergence.

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Global Patterns of Vicariance and Dispersal When geographical barriers split a previously unified population or species, allowing speciation, the resulting geographical pattern is due to vicariance. Alternatively, individuals of a species can migrate to a new location. The resulting geographical pattern is due to dispersal. Since each dispersal event is independent, it is unlikely that broad-scale biogeographic patterns are due to dispersal. Often, biogeography on a higher taxonomic level (such as class or family) may need to invoke more ancient continental movements and climatic changes, while biogeography on a lower taxonomic level (such as genus or species) may be attributed to more recent continental movements and climatic changes. Consider the example of the oak family, Fagaceae: ●●

The oak family, Fagaceae, apparently evolved soon after the breakup of the supercontinent Pangaea at the end of the Mesozoic era. This family may have been found throughout the supercontinent remnants. Since the northern and southern continents diverged, they have remained largely separate, except for the connection of Africa to Eurasia, the collision of the Indian subcontinent into Eurasia, and the recent formation of the Isthmus of Panama. Because the family Fagaceae was already in existence, both hemispheres contain members of this plant family. Recently, some scientists have split

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the southern members of Fagaceae into their own family, the Nothofagaceae. The modern genera within the Fagaceae family evolved after the separation of northern from southern continents. Therefore, oaks (genus Quercus), chestnuts (genus Castanea), and beeches (genus Fagus) are restricted to the northern continents, where they evolved (see table on page 74), while South America and Australia have the genus Nothofagus, where it evolved. Some 50 million years ago, North American and European forests were continuous with those of northern Asia. Thereafter, climates began to change, and the northern continents drifted apart. Asian, North American, and European oaks were separated from one another. Within North America, the development of the Rocky Mountains and the southwestern desert separated the western oaks (especially in California) from the oaks of the eastern deciduous forest. Europe and North America had apparently already separated by the time the red oak subgenus (section Lobatae) and cork oak subgenus (section Cerris) had evolved; red oaks are found only in America and cork oaks only in Eurasia. Separate species within the white oak subgenus (section Quercus) are found in America, Europe, and eastern Asia (see table on page 74). Further speciation occurred after the separation of North America and Europe. California, separated by mountains and deserts, has a completely separate set of oak species from eastern North America.

Many plant families are largely tropical, and they have remained in the tropical areas of the world as the continents have moved. Some of them have a pantropical distribution, in tropical forests all over the world, while others are found only in the Old World or the New World. There are numerous examples of families, genera, or subgenera of plants that are found only in the Northern Hemisphere, for example the oaks, beeches, and chestnuts; elms (genus Ulmus); birches (genus Betula); cottonwoods (genus Populus, section Aegiros); aspens (genus Populus, section Populus); and maples (genus Acer) (see table on page 74). There are fewer examples of families, genera, or subgenera restricted to the temperate regions of the Southern Hemisphere in the manner of Nothofagus. This may be because the cold climates of the Southern Hemisphere are not as cold as those of the Northern Hemisphere. There is almost no land surface in the Southern Hemisphere

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Biogeography of Selected Species of Angiosperms   (Excluding Tropical Areas and the Southern Hemisphere) Plant Group

North America

Europe and Western Asia

Eastern Asia

Fagaceae: Fagus

Fagus grandiflora

Fagus sylvatica

Fagus crenata

Fagaceae: Castanea

Castanea dentata

Castanea sativa

Castanea crenata

Quercus ilex

Quercus lanata

Quercus suber

Quercus acutissima

Fagaceae: Quercus Section Lobatae

Quercus rubra

Section Quercus

Quercus alba

Section Cerris Ulmaceae: Ulmus

Ulmus americana

Ulmus glabra

Ulmus parvifolia

Betulaceae: Betula

Betula nigra

Betula pendula

Betula utilis

Section Alnus

Alnus serrulata

Alnus cordata

Alnus japonica

Section Clethropsis

Alnus maritima

Betulaceae: Alnus

Salicaceae: Salix

Alnus nitida

Salix nigra

Salix alba

Salix tetrasperma

Section Aegiros

Populus deltoides

Populus nigra

Section Populus

Populus tremuloides

Populus tremula

Populus adenopoda

Acer saccharum

Acer platanoides

Acer palmatum

Salicaceae: Populus

Aceraceae: Acer

climatic zone that corresponds to the tundra of the Northern Hemisphere, for example. Furthermore, the Southern Hemisphere is mostly ocean, and water does not change in temperature as readily as does land. The gentler temperature conditions of the Southern Hemisphere temperate zone have apparently allowed many otherwise tropical plant families to extend throughout South America and Africa. In these examples, vicariance seems to explain most of the patterns of plant biogeography. In some cases, dispersal appears to have also played a role. For example, most willows (genus Salix) are found in northern continents (see table), but a few species are found in the southern continents: Salix humboldtiana in South America and Salix cinerea in Australia. These may be the evolutionary descendants of willows that dispersed southward. In contrast to trees, the differences between Eurasian and North American mammal genera may be attributed primarily to dispersal. The major modern genera of mammals (such as bears, raccoons, deer, horses, bison, etc.) evolved after North America and Eurasia had separated. These animals dispersed across the Bering land bridge (Beringia). This dispersal occurred more readily in periods between ice

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ages. This explains why North America and Eurasia share many genera but not many species of mammals. Dispersal may explain the biogeography of groups of animals more readily than of plants. Birds, some of which migrate thousands of miles, disperse best of all. Some groups of organisms are cosmopolitan, or worldwide, in their distribution. This may be the result of both vicariance and dispersal. The major examples appear to be groups of organisms that disperse very well or live in disturbed habitats: rodents among mammals and plants in the mustard (Brassicaceae), composite (Asteraceae), bean (Fagaceae), and grass (Poaceae) families. Placental mammals proliferated in the northern continents, while marsupial mammals proliferated in the southern continents, and they remained largely separate from one another. By about a million years ago, the Isthmus of Panama formed a land bridge over which placental mammals dispersed from the Nearctic realm into South America and marsupial mammals in the opposite direction. Plants of temperate climates, not adapted to tropical conditions and less mobile than animals, did not disperse across this land bridge. As it turned out, placental mam-

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biogeography  mals frequently drove marsupial mammals toward extinction by competition. The placental mammals of South America, now dominant, are the descendants of invaders from North America. Most of the marsupials that moved north into North America became extinct except for the opossum. Meanwhile, Australia and New Guinea remained separate and the territory of marsupials. Few placental mammals made the journey into the Australasian realm. One exception was humans. Homo erectus ventured into the islands of Indonesia and became Java Man, but there is no clear evidence that they traveled to Australia. Some may have become isolated on the island of Flores, evolving into the diminutive species Homo floresiensis. Modern humans dispersed to Australia at least 50,000 years ago and brought dogs with them. For thousands of years, humans and dogs were the main placental mammals of Australia. Australian marsupials included many species that were similar to placental species but that had evolved separately. Europeans brought placental mammals, such as rodents and livestock, with them. Once again, the placental mammals proved to be the superior competitors. Most of the Australian marsupials, except for various species of kangaroo, have become rare or extinct, largely as a result of competition with the placental invaders. When a continental fragment separates, it may sometimes retain a collection of species that closely resemble their ancestors because they are not exposed to many of the newly evolved continental species. This appears to be what happened with the island of New Caledonia. The forests consist largely of conifers more similar to those that dominated Mesozoic forests than to those that dominate modern forests. This is why film crews who want a realistic backdrop for dinosaur movies choose New Caledonia for their film site. The species of flowering plant that most closely resembles the presumed ancestor of all flowering plants, Amborella trichopoda, is found only on New Caledonia. New Caledonia is one of the biodiversity hot spots and contains many more unique plant species per unit area than any of the other hot spots. Some distribution patterns remain mysterious. One example is the plant family Empetraceae (crowberries), which are found in the cool regions of North America and Eurasia but also at the cool tip of South America and in the warm climate of Florida. This is difficult to explain in terms of continental movements or dispersal to another habitat with similar climatic conditions.

Islands Islands, starting with Darwin’s experience in the Galápagos Islands, have proven to be evolutionary

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75

showcases. When a new island forms, it receives only a genetic subset of organisms from the nearby mainland. In particular: ●●

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In any species some of whose members disperse to a new island, only a small portion of the mainland genetic variability may be represented on the island. This founder effect may be followed by random genetic changes in the population (genetic drift) if the island population remains small. The newly arrived species may have fewer parasites and perhaps no predators or competitors. This may, if the species happens to be well suited to the physical environment of the island, allow a population explosion, leading to evolutionary change and diversification. Many small mammals remain small partly because their small size allows rapid population growth, giving them an advantage in competition, but on an island with fewer or no competitors, the small mammals may evolve into larger forms. The same thing appears to happen in plants. Many small, weedy plants have an advantage due to rapid growth and early reproduction. In this way, they avoid competition with large trees. When the plants disperse to an island where there are no trees, the weedy plants may evolve into a tree form. The plant family Asteraceae consists mostly of weedy herbaceous plants, except on some islands (such as the Channel Islands of California and St. Helena in the Atlantic), where they have evolved into small trees. The nettle family Urticaceae consists mostly of weedy herbaceous plants, but on Hawaii there is a bush nettle. Many large mammals remain large partly because their large size allows them to resist the attacks of predators, but on an island with no predators, the large mammals may evolve into smaller forms. Mammoths on Wrangel Island, northeast of Siberia, and on Santa Rosa Island, off the coast of California, evolved into smaller forms. Another example is the previously mentioned Flores Island people, Homo floresiensis. Some large mammals evolved into smaller forms on this island at the same time that the Flores Island people lived there; the predator exclusion explanation, however, is unlikely to be true for the small size of these people. The explanation for the small size of the Flores Island people remains a mystery.

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first entry

Many island species lose their defenses. Since defenses (spines or chemicals in plants and behaviors in animals) can be expensive, natural selection favors their loss in conditions where they are not useful. Many island plants have lost their defenses. For example, not only is the Hawaiian nettle unusual in its family for being a bush but also for its lack of stinging hairs. Numerous island animal species (reptiles, birds, and mammals) are notorious for their lack of fear of humans, with whom they have had little contact until recently. In order to get to an island in the first place, plants and animals need to have superior dispersal abilities. Once on the island, many lose their dispersal abilities. One extreme example is the flightless cormorant of the Galápagos Islands. On some islands, plant families with small seeds have produced species with seeds larger than are normal for the family.

Ice Ages Genera and even species of plants are shared between the arctic and alpine tundras, enough to allow these two regions to both be called tundras. Arctic tundra is found around the Arctic Ocean, while alpine tundra is on mountaintops. This biogeographical pattern is explained mostly by the Ice Ages. When glaciers were at their maximum extent, the arctic tundra formed a band across what is now the northern United States and extended as far south as Chicago. The Rocky Mountains, Sierra Nevada, and Cascades received tundra species from contact with this band of tundra, and some mountains that were not in direct contact with the tundra (e.g., the San Francisco Peaks of Arizona) were close enough to receive tundra species by dispersal. When the glaciers retreated northward, the tundra plants retreated into the remaining zones of cold climate, either northward, where they are found today in the arctic tundra, or up the mountains, where they are today found on alpine peaks. The alpine tundra is now stranded, sometimes in very small patches (as in the San Francisco Peaks). This is not the entire explanation for tundra plant species. The tundra of the Sierra Nevada contains not only species affiliated with the arctic but also the evolutionary descendants of desert species, such as the buckwheat Eriogonum. The tundra of the Sierra Nevada not only has drier soil than other tundras but also is close to the desert. Adaptations to cold and to drought are often similar, and this similarity allowed some desert plants to adapt to tundra conditions in California. This pattern is also evident

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in some animals: The caribou of the cold climates of North America is the same species as the reindeer of the cold climates of Eurasia. Most of the North American continent south of the tundra was boreal (mainly spruce) and pine forests. Nearly the entire area that is now the Great Plains was covered with white spruce (Picea glauca). There was a small area of grassland in what is now Texas, but there was no hot desert. It would have been an alien world to modern eyes. There were many modern mammals but also many mammals such as mammoths and mastodons that have become extinct. Most of the trees and other plants would have been familiar to modern observers, but they were in combinations that no longer exist. For example, in some places there were spruce trees scattered in grassland, an arrangement uncommon today. As the ice sheets retreated, each surviving species moved to new locations independently, and some species dispersed more rapidly than others. The glacial retreats and the movements of species were not uniform; glaciers sometimes temporarily advanced again. The forests are still moving, though too slowly for human observers to notice without consulting long-term records. The tallgrass prairie did not exist before or during the ice ages. The tall, deep-rooted, warm-weather grasses of the prairie were established during the period of maximum warmth (the hypsithermal period, about 7,000 years ago). The prairies persisted even when conditions became cooler and wetter until American agriculture and civilization destroyed most of them. The prairies persisted because periodic fires killed any forest trees that began to encroach. In North America, where most mountain ranges run in a north-south orientation, there were few barriers to the primarily northward movement of plant and animal species. In Europe, however, the Mediterranean Sea and mountain ranges such as the Alps were barriers to northward movement. This helps explain why British forests have fewer species of trees and spring wildflowers than do many American forests. The explanations for current patterns of distribution and diversity are rooted in the past rather than in modern climatic conditions. The greenhouse effect may be altering the patterns of species movement that have been occurring for the past few millennia. Humans have had a tremendous effect on biogeographical patterns. First, humans have carried species of plants and animals from one place to another. In some cases, these plants and animals have become invasive, displaced native species, and greatly altered the original environment. Humans have allowed species to disperse, especially by ship and airplane, more effectively than almost any spe-

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biological classification  cies could previously have dispersed. Second, humans have created a great deal of disturbed habitat (such as farming, road building, and construction). Species that specialize in disturbed areas (especially weeds) have found a worldwide network of suitable habitats, courtesy of humankind. Some of the most widespread species, such as dandelions and barn swallows, live in areas altered by human activity. Finally, humans are causing a greenhouse effect that greatly exceeds any of the periods of global warming that have occurred between the ice ages. See also adaptive radiation; boreal and subalpine forests; coevolution; convergence; Darwin, Charles; founder effect and genetic drift; invasive species; island biogeography; mammals; Pleistocene extinction; speciation; tundra; Wallace, Alfred Russel. Further Reading Bonnicksen, Thomas M. America’s Ancient Forests: From the Ice Age to the Age of Discovery. New York: John Wiley and Sons, 2000. Cox, C. Barry, and Peter D. Moore. Biogeography: An Ecological and Evolutionary Approach. Hoboken, N.J.: John Wiley, 2010. Gillespie, Rosemary G. “The ecology and evolution of Hawaiian spider communities.” American Scientist 93 (2005): 122–131. Grehan, John R., and Jeffrey H. Schwartz. “Evolution of the second orangutan: Phylogeny and biogeography of hominid origins.” Journal of Biogeography 36 (2009): 1,823–1,844. International Biogeography Society. “The International Biogeography Society.” Available online. URL: http:// www.biogeography.org. Accessed July 4, 2010. MacDonald, Glen M. Biogeography: Space, Time, and Life. New York: John Wiley and Sons, 2003. McCarthy, Dennis. Here Be Dragons: How the Study of Animal and Plant Distributions Revolutionized Our Views of Life and Earth. New York: Oxford University Press, 2009. Médail, Frédéric, and Katia Diadema. “Glacial refugia influence plant diversity patterns in the Mediterranean Basin.” Journal of Biogeography 36 (2009): 1,333–1,345. Pielou, E. C. Biogeography. Malabar, Fla.: Krieger, 1992. Quammen, David. Song of the Dodo: Island Biogeography in an Age of Extinctions. New York: Scribner, 1996. Whittaker, Robert J. Island Biogeography: Ecology, Evolution, and Conservation. New York: Oxford University Press, 1998. Woodruff, David S., and Leslie M. Turner. “The Indochinese-Sundaic zoogeographic transition: A description and analysis of terrestrial mammal species distributions.” Journal of Biogeography 36 (2009): 803–821.

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77

biological classification  The system used

by most biologists to classify species of organisms into nested categories was invented by the Swedish botanist Carl von Linné, also known as Carolus Linnaeus. Taxonomy is the study of classification. Before Linnaeus, the classification of organisms was in disarray. First, each species was usually identified by long Latin descriptions. For example, the common ground cherry was called Physalis amno ramosissime ramis angulosis glabirs foliis dentoserratis, which means, in part, that it had angled stems and that the leaves were hairless and had toothed margins. Linnaeus shortened these long names to two-word names (in this case, Physalis angulata, a name it still carries). Thus, Linnaeus established the practice of binomial nomenclature (“naming system that uses two names”). Second, the same species could be given different descriptive names by different botanists. Linnaeus standardized the names. Was Rosa sylvestris alba cum rubore, folio glabro, the same as Rosa sylvestris inodora seu canina? Linnaeus standardized it to Rosa canina. Mistakes still happen, in which the same species is accidentally given two different names, but this error is uncommon. These innovations were accepted by the biological community with a sense of relief, but this was not the most important innovation of the Linnaean system. Before Linnaeus, there was no recognizable basis for classification. Some zoologists classified animals on the basis of terrestrial versus aquatic, others on the basis of big versus small. The French paleontologist Georges Buffon organized animals according to their usefulness in the human economy. Linnaeus brought order into this chaos. In classifying plants, Linnaeus recognized that reproductive characteristics were less variable than the characteristics of leaves and stems. He therefore classified plants on the basis of the numbers and condition of the stamens (male parts) and pistils (female parts) of their flowers. Consistent with the male bias of science and society, Linnaeus’s major axis of classification was the number of stamens: 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 12, and many individual stamens; the grouping of the stamens (tetradidymous, dididymous, monadelphous, diadelphous, polyadelphous); the fusion of stamens to one another or to pistils; and plants with separate male and female flowers on the same tree (monoecious) or different trees (dioecious) or a mixture of arrangements. His last class, the cryptogams (crypto- means hidden), consisted of plants that had no obvious flowers. Within the male axis, he divided plants on the basis of their female parts. He applied his system in a rigid fashion that resulted in classifications that are surprising to modern botanists. For example, he placed oaks,

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78 78 biological classification  beeches, hazelnuts, and cattails into the same category; modern botanists recognize cattails as very different from the other three. The central feature of the Linnaean system is that it is a nested hierarchy. The specific epithet (the second of the two words in the name) referred to the species, and the genus name (the first word) was given to a set of closely related species. As the system was modified by later scientists, closely related genera were clustered into families, closely related families into orders, closely related orders into classes, closely related classes into phyla, and phyla into the major kingdoms, of which there were originally only two: plants and animals. Linnaeus inspired the scientific world because he brought, or revealed, order within the diversity of organisms on Earth, which was just then being thoroughly explored. The Linnaean system seemed to correspond closely to the concept of the Great Chain of Being, also known as the scala naturae. All things, from rocks to plants to animals to humans to angels to God, were believed to be connected like a tapestry of fibers. Scientists were not surprised to find intermediate entities—for example, a sponge as intermediate between animal and rock, or beings halfway between humans and apes—because they were all part of the created tapestry. Linnaeus had no thought of the evolutionary origins of organisms. This is revealed by the fact that he applied his system to rocks as well as to organisms. Linnaeus tried to make the system as natural as possible by using characteristics that were a realistic reflection of the Chain of Being. While Linnaeus gave no thought to evolution, the fact that the natural world could be so readily classified into nested categories struck Charles Darwin as being a major piece of evidence favoring evolution. Despite naturalists’ belief in the scala naturae, there actually were not many intermediates between modern entities. Sponges are not really half-rock, half-animal. Dogs, wolves, coyotes, and foxes form a group of similar canines; cats, lions, tigers, leopards, and cheetahs form a group of similar felines; and there are no cat-dogs. Organisms, as Linnaeus classified them, display a pattern like branches of an evolutionary tree. Today, biologists attempt to classify organisms using the Linnaean system but try to make the system as natural as possible by defining genera, families, orders, classes, and phyla on the basis of evolutionary divergence. The species themselves are recognized on the basis of reproductive isolation. When a group of species share many features with one another, scientists conclude that they evolved from a common ancestor more recently than species that share few features.

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first entry The Latin (or Greek) generic and specific names may describe the characteristics that make the genus or species different from other species or genera; they may describe visible features of the organism or the location in which it lives; they may be the ancient Greek or Latin names for the organisms; or they may be a tribute to a scientist who studied the organisms. For example, dogs are Canis familiaris—genus Canis, species familiaris. Canis is a Latin word for “dog.” Other members of the genus Canis include Canis lupus, the wolf (lupus is Latin for “wolf”), and Canis latrans, the coyote (latrans comes from Latin for “barking”). This system of groupings also explains the higher levels of the Linnaean system (see figure on page 79): ●●

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Genera that evolved from a common ancestor most recently and are therefore most similar to one another are grouped together into the same family. The canid family, Canidae, contains all the doglike animals, such as foxes, along with the true dogs. Families that evolved most recently from a common ancestor and are therefore most similar to one another are members of the same order. Canids, along with cats, bears, raccoons, weasels, badgers, skunks, and otters, are members of the order Carnivora, the carnivores. The families in the carnivore order share common features such as the kinds of teeth they possess. Orders that evolved most recently from a common ancestor and are therefore most similar to one another are members of the same class. Carnivores, along with all other mammals, are members of the class Mammalia. The orders within the mammal class share common features such as the production of hair and milk. Classes of animals and protists that evolved most recently from a common ancestor and are therefore most similar to one another are members of the same phylum (plural, phyla). In plants, fungi, and bacteria, this category has traditionally been called a division. Mammals, along with all other vertebrates (most of which possess a backbone), and those other animals that have a flexible rod instead of a backbone are members of the phylum Chordata. Phyla or classes of organisms that evolved most recently from a common ancestor and are therefore most similar to one another are members of the same kingdom. Most biologists recognize five kingdoms of organisms.

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The chordates and the arthropods are two of the phyla within the animal kingdom. The mammals are one of the classes within the chordate phylum. Carnivores and primates are two of the orders within the mammalian class. The canids (dogs, wolves, and coyotes) and the felids (lions, cheetahs, and housecats) are two families within the carnivore order.

In recent years, biologists have classified kingdoms into three domains. Two of the domains, often placed into the kingdom Monera, consist of singlecelled organisms commonly called bacteria: ●●

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The archaebacteria (domain Archaea) live in environments such as deep ocean volcanic vents and salt slush that, while they seem extremely inhospitable to humans, are similar to the conditions found on the early Earth. The eubacteria are mostly the bacteria that live in soils and water and on or in larger organisms on Earth’s surface. Some of them are green and make food energy from sunlight by photosynthesis.

The other three kingdoms consist of organisms that either are, or are constructed from, a more complex form of cell called eukaryotic, and make up the domain Eucarya: ●●

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The protists are either single-celled or, if multicellular, are not organized into fully integrated bodies. The fungi secrete digestive enzymes, then absorb the digested food molecules individually from the environment. Plants make food from small molecules in the environment using energy from the Sun. Animals consume food as particles or chunks rather than as individual molecules.

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The protists do not all have a common ancestor that differs from the common ancestor of fungi, plants, and animals. Therefore, it is not a monophyletic group. Many biologists no longer recognize the kingdom Protista as a formal category. Instead, they divide all of life into three domains; the fungi, plants, and animals are kingdoms within one of these domains. Early in the 20th century, some biologists applied the Linnaean system at least roughly to communities, particularly of the plants that dominated the landscape. Therefore, to ecologists such as Frederick Clements, a forest of pines (genus Pinus) was quite literally a Pinetum, and an oak forest (genus Quercus) was a Quercetum. By the middle of the 20th century, however, biologists realized that each species of organism had its own geographical range and set of habitat preferences. A pine forest was not a coherent entity but rather a collection of interacting species that happened to be in the same place. Scientists have described more than 1 million species. They have had to extensively modify the Linnaean system in order to accommodate the astonishing diversity of the natural world. For example, some large families must be broken into subfamilies and tribes, and orders into infraorders; groups of orders are superorders. That is, the Linnaean system still works only because of extensive fixes. Some evolutionary scientists have decided the Linnaean system is not worth all the bother. For example, the Tree of Life project Web site classifies many of the known species of organisms within nested groups (each connected to the next by hyperlinks), but the

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80 80 biological species concept  levels do not correspond rigidly to the Linnaean system. In its classification of the flowering plants, for example, it separates Amborella trichopoda from a branch (or clade) containing all other flowering plants. Within this other branch, one branchlet contains the families Chloranthaceae, Ceratophyllaceae, and the monocot, magnoliid, and eudicot groups—a mixture of families and clusters of orders. It is possible to fit this into a Linnaean system, but only by placing Amborella by itself in its own order and family. Evolutionary biologists may assign a name to each clade, regardless of whether it is a species, genus, or higher level of classification. They refer to this system as “rank-free” classification. The International Society for Phylogenetic Nomenclature is working on an evolution-based system, called PhyloCode, to replace the Linnaean system. Some have even suggested that the species concept should be replaced with “least-inclusive taxonomic unit.” The PhyloCode approach is not without its critics, one of whom wrote an article entitled “Critique of pure folly.” Some PhyloCode critics, such as the biodiversity expert Edward O. Wilson, see it as too much of a disruption right at the time that scientists are trying to identify as many species as possible. See also cladistics; Darwin, Charles; eukaryotes; speciation. Further Reading Benton, Michael J. “Stems, nodes, crown clades, and rankfree lists: Is Linnaeus dead?” Biological Reviews 75 (2000): 633–648. Cantino, P. D., et al. “Species names in phylogenetic nomenclature.” Systematic Biology 48 (1999): 790–807. Dayrat, B., et al. “Suggestions for a new species nomenclature.” Taxon 53 (2005): 485–591. DeQueiroz, Kevin, and J. Gauthier. “Phylogenetic taxonomy.” Annual Review of Ecology and Systematics 23 (1992): 449–480. Dubois, A. “Naming taxa from cladograms: A cautionary tale.” Molecular Phylogenetics and Evolution 42 (2007): 317–330. Fisher, K. “Rank-free monography: A practical example from the moss clade Leucophanella (Calymperaceae).” Systematic Botany 31 (2006): 13–30. International Society for Phylogenetic Nomenclature. “International Society for Phylogenetic Nomenclature.” Available online. URL: http://phylonames.org. Accessed August 8, 2011. Kastner, Joseph. “An Adam and his apostle.” Chap. 2 in A Species of Eternity. New York: Dutton, 1977. Nixon, Kevin C., et al. “The PhyloCode is fatally flawed, and the ‘Linnaean’ system can easily be fixed.” Botanical Review 69 (2003): 111–120. Pleijel, F., and G. W. Rouse. “Least-inclusive taxonomic unit: A new taxonomic concept for biology.” Proceed-

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first entry ings of the Royal Society of London B (Biology) 267 (2000): 627–630. Polaszek, A., and Edward O. Wilson. “Sense and stability in animal names.” Trends in Ecology and Evolution 20 (2005): 421–422. Schuh, R. T. “The Linnaean system and its 250-year persistence.” Botanical Review 69 (2003): 59–78. Tree of Life Web Project. “Explore the Tree of Life.” Available online. URL: http://www.tolweb.org. Accessed August 8, 2011.

biological species concept  See speciation. biomagnification  Biomagnification is the increasing concentration of toxic compounds in the tissues of organisms higher on the food chain. These compounds do not quickly break down upon exposure to environmental conditions such as sunlight and oxygen, nor are they readily broken down by enzymes in the tissues of organisms. In fact, the reduced ability of enzymes to break them down is what makes these compounds toxic. Some of these pollutants are elemental contaminants such as mercury, and others are organic molecules known as persistent organic pollutants (POPs). Biomagnification differs from bioaccumulation, which is the storage of toxins in the tissues of an organism. The pollutants may be present in the environment at concentrations sufficiently low that direct human contact with them is harmless. Organisms at the base of the food chain (for example, microscopic aquatic plants) may accumulate these toxins to a higher concentration because they metabolize the nontoxic compounds from the environment but store the toxins in their tissues. At each level of the food chain, an organism consumes its food, metabolizes the nontoxic compounds, and may accumulate the toxins. This causes the toxins to reach a higher concentration in the tissues of organisms with each level in the food chain. One of the functions of the liver is to break down toxic materials that are absorbed into the bloodstream, particularly toxic materials that are part of the food absorbed by the intestines and delivered to the liver by the hepatic portal vein. Toxins may accumulate in the liver rather than being eliminated by the kidneys. One famous example of biomagnification and one of the earliest to be discovered involved the pesticide DDT, which was sprayed extensively to control mosquitoes (see figure on page 81). DDT levels were particularly high in wetlands, but still not high enough to cause harm to humans upon direct exposure. Ospreys, which are birds of prey, eat large fish from wetlands. In the 1960s, biologists noticed

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Persistent organic pollutants, such as the pesticide DDT, may contaminate a wetland, but in vanishingly small concentrations (in this case, only 0.00005 parts per million, or 50 parts per trillion). Nevertheless, the pollutant accumulates in the tissues of organisms, becoming more concentrated at each link in the food chain. DDT accumulation in top predators, such as ospreys, can be high enough to endanger their survival.

that the osprey populations were declining in a wetland near new york city because the eggs had weak shells and frequently cracked open. the pesticide DDt had accumulated in the bodies of the ospreys and caused them to lay eggs with shells deficient in calcium. DDt concentrations as high as 14 parts per million (ppm) were found in the eggs of the ospreys, enough to cause the damage that was observed. However, the water contained only 0.00005 ppm. Bioaccumulation had occurred in the following manner. DDt from the water was also found in the microscopic aquatic plants. Many of the molecules that made up the microscopic plants were broken down by the microscopic animals that consumed them. Much of the plant biomass was lost as respiratory cO2 or excreted as wastes. the microscopic animals could not digest the DDt, which accumulated in the animals’ fat deposits. Because the total amount of biomass was reduced and the amount of DDt was not, as matter flowed through the food web from one level of the food chain to another, the DDt became concentrated. in the microscopic animals found in this estuary, the DDt reached a concentration of 0.04 ppm—a concentration more than a thousand times higher than in the water. the microscopic animals were eaten by small fi sh, which stored DDt in their livers. the average DDt concentration of the small fi sh was 0.5 ppm, a 12-fold increase. When big fi sh ate the little fi sh, the DDt continued to accumulate and reached a level of 1.5 ppm, a threefold increase. Finally, when ospreys ate the big fi sh, the DDt reached the toxic level of 14 ppm.

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the use of DDt has been banned in the United States since 1972, but thousands of tons of DDt are still manufactured in industrialized countries and exported, mainly to control malaria in tropical countries. the pesticides used instead of DDt on american farms today have proven, in laboratory tests, to be short-lived. Because they are supposed to break down shortly after killing the insects, they do not have time to undergo biomagnification. For this reason, they have been considered safe by government regulators and by the companies that manufacture them. However, some of these same pesticides have been detected in well water. the pesticides slowly percolated through the soil and contaminated the groundwater. this process took a longer time than the supposed lifetime of the pesticides. When deep in the soil and in the groundwater, the pesticides were not in contact with oxygen and warm temperatures, which are apparently important in breaking them down. in some tropical african countries, the agricultural use of DDt was banned in the 1990s, but DDt could still be used to control mosquitoes that spread malaria. However, the ban made DDt harder to obtain, and many people died of malaria. the use of DDt for mosquito control has been resumed in these countries. Perhaps the most notorious example of biomagnification involved mercury pollution in Japan. industrial plants dumped mercury wastes into Minamata Bay in the middle of the 20th century. the mercury atoms, incorporated into an organic molecule (methyl mercury), underwent biomagnification to toxic levels

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first entry

in the local seafood. Many people experienced permanent nerve damage from eating the seafood in the 1960s. Bioaccumulation of radioactive wastes occurred in reindeer that ate plants contaminated with the fallout from the nuclear plant that exploded at Chernobyl, in the Ukraine, in 1986. Unlike Minamata in the 1960s, the Ukraine in the 1980s avoided extensive human illness from bioaccumulation because the concept had become well established and health officials were able to prevent the consumption of contaminated food following the release of radioactive wastes from the Chernobyl nuclear disaster. The biologist Rachel Carson brought intense and rapid public attention to biomagnification, as well as other problems associated with the use of pesticides, in her 1962 book Silent Spring. A decade later, the United States banned the use of DDT. Most nations now recognize that biomagnifications and other pollution problems cross national boundaries and that international agreements are necessary in order to control the problem. The United States was one of 90 signatories to the Stockholm Conven-

The Twelve Persistent Organic Pollutants Controlled by the 2001 Stockholm Convention Pollutant

Use/Source

Aldrin

insecticide

Chlordane

insecticide

Dichlorodiphenyltrichloroethane (DDT)

insecticide

Dieldrin

insecticide

Endrin

insecticide

Heptachlor

insecticide

Hexachlorobenzene

fungicide, industrial chemical, combustion

Mirex

insecticide

Toxaphene

insecticide

Polychlorinated biphenyls (PCBs)

industrial chemical, combustion

Polychlorinated dibenzo-p- combustion dioxins (dioxins) Polychlorinated dibenzo­ furans (furans)

combustion

Note: From U.S. Environmental Protection Agency

xviii+598_Biodiversity_F.indd 82

tion of 2001, which limited the production, use, and release of the 12 most abundant POPs, often called “the dirty dozen” (see table). Environmental activists continue to oppose the construction of new coal-fired power plants because the combustion of coal releases a small amount of mercury—a small amount that can be magnified by the food chain. Organic chemicals that are not on the “dirty dozen” list, such as endosulfan, can persist long enough in the environment to penetrate into ecosystems far from their point of release. See also biogeochemical cycles; Carson, Rachel. Further Reading Environmental Protection Agency. “Persistent organic pollutants: A global issue, a global response.” Available online. URL: http://www.epa.gov/oia/toxics/pop.html. Accessed August 8, 2011. Hu, Guo-cheng, et al. “Bioaccumulation behavior of polybrominated diphenyl ethers (PBDEs) in the freshwater food chain of Baiyangdian Lake, North China.” Environment International 36 (2010): 309–315. Kidd, Karen A., et al. “Biomagnification of DDT through the benthic and pelagic food webs of Lake Malawi, East Africa: Importance of trophic level and carbon source.” Environmental Science and Technology 35 (2001): 14–20. Molina, Carlos Israel, et al. “Transfer of mercury and methylmercury along macroinvertebrate food chains in a floodplain lake of the Beni River, Bolivian Amazonia.” Science of the Total Environment 408 (2010): 3,382–3,391. Morel, François M. M., et al. “The chemical cycle and bioaccumulation of mercury.” Annual Review of Ecology and Systematics 29 (1998): 543–566. Weber, Jan, et al. “Endosulfan, a global pesticide: A review of its fate in the environment and occurrence in the Arctic.” Science of the Total Environment 408 (2010): 2,966–2,984.

biome  See communities, ecological. biomimicry  Biomimicry is the human imitation

of the adaptations of wild species for commercially useful purposes. The invention of new processes and products for medicine, industry, and agriculture is limited by the knowledge and imagination of researchers. In contrast, natural selection has been operating for billions of years in millions of species; relative to human knowledge, natural selection has tried out almost everything that can be done and eliminated the things that did not work well within the range of conditions in the biosphere.

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bioremediation  The Swiss engineer George de Mestral closely observed the barbs surrounding cocklebur seeds in the 1940s, which appeared perfectly adapted to entangle mammalian fur. He realized that the system of microscopic hooks and hairs could be imitated industrially. The result was Velcro, marketed in 1953. Most of the possibilities of biomimicry remain untapped. Below are some products of biological evolution that have had or may soon have great importance to the human economy. ●●

●●

●●

●●

●● ●●

Computers use binary digital code, while DNA in cells uses a digital code of four kinds of molecules, which vastly increases the potential to store and process information. The development of DNA computers, which would operate in a test tube (in vitro) rather than on a chip (in silico), currently has major hurdles, as it is difficult to control the movement and interaction of the DNA molecules. Chloroplasts use photosynthesis to convert solar energy to chemical energy with higher efficiency than any industrial process. Chloroplasts produce sugar, while solar energy technology needs to produce electricity. Researchers may be able to design artificial chloroplasts that produce electricity. Geckos (a kind of lizard) can walk on walls and ceilings, but they do so without chemical adhesives. Geckos form very short-lived bonds when electrons in the molecules of their feet displace electrons in the molecules of a wall or ceiling. Temporary adhesion that does not leave chemical residues may have very important industrial applications. The surfaces of the eyes of some moths admit light very efficiently, without reflection. Understanding the physical and chemical basis of moth eye surfaces may allow the production of much more efficient photographic imaging. Spider silk is one of the strongest materials known. A beetle in Brazil, Lamprocyphus augustus, has crystals in its iridescent green scales that focus light more precisely than can industrially produced photonic crystals. Studying this beetle may allow the development of photonic crystals that will allow the production of ultrafast optical computers.

Scientists can even gain insights from the study of ecosystems that may allow the more efficient management of commercial systems. The agricultural ecologist Wes Jackson has demonstrated that it is possible to produce a much more efficient system

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83

of agriculture (which he calls natural systems agriculture) by imitating the ecological processes of a tallgrass prairie. The direct application of biological adaptations to human use may be difficult or impossible in some cases. Many biological processes occur on a microscopic scale and will not work the same way on the human scale. Spider silk is stronger than steel for making very small fibers, but not necessarily for making larger structures. Partly for this reason, the promise of strong yet pliant spider silk body armor has thus far remained elusive. Similarly, it is unlikely that organisms much larger than geckos could walk on walls and ceilings using only the forces of electron displacement. Natural adaptations have been successful in the global environment. In contrast, many human industrial processes are destructive to the environment in the long term. Biomimicry may allow the development of processes that bring the human economy into better compliance with the ecological limitations of the biosphere. Along with the benefits to agriculture and medicine, biodiversity offers the promise of biomimicry. This is yet another reason to save as many species as possible from extinction. While some adaptations, such as DNA, are found in all organisms, many others may have evolved in only one obscure species. Who would have guessed that the key to improved photonic crystals might have been found in a Brazilian beetle? In addition, just as spider silk is stronger than silkworm silk, a breakthrough for the industrial production of yet stronger fibers might be hidden in the silk produced by some unknown species of rain forest spider. See also biodiversity, resources for agriculture; biodiversity, resources for medicine; natural systems agriculture. Further Reading Ayoub, Nadia A., et al. “Blueprint for a high-performance biomaterial: Full-length spider dragline silk genes.” Public Library of Science ONE 2 (2007): e514. Available online. URL: http://www.plosone.org/article/ info:doi/10.1371/journal.pone.0000514. Accessed July 3, 2010. Benyus, Janine M. Biomimicry: Innovation Inspired by Nature. New York: William Morrow, 1997. Mueller, Tom. “Biomimetics: Design by nature.” National Geographic, (April 2008): 68–91.

biophilia  See environmental psychology. bioremediation  Bioremediation is the use of organisms to break down or remove pollution from

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84 84 birds the environment, such as organic pollutants or heavy metals such as lead, chromium, cadmium, nickel, zinc, copper, selenium, arsenic, and even radioactive metals such as cesium and uranium. Chemists generally restrict the use of the word to the biological breakdown, rather than accumulation, of pollutants. Some natural bacteria, such as Alcanivorax borkumensis, live in sediments that contain natural petroleum seepage, and they have evolved the ability to break down oil. Other bacteria can break down compounds that are not found in nature. They do this because they have enzymes that break down chemically similar natural compounds. Examples include bacteria that break down vinyl chloride and pesticides. Some natural species are very good at accumulating toxic ions. Examples include the following: ●● ●● ●● ●● ●● ●● ●●

Indian mustard (Brassica juncea) Alpine pennycress (Thlaspi caerulescens) Sunflower (Helianthus annuus) Lichen (Trapelia involucrata) Fungi (Phanerochaete chrysosporium and Gloeophyllum sp.) Brakefern (Pteris ensiformis) Water hyacinth (Eichhornia crassipes)

Brakefern and water hyacinth absorb arsenic, and the Trapelia lichen absorbs uranium. Other wild species have a significant, though lesser, ability to accumulate toxic ions: alfalfa, cordgrass, tomato, pumpkin, bamboo, willow, poplar, and kudzu vines. Some wild plants absorb heavy metal ions precisely because they are toxic. They store the ions in vacuoles, where they will not damage the tissues, but if a herbivore eats the leaf, the vacuoles burst open and make the food poisonous. Locoweeds of the genera Oxytropis and Astragalus accumulate selenium in leaf vacuoles, a toxin against herbivores. Without bioremediation, it is nearly impossible to detoxify soil that has been polluted with industrial chemicals without destroying the structure of the soil and turning it into a big adobe brick on which most plants cannot grow. Plants that absorb toxins, however, penetrate the soil with their roots and leave it undamaged. The stems and leaves of the plants, which contain most of the toxins, can then be harvested and disposed of safely. Some biologists have produced genetically modified strains of plants that have an enhanced ability to absorb toxins. In nature, the plants absorb only as much toxin as they need for defense, but biologists can manipulate the plant’s genes such that they overexpress the genes involved in absorption. Success stories include the following. Chrysler Corporation used mustard plants to reduce the

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first entry amount of lead from contaminated soil at its industrial complex in Detroit by half, bringing it into compliance with pollution laws. Sunflowers have been used to absorb radioactive metals from areas around Chernobyl, the site of the 1986 Ukrainian nuclear disaster. See also biogeochemical cycles; bio­ magnification. Further Reading Al Agely, A., et al. “Mycorrhizae increase arsenic uptake by the hyperaccumulator Chinese brake fern (Pteris vittata L.).” Journal of Environmental Quality 34 (2005): 2,181–2,186. Arthur, E. L., et al. “Phytoremediation—an overview.” Critical Reviews in Plant Sciences 24 (2005): 109–122. Connell, S., and S. Al-Hamdani. “Selected physiological responses of kudzu to different chromium concentrations.” Canadian Journal of Plant Science 81 (2001): 53–58. Mitra, J., et al. “Bioremediation of DDT in soil by genetically improved strains of soil fungus Fusarium solani.” Biodegradation 12 (2001): 235–245. Ralebitso, T. K., et al. “Microbial aspects of atrazine degradation in natural environments.” Biodegradation 13 (2002): 11–19. Revkin, Andrew. “New pollution tool: Toxic avengers with leaves.”NewYorkTimes, March 6,2001.Available online. URL: http://www.nytimes.com/2001/03/06/science/ new-pollution-tool-toxic-avengers-with-leaves.html. Accessed August 4, 2011. Singh, O. V., et al. “Phytoremediation—an overview of metallic ion decontamination from soil.” Applied Microbiology and Biotechnology 61 (2003): 405–412. Soudek, P., et al. “Laboratory analyses of Cs-137 uptake by sunflower, reed, and poplar.” Chemosphere 55 (2004): 1,081–1,087. Vidali, M. “Bioremediation: An overview.” Pure and Applied Chemistry 73 (2001): 1,163–1,172.

birds  Birds are vertebrates that have feath-

ers. Feathers not only allow birds to fly but keep them warm. Feathers can have spectacular colors that function in sexual reproduction (see figure on page 85). Feathers are the defining characteristic of birds. One of the earliest birds, Archaeopteryx, which lived about 150 million years ago during the Jurassic period, had a skeleton indistinguishable from those of other theropod dinosaurs. It would have been classified as an ordinary dinosaur had it not been for impressions of feathers that were found in the rocks along with its fossilized bones. Indeed, some Archaeopteryx specimens without the feather impressions had been misclassified in this way. Since birds are one evolutionary lineage among the dinosaurs, many biologists consider

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birds 

85

Many birds have colorful feathers, such as this peacock. (Pavo cristatus)  (Duisberg Zoo)

birds to actually be dinosaurs. Once feathers had evolved, bird evolution continued rapidly. Another bird fossil from about this same period had a large breastbone, short tail, and perching feet, all of them features found in birds today. There were many bird lineages during the Jurassic and Cretaceous periods, all of which (including the one with Archaeopteryx) became extinct except one, the ancestral lineage of all modern birds.

Anatomical Features that Allow Birds to Fly Birds possess many features that enable them to fly. These features provide a strong surface for pushing against the air, enhance birds’ metabolism, and reduce birds’ weight. Feathers. Feathers emerge from the skin of all birds and form most of birds’ outer covering. They apparently evolved from reptile scales, as the early stages of development in both feathers and scales are the same. Both are made of keratin, the same protein that predominates in the skin tissue of mammals. Feathers have numerous functions:

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●● ●●

●●

They provide a very strong and light-weight surface that allows flight. They provide insulation by trapping air pockets. This is important because birds are warm blooded and have a high metabolic rate. Most birds are small and would lose significant warmth through their body surfaces were it not for feathers. They repel water, which would add to a bird’s weight during flight. The outer feathers are layered like shingles on a roof to shed water. During preening, many birds transfer oil from an oil gland to the feathers, making them even more water repellent.

Contour feathers cover the outside of an adult bird’s body. They have a central shaft. Many of the shafts grow out of the bones, leaving small indentations that can be identified in fossils. These indentations are sometimes the only evidence that a dinosaur had feathers. On either side of the shaft, vanes consist of hundreds of barbs, which branch into thousands of barblets, which are connected together by

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first entry

in addition to unidirectional air flow, birds have rapid heartbeats (up to 1,200 beats per minute in hummingbirds) that allow the blood to carry oxygen rapidly to all parts of the body. Digestion. Because they have no teeth, birds must swallow their food whole, sometimes regurgitating indigestible portions. they have crops in which to store food and gizzards, which are muscular stomachs that may use small stones and other hard objects to help grind food. the stones are called gastroliths; large, smooth gastroliths have also been found associated with the skeletons of large herbivorous dinosaurs. in birds, as in these dinosaurs, the use of gastroliths reduces the need for heavy teeth Flight feathers have a central shaft and barbs that are held together by to grind food and thus reduces hooks. Feathers are extremely strong relative to their light weight. weight. (Of course, gastroliths add to the bird’s weight.) thousands of tiny hooks. the most important fl ight Water balance. Most birds drink by dipping feathers are called primaries and grow on the ends their beaks in water and raising their heads, allowing of the wings. Bird wings provide lift because the the water to flow down their throats. Most doves, in air moves faster and therefore has a lower pressure contrast, can drink water by swallowing, as mamon the upper side. the feathers come together on mals do. Water is heavy, and birds do not carry a lot the downstroke to force the bird upward but move of it around with them. Birds eliminate nitrogenous apart on the upstroke to avoid pushing the bird wastes in the form of solid uric acid rather than urea downward. Flight feathers have a central quill with dissolved in water. the white nitrogenous wastes barbs projecting from the quill; barbules with hooks mix with dark intestinal wastes and leave the bird’s interlock the barbs (see figure). During preening, body through a single opening, called a cloaca. birds often zip disconnected barbules back together. Bones. the very large sternum (breastbone) the vanes are asymmetrical: the outer (leading) allows the attachment of large fl ight muscles. Birds vane is smaller than the inner vane, which further have partially hollow bones, which greatly reduces contributes to air movements that provide lift. Some the weight relative to the solid bones of other vertecontour feathers are modified into bristles. brates. Modern birds have no teeth, though ancient Down feathers line the trunk of a bird’s body. birds did. their beaks, similar to hardened lips, Very weak, their function is insulation. the first feathallow exploitation of different types of food: some ers to evolve may have resembled down feathers and for cracking large seeds, some for gathering small functioned as insulation rather than as flight feathers. seeds or insects. Hummingbirds have long beaks and Respiration. Birds breathe very efficiently. their tongues that allow them to obtain nectar from tubulungs are structurally different from those of all lar flowers. Modern birds do not have tail vertebrae, other living vertebrates. Most vertebrates breathe although early birds did. Modern birds have tail in and then breathe out, but in birds the air flows feathers rather than tails. in only one direction, exposing the lung tissues to Muscles. Birds have more muscle, relative to a continuous supply of fresh air. Birds do not have body weight, than almost any other group of ania diaphragm muscle; the entire body acts like belmals. about 40 percent of the body weight of a dove lows, pushing the air through the respiratory sysconsists of wing muscle. tem. alligators also have lungs in which air flows Temperature regulation. Birds produce internal in one direction. this implies that unidirectional body heat (are endothermic) and regulate their body lungs were an adaptation shared by the common temperatures (are homeothermic). their body temancestors of dinosaurs, pterosaurs, and alligators. peratures are higher than those of humans and most

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birds  other mammals. This is an important feature in providing the high levels of energy needed for flight. At rest, a bird’s metabolic rate is 10 times higher than the metabolic rate of a mammal of the same size. Small birds must produce more body heat per unit body weight than do large birds in order to maintain a constant warm body temperature. Small birds must eat 30 percent and large birds 5 percent of their body weight each day. For comparison, a 150-pound (70-kg) human would have to eat up to 45 pounds (20 kg) of food per day in order to “eat like a bird”! Some birds eat three times their body weight per day during cold seasons. Bird metabolism is so high and so expensive in terms of food energy that very small birds cannot maintain a constant body temperature all the time. Some hummingbirds, for example, allow their body temperatures to drop to about 60°F (14°C) on cool nights. Sexual reproduction and life cycle. Sexual reproduction in birds is well adapted to life in the air and on dry land. ●●

●●

The reproductive organs of birds remain reduced in size except during the breeding season, and even then in many species the females have only a left ovary. This allows a great reduction in weight during flight. Most birds do not have external reproductive organs. Some male birds, such as waterfowl, turkeys, and ostriches, have penises that remain hidden except during copulation. Birds typically achieve internal fertilization by pressing their cloacae together. Bird eggs have calcium carbonate shells with small pores that allow air to diffuse in but prevent the rapid evaporation of water. The yolk is the egg cell itself and contains many nutrients. The albumin, or “egg white,” consists mostly of protein for nourishment of the embryo. As a result, the gametes and the embryo are protected from drying.

Some humans have attempted to fly under their own power by building winglike structures. These have proven unsuccessful largely because birds, unlike humans, are very lightweight and have an enormous amount of muscle tissue. Still, a combination of lightweight materials and pedal-powered propellers has allowed some very muscular humans to fly significant distances. The distance record is 74 miles (115 km), and the speed record is about 20 miles (about 30 km) per hour for about 1 mile (about 1.5 km).

Early Birds Birds, like lizards, snakes, crocodiles, tuataras, and dinosaurs, are in the diapsid lineage, which means

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87

that their skulls have two openings on each side of the skull, in contrast to the anapsids (turtles), which have no such openings, and the synapsids (mammals and their ancestors), the earliest members of which lineage had a single opening. In the late Paleozoic era, the diapsids split into two evolutionary lineages: the lepidosaurs (lizards, snakes, tuataras, and others) and the archosaurs (crocodiles, dinosaurs, and others). There were many important lineages of archosaurs during the Triassic period, but only the crocodile and dinosaur lineages have survived. Dinosaurs evolved into many forms during the Jurassic and Cretaceous periods. Some, the theropods, were predators. Many (except for the tyrannosaurs) were small and ran rapidly on the ground, occasionally jumping into the air or gliding from tree to tree. These were the ancestors of birds. Since birds arose from a lineage of dinosaurs, modern taxonomists consider birds to be dinosaurs. The common ancestor of all bird lineages had feathers. Several lineages of primitive birds, such as Archaeopteryx, Confuciusornis, Ichthyornis, and Hesperornis, eventually became extinct. The surviving lineage diverged into the paleognath and neognath lineages (see table on page 88).

Modern Birds The following description focuses on the major lineages of birds and is not a complete list of orders. All the orders and the number of species in each are included in the table on page 88. The groupings follow the 2008 publication by Shannon J. Hackett (see Further Reading source on page 90). Paleognaths. The paleognaths are represented today by ostriches in Africa, rheas in South America, cassowaries in Papua New Guinea, emus in Australia, kiwis in New Zealand, and tinamous in South America. Two other paleognath lineages, the elephant birds of Madagascar and the moas of New Zealand, became extinct recently when humans first took up residence on the islands they inhabited. Paleognath means “old jaw,” which refers to a palate structure more similar to that of reptile lineages than are the palates of other birds. All paleognaths are or were flightless except the tinamous, which fly weakly and slowly. If the common ancestor of paleognaths was flightless, the tinamous must have regained the ability to fly. It is more likely that all these paleognath lineages independently lost the ability to fly. Flightless paleognaths still have wings but use them for things such as mating displays. Kiwi wings are very small. All paleognaths live in the Southern Hemisphere on continents that were once connected. This suggests that they evolved before the formation of ­Pangaea preceding the Mesozoic era, although fossils that old have not been found.

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first entry

Paleognaths seem to represent an evolutionary convergence with mammals, because they run and are large. They can rapidly outrun predators. Ostriches are the largest birds and weigh more than

300 pounds (130 kg). Some are almost nine feet (almost 3 m) tall. They have been observed to run at 45 miles per hour (72 km per hour) for several miles. Their eggs weigh about 3.6 pounds (1.6 kg).

Number of Species in Bird Orders* Order

Examples

Species

Casuariformes

cassowaries

2

Dinornithiformes

kiwis

3

Rheiformes

rheas

2

Tinamiformes

tinamous

47

Struthioniformes

ostrich

1

Anseriformes

ducks, geese, swans

161

Apodiformes**

swifts, hummingbirds

422

Caprimulgiformes

nighthawks

113

Charadriiformes

gulls, terns, plovers

366

Ciconiiformes

herons, storks, New World vultures

127

Coliiformes

mousebirds

6

Columbiformes

pigeons, doves

313

Coraciiformes

kingfishers

218

Cuculiformes

cuckoos

143

Falconiformes***

hawks, eagles, Old World vultures

304

Galliformes

chickens, quail, turkeys, pheasants

258

Gaviiformes

loons

3

Gruiformes

cranes

213

Musophagiformes

turacos

23

Passeriformes

perching birds

ca. 5,400

Pelecaniformes

pelicans

67

Phoenicopteriformes

flamingoes

5

Piciformes

woodpeckers

410

Podicipediformes

grebes

21

Procellariiformes

petrels, albatrosses

115

Psittaciformes

parrots

358

Sphenisciformes

penguins

17

Strigiformes

owls

17

Trogoniformes

trogons

39

Paleognaths

Neognaths

Total

ca. 11,300

*Based on Smithsonian Institution Web site and Hackett source on page 90 **Includes Trochiliformes. ***Includes Accipitriformes.

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birds  The kiwis resemble mammals exceptionally well. New Zealand has no native mammals except bats, and kiwis evolved into a mammalian mode of living. Kiwis, unlike most birds, are nocturnal and use scent to locate prey. Even their feathers resemble mammal fur. Neognaths. Neognaths include the following lineages. One group of neognaths consists of order Anseriformes (ducks, geese, swans, etc.) and the order Galliformes (fowl, quail, turkeys, pheasants, etc.). The ducks, geese, and swans are large birds with long necks and spatulalike bills and are among the most abundant and noticeable members of freshwater ecosystems. Most of them swim with webbed feet and forage by sticking their necks underwater. They are typically migratory. Some swans mate for life. Geese are important in some tundra ecosystems because they consume so much plant material and produce fertilizer. Some geese have been seen migrating over the Himalayas, the highest mountains in the world. Members of order Galliformes (fowl, quail, turkeys, and pheasants) fly slowly and near the ground, preferring to walk as they forage on seeds and insects. The most well-known fowl is the red jungle fowl Gallus gallus, which has been domesticated into the chicken. The chicken is perhaps the most energyefficient producer of animal protein, in the form of meat and eggs, and as such is extremely important to billions of poor people around the world. While 54 calories of fossil fuel is required to produce a calorie of beef, only 26 are required for a calorie of eggs, and only four for a calorie of chicken meat. Another group contains the order Apodiformes (hummingbirds and swifts). Hummingbirds live primarily off nectar, and they beat their wings up to 70 times per second to hover in front of tubular flowers into which they insert their long bills. Because they are so small, they are often unable to maintain their body temperatures at night, and they enter a brief version of hibernation. Swifts are small birds with short bodies and narrow wings that extend beyond the tail. They eat insects with their short bills and are best known for nesting in chimneys. Another group contains the order Columbiformes (doves and pigeons). Pigeons and the more slender doves have small legs, heads, and beaks. They are strong fliers. They reproduce rapidly and adapt readily to human habitats. Urban pigeons come from the wild European rock dove, Columba livia. Doves and pigeons are almost the only birds that can drink water by suction. Perhaps because of their gentle “cooing,” doves have been symbols of peace for millennia. Another group contains the orders Procellariiformes (petrels and albatrosses), Pelecaniformes

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89

(pelicans), Ciconiiformes (herons, storks, New World vultures), Spheniciformes (penguins), and Gaviiformes (loons). Most are water birds that eat fish, which they may store (as pelicans do) in their sac-like bills. Penguins cannot fly; their wings are modified as flippers. They are famous for survival in the Antarctic even during the winter. New World vultures evolved separately from the Old World vultures, which are related to hawks and eagles (see below). Like them, the New World vultures have featherless heads, which prevents an excessive buildup of decaying flesh when they stick their heads into carcasses. Another group contains the order Charadriiformes (sandpipers, plovers, and gulls). Sandpipers and plovers feed on the seashore by inserting their bills, of various lengths, into the sand. Gulls and terns live mostly on seashores and catch fish or crabs or eat carrion. They seldom travel over the open ocean. Seagulls have followed rivers and canals (especially those with slightly saline water) hundreds of miles inland. The arctic tern (Sterna paradisaea) migrates each year between the arctic and antarctic regions of the world, an annual journey of 22,000 miles (about 36,000 km). The group that has evolved furthest from the neognath common ancestor contains the following orders: Order Strigiformes (owls) are nocturnal predators. They have large wings and short tails. Their forward-facing eyes allow binocular vision. Serrations on the leading edges of their wing feathers minimize the sound they make while flying. Some owls have begun moving into suburban areas, where their rodent-controlling activity is welcome. Order Falconiformes (falcons) usually includes the Accipitriformes (hawks, eagles, and Old World vultures). They are hovering and swiftly flying predators with eyesight far more acute than that of any human. They catch their prey with extremely sharp talons. Peregrine falcons can fly at almost 200 miles per hour (320 km per hour). Old World vultures evolved separately from the New World vultures. Like them, the Old World vultures have featherless heads, which prevents an excessive buildup of decaying flesh when they stick their heads into carcasses. Most recent evidence separates the falcons, which are close relatives of perching birds, from the Accipitriformes. Order Piciformes (woodpeckers) have numerous adaptations for forming holes in the wood of dead branches: very sharp beaks, the ability to pound their beaks rapidly, and feet and stiff tail feathers that prop them firmly against the branch. They have extremely long tongues, which may be as long as their bodies. If, while pecking a hole, a woodpecker

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90 90 bogs, life in  encounters an insect burrow, it can insert its barbed tongue several inches and skewer the insect. They also return to old holes to seek insects that may have colonized them. The acorn woodpecker of California (Melanerpes formicivorus) pecks holes in oak trees, each of which is precisely the right size for storing a particular acorn. Order Passeriformes (the perching birds) is the largest and most recently evolved order of neognath birds. Almost half of bird species (by some estimates, 5,400 of 11,240) are passerines. Not only do passerines represent the greatest number of species, they often have the largest populations. The number of insects consumed by the billions of passerines in the United States is nearly incalculable, and they keep many insect populations under control that would otherwise cause massive pest outbreaks. They are small birds and specialize on many different food sources, most of them small, such as seeds and insects. Because they can produce a great diversity of vocalizations and colors, it is likely that sexual selection has played an important role in their diversification. Examples include the following families. ●● ●● ●● ●● ●● ●● ●● ●● ●● ●●

Corvidae (jays, crows) Fringillidae (finches) Hirundinidae (swallows) Icteridae (blackbirds, meadowlarks) Mimidae (mockingbirds, thrashers) Paradisaeidae (birds of paradise) Passeridae (sparrows) Troglodytidae (wrens) Turdidae (thrushes, robins) Tyrannidae (flycatchers)

Birds have sex chromosomes. Male birds have two Z chromosomes, while female birds have a Z and a W chromosome. In paleognaths, considered to be more primitive, the Z and W chromosomes are about the same size, while in neognaths the W chromosome is smaller. See also convergence; dinosaurs; reptiles; sexual selection. Further Reading Benton, Michael. “Dinosaur summer.” Chap. 4 in Gould, Stephen Jay, ed., The Book of Life: An Illustrated History of the Evolution of Life on Earth. New York: Norton, 1993. Chiappe, Luis M. “Downsized dinosaurs: The evolutionary transition to modern birds.” Evolution Education and Outreach 2 (2009): 248–256. Cornell Lab of Ornithology. “All about birds.” Available online. URL: http://www.allaboutbirds.org. Accessed August 8, 2011.

xviii+598_Biodiversity_F.indd 90

first entry Dalsgaard, Bo, et al. “Plant-hummingbird interactions in the West Indies: Floral specialisation gradients associated with environment and hummingbird size.” Oecologia 159 (2009): 757–766. Dingus, L., and T. Rowe. The Mistaken Extinction: Dinosaur Evolution and the Origin of Birds. New York: Freeman, 1997. Dyrcz, Andrzej, and Konrad Halupka. “Why does the frequency of nest parasitism by the cuckoo differ considerably between two populations of warblers living in the same habitat?” Ethology 113 (2007): 209–213. Farmer, C. G., and Kent Sanders. “Unidirectional airflow in the lungs of alligators.” Science 327 (2010): 338–340. Hackett, Shannon J., et al. “A phylogenomic study of birds reveals their evolutionary history.” Science 320 (2008): 1,763–1,768. Haroldson, Kurt J., et al. “Association of ring-necked pheasant, gray partridge, and meadowlark abundance to Conservation Reserve Program grasslands.” Journal of Wildlife Management 70 (2006): 1,276–1,284. Houston, David. Condors and Vultures. Osceola, Wis.: Voyageur Press, 2001. Mathiessen, Peter. Birds of Heaven: Travels with Cranes. New York: Farrar Straus and Giroux, 2001. Ornithological Council, National Museum of Natural History, Smithsonian Institution. “Birdnet: The Ornithological Information Source.” Available online. URL: http://www.nmnh.si.edu/BIRDNET/. Accessed August 8, 2011. Padian, Kevin and L. M. Chiappe. “The origin of birds and their flight.” Scientific American 278 (1998): 38–47. Paul, Gregory S. Dinosaurs of the Air: The Evolution and Loss of Flight in Dinosaurs and Birds. Baltimore, Md.: Johns Hopkins University Press, 2002. Reichard, Dustin G., and J. Jordan Price. “Species recognition in a vocal mimic: Repetition pattern not the only cue used by northern mockingbirds in discriminating songs of conspecifics and brown thrashers.” Wilson Journal of Ornithology 120 (2008): 717–724. Short, Lester L. The Lives of Birds: Birds of the World and Their Behavior. New York: Henry Holt, 1993. Snyder, Noel, and Helen Snyder. Raptors of North America: Natural History and Conservation. Osceola, Wis.: Voyageur Press, 2006. Sodhi, Navjot S., et al. “Avian extinctions from tropical and subtropical forests.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 323–346. Tilford, Tony. Complete Book of Hummingbirds. Holt, Mich.: Thunder Bay Press, 2009.

bogs, life in  Bogs are among the most specialized and unusual of aquatic habitats. Most bogs formed from fragments of glacier left behind at the end of the most recent ice age and are most common in regions that were recently glaciated. They

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boreal and subalpine forests  are clay-lined bowls of glacial meltwater. Because of the dense clay lining, bogs retain water from rain. Furthermore, they are ombrotrophic because they receive no mineral nutrients from rivers or streams. The water is therefore very low in nutrients. One kind of plant that thrives in these conditions is sphagnum moss, which forms rafts that float on and may entirely conceal the surface of the water. Not only is the bog nutrient-poor, the moss releases acid into it, inhibiting the growth of larger plants even further. Moreover, the mat of moss keeps the water beneath it cool. Sphagnum is also known as peat moss. The only plants that grow in bogs are those that can tolerate cool acidic water with few nutrients. Some plant species specialize on bogs and similar habitats. For example, in the Black Hills, the bog birch (Betula glandulosa) inhabits bogs, while the mountain birch (B. occidentalis) inhabits nearby streamsides. Many bog plants, such as the larch (Larix decidua) and the cotton sedge (Eriophorum vaginatum), are adapted to nutrient-depleted, wet, cool conditions and can be found in the boreal and subalpine forests or the tundra as well as in bogs. Indeed, the bog could be considered a southerly remnant of the tundra as vegetation zones shifted northward after the most recent Ice Age. Other bog plants include heath bushes of the plant family Ericaceae. Examples include cranberries and blueberries. Around the world, heath bushes (for example, the ones that dominate the heather of Scotland) tolerate acidic soils. Bog bushes may be evergreen, which is an adaptation that prevents the plants from losing the scarce mineral nutrients in their leaves. The most famous plants of the bog are the carnivorous plants, which trap and digest insects. Pitcher plants (such as Sarracenia purpurea) trap insects in pools of digestive fluid; sundews (such as Drosera rotundifolia) trap insects on sticky hairs. Why do carnivorous plants eat insects? The plants are green and make their own sugar through photosynthesis. Therefore, they do not eat insects in order to obtain food energy. Instead, they use the insects as a source of fertilizer, such as nitrates and phosphates, which are scarce in the acidic moss or soil. Animals are less abundant in bogs than in regular ponds. The acidic conditions make calcium, which is necessary for bones, unavailable. Obstruction of the surface also inhibits the diffusion of oxygen from the air into the water. Because of the acidic and low-oxygen conditions, fishes are rare in bogs. Amphibians and insects, which have access to the air, may be abundant. A fen is similar to a bog but contains open water and may receive some minerals from groundwater.

xviii+598_Biodiversity_F.indd 91

91

Ecological succession may in time fill in the fen and turn it into a bog. Decomposition is very slow in the cold, acidic waters of a bog. It may therefore hide many ancient mysteries. Layers of bog sediments preserve ancient pollen and chemicals that allow the reconstruction of past environments. Human corpses, some thousands of years old, have been found well preserved in bogs, although the hair has been bleached and the skin literally tanned like leather. Analysis of the corpses of “bog people,” particularly in Europe, has helped to reveal facts about the daily lives of people in prehistoric cultures and, in some cases, methods of execution. Therefore, bogs, besides being interesting microclimates, act as time capsules that preserve bits of the past. Bogs are also disproportionately important to the global atmosphere because their bacterial decomposition may emit large amounts of methane (and other molecules) into the atmosphere. See also boreal and subalpine forests; carnivorous plants; ice ages; tundra. Further Reading Cadillo-Quiroz, Hinsby, et al. “Diversity and community structure of archaea inhabiting the rhizoplane of two contrasting plants from an acidic bog.” Microbial Ecology 59 (2010): 757–767. Krachler, Regina, et al. “Relevance of peat-draining rivers for the riverine input of dissolved iron into the ocean.” Science of the Total Environment 408 (2010): 2,402–2,408. Simmonds, P. G., et al. “Natural chloroform emissions from the blanket peat bogs in the vicinity of Mace Head, Ireland over a 14-year period.” Atmospheric Environment 44 (2010): 1,284–1,291. Tsujino, Riyoˉ, et al. “Restoration of floating mat bog vegetation after eutrophication damages by improving water quality in a small pond.” Limnology 11 (2010): 289–297. Wright, Margaret E., and Tom A. Ranker. “Dispersal and habitat fidelity of bog and forest growth forms of Hawaiian Metrosideros (Myrtaceae).” Botanical Journal of the Linnaean Society 162 (2010): 558–571.

bony fishes  See fishes. boreal and subalpine forests  Boreal for-

ests, also called taiga, cover one-third of the forested area of Earth. Boreal comes from Greek for “northern.” These forests occur between 50° and 60° north latitudes, which is about the extent of the arctic air mass in winter and summer, respectively. Boreal forests form a broad belt of forest across North America, Scandinavia, and Siberia.

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92 92 boreal and subalpine forests  Boreal forests have short, moderately warm summers and long, cold, snowy winters. The growing season is about three months long—only 50 to 100 days are frost free. This is the principal reason that needle-leaved evergreen trees dominate the boreal forests. The summers are too short to allow trees to grow a new set of leaves each year. Therefore, none of the dominant tree species is deciduous. Furthermore, the leaves must be adapted to surviving long, snowy winters. Their needlelike shape allows them to prevent the buildup of snow, the weight of which could damage tree branches. In both of these ways, boreal forests contrast with broad-leaved deciduous forests. The trees in boreal forests also have a conical shape that allows them to shed snow in the winter. Summers can, however, be much warmer. Verkoyansk, Siberia, has recorded extremes of temperature from -90° to 90°F (about -68° to 35°C). The precipitation does not much exceed that of an arid climate, but there is so little evaporation that the region is humid. The soils in a boreal forest tend to be thin, nutrient poor, and acidic, both because the low temperatures do not allow extensive decomposition to form humus and because needle leaves tend to be acidic. The acid leaches minerals from the shallow soils, leaving them gray in color. The diversity of tree species in boreal forests is much lower than that of temperate forests; spruce (genus Picea) and fir (genus Abies) trees are abundant over large geographical areas (see table on page 93). A few deciduous trees, such as birches (genus Betula), alders (genus Alnus), and aspens (Populus tremuloides), grow in disturbed and streamside habitats of the boreal forest. Fires are common in the boreal and subalpine forests. Burned areas are quickly filled by jack pine (Pinus banksiana) and aspens. Boreal forests were found in southern Europe and southern North America during the most recent Ice Age. When the glaciers retreated, starting about 12,000 years ago, the trees of the boreal forest migrated (through seed dispersal) northward to their present locations and also to the tops of mountains, where they exist today as subalpine forests (see figure). This is why many subalpine forests of the Rocky Mountain region are dominated by trees very similar to those of the boreal forest. However, pines dominate some subalpine forests of the Rocky Mountains, especially of the Sierra Nevada of California (see table on page 93). These are not the same pine species that occur in lower-elevation montane or other temperate coniferous forests. Examples include the limber pine (Pinus garryana) and the bristlecone pines (P. longeava in the Sierras, P. aristida in the Rockies). The bristlecone pines of California grow extremely slowly in the cold, dry

xviii+598_Biodiversity_F.indd 92

first entry environment and are the oldest known trees in the world, some exceeding 4,700 years of age. Some subalpine forests also exist in the Southern Hemisphere. One example is the subalpine forests of Australia, where the snow gum (Eucalyptus pauciflora) is a dominant tree species. Boreal forests intergrade with tundra. A transitional zone that can be 60 miles (almost 100 km) in width connects the arctic tundra and the boreal forest in Canada. The boreal forest dominates the warm, south-facing, well-drained slopes in this zone. The numerous bogs in some parts of the taiga (forming a mixture known as muskeg) are tundra inclusions. The transitional zone between alpine tundra and subalpine forest is characterized by stunted subalpine trees (called krummholz) that are often short enough to be protected by snow in the winter and that may have branches only on the leeward side where winter winds have not killed them. The krummholz trees form a vaguely defined timberline. Boreal forests also intergrade with temperate forests, for example, in northern Minnesota. To a certain extent, the ecological border between tundra and boreal forest is regulated by the boreal forest itself. Boreal forest trees are dark and become warm by absorbing sunlight. This hastens

Coniferous trees grow in subalpine forests, such as these red firs (Abies magnifica) in the Sierra Nevada of California.  (Stanley A. Rice)

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boreal and subalpine forests 

93

Dominant Woody Plants and Large Mammals of Boreal   and Subalpine Forests Plant Species

Boreal Forest Canada

Subalpine Forest

Siberia

Rockies

California

x

x

Coniferous trees: Abies balsamea (balsam fir)

x

Abies lasiocarpa (subalpine fir) Abies sibirica (Siberian fir) Larix laricina (tamarack)

x x

Larix dihurica (Siberian larch)

x

Picea glauca (white spruce)

x

Picea mariana (black spruce)

x

Picea obovata (Altai spruce)

x x

Pinus contorta (lodgepole pine)

x

Pinus monticola (Western white pine)

x x

Pinus albicaulis (whitebark pine)

x

x

Pinus flexilis (limber pine)

x

x

Pinus aristata (bristlecone pine)

x

Pinus longeava (bristlecone pine)

x

Pinus sibirica (stone pine)

x

Pinus sylvestris (Scots pine)

x

Deciduous trees Betula papyrifera (paper birch)

x

x

Betula platyphylla (white birch)

x

Populus suaveolens (Siberian poplar)

x

Populus tremuloides (quaking aspen)

x

x

x

x

x

Shrubs and wildflowers Arctostaphylos uva-ursi (bearberry)

x

x

Cornus canadensis (bunchberry)

x

x

Cornus sericea (red osier dogwood)

x

x

x

Linnaea borealis (twinflower)

x

x

x

x

Alces alces (moose)

x

x

x

Cervus elaphus (elk)

x

x

x

x

Lynx canadensis (American lynx)

x

x

x

Gulo gulo (wolverine)

x

Lepus americanus (snowshoe hare)

x

x

x

x

x

Large mammals

Lynx lynx (Siberian lynx)

x

Rangifer tarandus (caribou, reindeer)

x

Ursus americanus (black bear)

x

Ursus arctos (brown bear)

x

xviii+598_Biodiversity_F.indd 93

x

x x

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94 94 brown algae

first entry

the melting of snow in the spring and creates warmer conditions in which the boreal species can grow. Boreal and subalpine forests are experiencing threats from human activity. Logging is very common in boreal forests because of the abundant softwood (coniferous) trees with little undergrowth. Logging in boreal forests has become a controversial issue, as many ecologists believe these forests are subject to destruction if well-planned management is not practiced. Global warming also threatens boreal and subalpine forests. Since boreal forests have low species diversity, they are subject to outbreaks of insect and other pests. Such outbreaks have been rare because of the short growing season. Global warming has produced longer, warmer summers that have allowed insect outbreaks to kill trees in large areas of Alaska. Subalpine forests can survive only on cold mountaintops; if mountaintops become even slightly warmer as a consequence of global warming, montane and deciduous forests may grow all the way to the summits, resulting in the elimination of the subalpine forests. Acid rain has weakened the remnant subalpine forest of Fraser firs (Abies fraseri) in the highest Appalachians and allowed them to fall victim to the woolly adelgid bug.

Grundale, Michael J., et al. “Vascular plant removal effects on biological N fixation vary across a boreal forest island gradient.” Ecology 91 (2010): 1,704–1,714. Hoffman, Ary A., et al. “Phenological changes in six Australian subalpine plants in response to experimental warming and year-to-year variation.” Journal of Ecology 98 (2010): 927–937. Josefsson, Torbjörn, et al. “Linking forest history and conservation efforts: Long-term impact of low-intensity timber harvest on forest structure and wood-inhabiting fungi in northern Sweden.” Biological Conservation 143 (2010): 1,803–1,811. Lynch, Wayne. Life in the Boreal Forest. Markham, Ont.: Fitzhenry & Whiteside, 2006. Rice, Stanley A. “Plants create habitats.” Ch. 8 in Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Runesson, Ulf T. “Boreal forests of the world.” Available online. URL: http://www.borealforest.org/world.htm. Accessed May 4, 2009. Tremblay, Junior A., et al. “Foraging ecology of blackbacked woodpeckers (Picoides arcticus) in unburned eastern boreal forest stands.” Canadian Journal of Forest Research 40 (2010): 991–999.

Further Reading

brown algae  (Phaeophyta)  See protists.

Allison, Steven D., et al. “Nitrogen alters carbon dynamics during early succession in boreal forest.” Soil Biology and Biochemistry 42 (2010): 1,157–1,164.

Burgess Shale  See Cambrian explosion.

xviii+598_Biodiversity_F.indd 94

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C Cambrian  explosion  the cambrian explosion was the fi rst major eruption of biodiversity in earth history. the cambrian period began about 540 million years ago. life had existed for almost 3 billion years before it. the fundamental components of life had evolved before the cambrian period: metabolism, prokaryotic cells, eukaryotic cells, and multicellularity. Protists, including seaweeds, existed before the cambrian. Fossilized animal embryos and burrows indicate the existence of at least simple animal life before the cambrian, although recent evidence suggests that the burrows may have been produced by a giant protist similar to the modern genus Gromia. immediately before the cambrian period, simple organisms called ediacarans dominate fossil deposits worldwide. However, at the beginning of the cambrian period, a rapid diversification of complex animals, particularly animals with hard skeletons, occurred in the oceans of the world. Because much of this evolution occurred right at the beginning of the cambrian period, it has been called the cambrian explosion. the paleontologist andrew Knoll wrote that the cambrian explosion looked like a “brief moment . . . when all things were possible in animal evolution.” the appearance of new animal forms was rapid, but not sudden: it occurred over a period of about 5 million years. Some scientists explain the cambrian explosion as the appearance of animals that had previously existed but had not been fossilized. according to this view, complex animals without hard parts had previously existed, although complex animals with hard skeletons had not. Hard skeletons are much more readily preserved in the fossil record. However, organisms without hard parts have often been

preserved in the fossil record, including the Precambrian ediacaran organisms and animal embryos mentioned previously. the cambrian explosion, then, must be explained as the rapid evolution of new animals, not just the evolution of hard skeletons. Some observers have classified ediacaran organisms as relatives of modern animal groups such as cnidarians, but even if this is true, the cambrian explosion represents spectacular diversification within those invertebrate groups as well as the origin of new animal groups such as the arthropods. a number of worldwide environmental changes occurred in the late Precambrian that were necessary for the cambrian explosion, as follows. ●



Oxygen gas accumulated in the atmosphere from the photosynthesis of bacteria and eukaryotes. Metabolism that uses oxygen is essential for complex animals. therefore, the explosive evolution of animals could not have occurred before the atmosphere and oceans contained abundant oxygen. Oxygen gas accumulated in the atmosphere and then in the oceans long before the cambrian period. For example, the Great Oxidation event of 2.4 billion years ago may have produced enough oxygen to fi lter out most of the ultraviolet radiation from the Sun. nevertheless, modern levels of atmospheric oxygen, sufficient for metabolism of large animals, may not have been reached until just before the beginning of the cambrian period. at least three major worldwide glaciations occurred during the Precambrian. the most recent of them may not have ended until

95

xviii+598_Biodiversity_F.indd 95

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96 96 Cambrian period, biodiversity in  about 600 million years ago. An explosive evolution of animals was unlikely to occur under such cold conditions. The melting of the ice also made more mineral nutrients available to the seaweeds and microscopic protists that were the basis of the marine food chain. However, there was a 60-million-year delay before the Cambrian explosion. Late Precambrian conditions were certainly suitable for the Ediacarans; why not complex animals? The leading explanation for the Cambrian explosion takes its cue from the rapid appearance of animals with hard parts. This explanation suggests that the Cambrian explosion began with the evolution of predation. The first predators were animals with a feeding apparatus that allowed them to chew their food. Previously, large organisms such as the Ediacarans were defenseless but safe. Now, any soft-bodied animal was helpless before the predators. The Cambrian explosion occurred when animals began to evolve different kinds of defenses as predators or against predators, such as the following. ●●

●●

●●

Natural selection favored many different structures that permitted predators to search for, catch, and chew their prey. Some evolved hard external skeletons. In many cases, this required the evolution of new body configurations. For example, the bivalve body form (as in mussels and oysters) could not function without hard shells. Hard shell defenses also evolved in a wide variety of forms. Even single-celled photosynthetic eukaryotes evolved hard and complex external coverings. Some prey, then as now, had soft bodies but hid from predators by burrowing into the mud. The complexity and depth of animal burrows increased rapidly during the Cambrian explosion.

As a result of these processes, the Cambrian world was filled with diverse and complex animals, as exemplified by fossil deposits such as the Burgess Shale in Canada and others. Animals with internal skeletons did not evolve until the latter part of the Cambrian period. See also Cambrian period, biodiversity in. Further Reading Budd, Graham E. and Sören Jensen. “A critical reappraisal of the fossil record of the bilaterian phyla.” Biological Reviews 75 (2000): 253–295.

xviii+598_Biodiversity_F.indd 96

first entry Conway Morris, Simon. The Crucible of Creation: The Burgess Shale and the Rise of Animals. New York: Oxford University Press, 1998. Knoll, Andrew H. Life on a Young Planet: The First Three Billion Years of Evolution on Earth. Princeton, N.J.: Princeton University Press, 2003. Lane, Nick. Oxygen: The Molecule that Made the World. New York: Oxford University Press, 2002. Rokas, Antonis, Dirk Krüger, and Sean B. Carroll. “Animal evolution and the molecular signature of radiation compressed in time.” Science 310 (2005): 1,933–1,938.

Cambrian period, biodiversity in  The

Cambrian period (540 to 510 million years ago) was the first period of the Phanerozoic eon and the Paleozoic era. During the previous eons, major evolutionary innovations had occurred, such as the origins of prokaryotic cells, of eukaryotic cells, and of multicellular organisms. At the beginning of the Cambrian period, complex animal forms rapidly evolved, a burst of biodiversity commonly known as the Cambrian explosion. This is why the Cambrian period is considered the beginning of the Phanerozoic eon, or the eon of “visible life.” An average of about 300 families of marine organisms existed during the Cambrian, compared to 1,000 marine families (and 2,200 total families) today. Climate. All Cambrian life lived underwater, with the possible exception of lichens on continental rocks. Temperatures are much more stable underwater than on land. Atmospheric oxygen levels were much lower and carbon dioxide levels much higher than today. Global temperatures were also higher than today (see table on page 97). Continents. Because there were no continents located near the poles, ocean currents were able to circulate freely. As a result, there was no significant formation of ice sheets. Sea level was more than 180 feet (about 60 m) higher than today. Marine life. Most and perhaps all of the major animal phyla evolved before or during the Cambrian period (see figure on page 97). Fossil deposits such as the Burgess Shale in Canada, Chengjiang in China, and Sirius Passet in Greenland preserve fossils of many animal phyla, including those that had no hard parts. These deposits reveal a somewhat uniform worldwide assemblage of animals that persisted for about 30 million years. The animals within these phyla were different from the ones within those phyla today. For example, the arthropods were represented by trilobites and by animals such as Anomalocaris, a large predator with a round mouth, both of which have long been extinct. The first vertebrates, jawless fishes, evolved during the Cambrian period. The 530-million-year-old Chengjiang deposit in China

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Cambrian period, biodiversity in

97

contains two jawless vertebrate fossils, Myllokunmingia and Haikouichthys, considered to be the fi rst fishes. conodont animals existed as far back as 540 million years ago. these fishlike animals had long bodies, large eyes, and conelike teeth but no jaws. Single-celled and multicellular photosynthetic protists (such as seaweeds) were the basis of the marine food chain. Continental life. there is no clear evidence that either animals or plants existed on land or in freshwater during the cambrian period. the continents consisted of bare rock, sand, silt, and clay. Moist rocks may have supported green algae and lichens. Extinctions. although the cambrian period is not considered a time of mass extinction, the edia-

multiCellular biodiversity  in the Cambrian period Conditions Atmospheric oxygen

63% of modern level

Atmospheric carbon dioxide

13 times modern level

Global temperature

9°F (7°C) higher than today

Sea level

190 feet (60 m) higher than today

Approximate Number of Families* Continental

0

Marine

100

Total

300

Examples of Marine Animals Anomalocaris canadensis

arthropod

Diagonella hinderi

chordate

Fallotapsis longa

trilobite arthropod

Hallucigenia sparsa

onychophoran

Myllokunmingia fengjiaoa

jawless “fish”

Nectocaris pteryx

mollusk?

Opabinia regalis

lobopod?

Palaecmaea typica

cnidarian

Phragmochaeta canicularis

annelid

Pikaia graciliens

chordate

Wiwaxia corrugata

mollusk?**

*Based on Benton **Identity uncertain

xviii+598_Biodiversity_F.indd 97

Three of the most unusual animals of the Cambrian period were (a) Anomalocaris, a predator with a round mouth and grasping appendages; (b) Hallucigenia, protected by a double row of spikes; and (c) Opabinia, with five eyes and an extended grasping mouthpart.

caran organisms and other Precambrian life forms apparently became extinct during this period. there were far fewer species in the cambrian period than in the following Ordovician period, but, on a percentage basis, cambrian extinctions were considerable. See also arthropods; cambrian explosion; fishes. Further reading Benton, Michael. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Briggs, Derek e. G., et al. The Fossils of the Burgess Shale. Washington, D.c.: Smithsonian Books, 1994. conway Morris, Simon. The Crucible of Creation: The Burgess Shale and the Rise of Animals. Oxford: Oxford University Press, 2000. Gould, Stephen Jay. Wonderful Life: The Burgess Shale and the Nature of History. new york: norton, 1989. Hou, Xian-Guang, et al. The Cambrian Fossils of Chengjiang, China: The Flowering of Early Animal Life. new york: Wiley-Blackwell, 2004.

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98 98 camouflage and mimicry 

camouflage and mimicry  Mimicry occurs

when natural selection favors characteristics that make organisms (the mimics) resemble other organisms or objects (the models). By resembling models, the mimics are often able to avoid being eaten by predators or are able to obtain benefits at the expense of other species. Mimicry does not have to be perfect in order to be highly effective. All that is necessary is that other species be unable to distinguish the mimic from the model at least part of the time. Most populations have a range of characteristics that affect their appearance. If some members of the population even slightly resemble a model, they may benefit from this resemblance. For example, an insect may not resemble a leaf very closely, but closely enough that a predator with imperfect eyesight or in the semidarkness of shade or dusk may overlook it. Male animals may rush to mate with artificial objects that (to human eyes) hardly resemble the female of the species at all. This likewise demonstrates that imperfect mimicry, in this case of a mimic that resembles a female animal, can be favored by natural selection. In examples of nest parasitism, the mimics may look very different from the hosts whose nests they parasitize, but the hosts are not using vision as their way of identifying which animals should be allowed into the nest. In many cases, generation by generation, the incipient mimics are selected to more and more closely resemble the model. After a long period of evolution, the resemblance can sometimes be very striking. Since mimicry involves the evolution of characteristics in the mimic and the evolution of the ability of other animal species to recognize them, it is an example of coevolution. Types of mimicry include the following. Camouflage mimicry. Camouflage is widespread among animals. Many mammals, for example, have dappled coats that help them blend in with vegetation and shade, and many lizards are colored like rocks. Many insects have a striking resemblance to sticks or leaves. The mantid Acanthodis curvidens closely resembles a stick, while the mantid Phyllium giganteum and the katydid Mimetica viridifolia closely resemble leaves. The scientific names define these insects by their ability to mimic leaves. The tropical leaf litter frog Rhinella margaritifera comes in several color patterns, all of which resemble decaying leaves. Most animals are countershaded, which means that their backs are darker than their bellies. Some caterpillars have a shape and coloration that resembles bird droppings. Some examples of camouflage, such as zebra stripes, appear quite imperfect in the middle of the day but make the zebras blend well into the grass at dusk, when their predators are hunting them.

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first entry Some animals mimic the appearance of their predators to escape notice. One example is the nymph of the Texas bow-legged bug Hyalymenus tarsatus, which closely resembles ants and feeds alongside them on plants. Camouflage does not always involve the mimic’s own coloration. Some caterpillars eat leaves by removing tissue from the outer edges while maintaining the overall shape of the leaf. Predators may seek caterpillars by looking for patches of missing leaf material and may be less likely to notice leaves that are smaller but otherwise almost normal in appearance. Camouflage mimicry is less common but not unknown among plants. Living stones, succulent plants of the genus Lithops in the deserts of southern Africa, resemble green rocks and thus avoid being eaten. The young leaves of many plant species, while still tender and not yet toxic, are often reddish or brownish in color, which may make herbivores mistake them for dead leaves. Even fungi can use camouflage mimicry, such as a fungus that lives in termite mounds. Normally, termites remove fungal hyphae and reproductive structures, but this fungus has reproductive structures that resemble termite eggs in size, shape, and texture. Distraction mimicry. The bug Anisocelis flavolineata has a large thorax, which a predator can easily see, but it also has large red flaps on two of its legs, which it holds away from its body. When the bug sits on a flower, the three red zones resemble flower parts. If the predator recognizes the prey, it may still grab at one of the leg flaps and eat just the leg, leaving behind an injured but surviving bug. Another example is the sea krait Laticauda colubrine (a type of sea snake), in which the tail is colored like the head. When the snake curls around, a predator may think that there are two venomous snakes rather than just one. Some insects have markings on them that look like large eyes, which may startle predators (see figure on page 99). Sexual and prey mimicry. There are numerous examples of organisms that mimic the sexual characteristics of another species in order to take advantage of them. Consider the example of the blister beetle Meloe fransiscanus, which parasitizes the nests of Habropoda pallida solitary bees. The beetle larvae gather together into clusters on the stems of plants; these clusters not only look a bit like female Habropoda bees, but the larvae produce a chemical that resembles the bee sex pheromone. A male bee attempts to mate with the cluster of beetle larvae, and they cling to him. He flies away with the cluster, and when he finds a female bee and attempts to

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camouflage and mimicry 

This click beetle (family Elateridae) has large spots on its thorax, which may deceive predators into thinking it is a large animal with large eyes.  (Stanley A. Rice)

mate again, the beetle larvae jump onto the female. Eventually, the female bee carries the beetle larvae to the nest. Certain flowers resemble, to some wasps and flies, either their food or the female of their species. Male wasps pollinate some species of orchids by attempting to mate with the flowers. The appearance of the orchids is close enough to that of female wasps that the males are tricked, and the orchids produce a scent that, to the male wasps, is indistinguishable from that of a female wasp. The green spider orchid Chiloglottis trapeziformis produces a chemical, 2-ethyl-5-propylcyclohexan-1,3-dione, that is the same as the sex hormone produced by the female Neozeleboria cyroptoides wasp. In many other cases, female flies lay eggs in flowers (especially arums and carrion flowers) that look and smell like rotting meat (see table on page 100). Even more numerous are examples of plant species (once again, many of them orchids) whose flowers do not produce their own nectar but that closely resemble the flowers of plant species that do produce nectar. The pollinator visits the nectarless flower to pol-

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99

linate it, discovering only too late that no nectar is available. Angler fishes are so called because they have extensions from their heads that resemble worms; they eat other fishes that approach to investigate the worm. In a similar fashion, the tongue of the alligator snapping turtle resembles a moving worm, and the turtle eats fishes attracted by it. Some freshwater mussels attract fishes with colored tissues that look like prey; when the fishes approach, the mussels spurt out larvae, which adhere to the fishes. The mollusks use the fishes as vehicles to transport their eggs back upstream. Some predators imitate their prey in order to attract them. The bolas spider produces sex hormones of female moths, thus attracting male moths. One kind of firefly beetle produces the light signals of the females of another kind of firefly beetle, which is its prey. A kind of katydid imitates the wingflick sound of female cicadas, thus attracting male cicadas. Mullerian mimicry. Named after the 19th-century German zoologist Fritz Müller, this form of mimicry occurs when poisonous prey species evolve to resemble one another. The entire set of species is both mimic and model. They converge upon a set of characteristics such as warning coloration that allows the predator to recognize them as poisonous. Black alternating with white, red, yellow, and/or orange are widespread warning colorations among animals, such as bees, wasps, and snakes. Batesian mimicry. Named after the 19th-century British naturalist Henry Walter Bates, who first observed this phenomenon in the Amazon rain forest, this form of mimicry occurs when nonpoisonous prey (mimics) evolve a resemblance to poisonous animals (models). The mimic therefore benefits from the protection afforded by the poisonous models without themselves having to expend resources to make themselves poisonous. Examples include stingless flies that resemble bees and wasps and the viceroy butterfly that resembles the poisonous monarch butterfly. If the mimic becomes too common relative to the model, the system becomes unstable because when the predators occasionally eat the mimic, they do not suffer the consequences that originally selected for the ability to recognize the model (see table on page 100). Social mimicry. In this kind of mimicry, also called social parasitism, the parasites mimic the social signals of the hosts. In turn, the hosts take care of them. Cowbirds and cuckoos are notorious for laying their eggs in the nests of other bird species. Baby cowbirds hatch sooner and grow faster and larger than the host species’ own babies and begin pushing the host species’ babies out of the nest, but

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100 camouflage and mimicry  100

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Examples of Mimicry Mimic

Model

Pollination mimicry Bee orchid (Ophrys apifera)

Female Eucera bee

Hammer orchid (Drakaea glyptodon)

Female Zapilothynnus trilobatus wasp

Orchid (Cryptostylis ovata)

Female Lissopimpla excelsa wasp

Spider orchid (Chiloglottis trapeziformis)

Female Neozeleboria cryptoides wasp

Orchid (Cyanicula gemmata)

Other orchids, which provide nectar

Predator mimicry Bolas spiders

Moths

Firefly (Photurus)

Photinus firefly

Katydid (Chlorobalius)

Cicadas

Batesian mimicry Kingsnake (Lampropeltis Micrurus fulvius coral snake triangulum) Bombyliid bee flies

Apid bees

Viceroy butterfly (Limenitis archippus)

Danaus plexippus monarch butterfly

Social mimicry Cowbird (Molothrus ater) Many nesting bird species Cuckoo (Cuculis canoris) Many nesting bird species Caterpillar (Maculinea rebeli)

Myrmica schencki ant

the parents do not seem to notice. The parents use the location of the baby bird as the sole indicator of its identity. The common cuckoo, as a species, parasitizes the nests of many nesting bird species, but each female specializes on just one species of host, the eggs of which most closely resemble those she lays. There are more than 10,000 species of insects that live in ant nests. Not only do the ants not kill them, they also feed them, often mistaking them for a queen of their own species. Usually, the parasites (mimics) produce a chemical that is indistinguishable from that produced by ant queens. In one

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case, the parasitic caterpillar (and later the pupa) produces a sound that the worker ants cannot distinguish from the sound produced by their queens (see table). In some cases, a parasite causes one of its hosts to undergo changes that make it resemble the prey of another of its hosts. For example, some parasitic worms live in snails and cause the snails to develop brightly colored structures and to crawl onto the tip of a branch or a leaf. This makes the snail obvious to predatory birds—the next of the worms’ hosts. There are other parasites that cause ant abdomens to swell and become red to imitate berries. Once again, birds, which eat the berrylike abdomens, are the next of the worms’ hosts. Mimicry provides numerous excellent examples of natural selection and coevolution. Batesian mimicry formed an important piece of evidence that Charles Darwin cited in his original presentation of evolutionary theory. Mimicry, like all other forms of coevolution, has stimulated the evolution of many new species. See also coevolution; natural selection; parasitism. Further Reading Angier, Natalie, and Jennifer S. Holland. “The art of deception.” National Geographic, August 2009, 70–87. Barbero, Francesca, et al. “Queen ants make distinctive sounds that are mimicked by a butterfly social parasite.” Science 323 (2009): 782–785. Kaiser, Roman. “Plants and fungi use scents to mimic each other.” Science 311 (2006): 806–807. Kronfrost, M. R., and Lawrence E. Gilbert. “The population genetics of mimetic diversity in Heliconius butterflies.” Proceedings of the Royal Society of London B 275 (2008): 493–500. Mallet, J. “Causes and consequences of a lack of coevolution in Müllerian mimicry.” Evolutionary Ecology 13 (2001): 777–806. ———, and M. Joron. “Evolution of diversity in warning color and mimicry: Polymorphisms, shifting balance, and speciation.” Annual Review of Ecology and Systematics 30 (1999): 201–233. Moksnes, A., and E. Roskraft. “Egg-morphs and host preference in the common cuckoo (Cuculus canorus): An analysis of cuckoo and host eggs from European museums and collections. Journal of Zoology 236 (1995): 625–648. Peakall, Rod. “Pollination by sexual deception in Australian terrestrial orchids.” Available online. URL: http:// www.anu.edu.au/BoZo/orchid_pollination/. Accessed May 11, 2011. Randall, J. E. “A review of mimicry in marine fishes.” Zoological Studies 44 (2005): 299–328.

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carbon cycle  101 Ruxton, Graeme D., Thomas N. Sherratt, and Michael P. Speed. Avoiding Attack: The Evolutionary Ecology of Crypsis, Warning Signals and Mimicry. New York: Oxford University Press, 2005. Saul-Gershenz, Leslie S., and Jocelyn G. Millar. “Phoretic nest parasites use sexual deception to obtain transport to their host’s nest.” Proceedings of the National Academy of Sciences USA 103 (2006): 14,039–14,044. Schiestl, Florian P., et al. “The chemistry of sexual deception in an orchid-wasp pollination system.” Science 302 (2003): 437–438. Soler, M., et al. “Magpie host manipulation by great spotted cuckoos: Evidence for an avian mafia?” Evolution 49 (1995): 770–775.

carbon cycle  The carbon cycle is the movement of carbon atoms from the atmosphere, through the crust of Earth and the food web, and back into the atmosphere. All the large molecules of which organisms consist are built from chains of carbon atoms. Nearly all of these molecules contain oxygen atoms, and many contain nitrogen atoms as well. When photosynthesis removes carbon dioxide (CO2) from the atmosphere, its oxygen atoms as well as its carbon atoms end up in carbohydrates and enter the food web. Carbon cycle concepts therefore apply to oxygen as well. The nitrogen cycle, described in a separate entry, differs from the carbon cycle at some points. The carbon cycle is of immense interest today not only because life is based on it but because the greenhouse effect has caused certain parts of the carbon cycle to change in a way that is not beneficial to humans and to the Earth as humans have come to depend upon it. Human activities, such as transportation and industry, have released tremendous amounts of CO2 into the atmosphere. Other human activities, such as deforestation, have reduced the ability of natural ecosystems to remove CO2 from the atmosphere. Agriculture has done both of these things by replacing forests and grasslands, which remove much CO2 from the air, with farmland, which does not remove as much. Indeed, farmland may release more CO2 into the atmosphere than it removes, because exposure of the soil to warmer conditions has stimulated the decomposition of humus that was previously stored in the soil, and soil erosion has removed much of the carbon-rich topsoil. As with all biogeochemical cycles, carbon follows long-term and short-term paths. The long-term paths occur on the scale of millions of years, while the short-term paths occur on the scale of tens to

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thousands of years. Therefore, only the short-term cycles are likely to be of any use in helping humans bring the greenhouse effect under control.

Short-Term Carbon Cycle The short-term carbon cycle is powered by photosynthesis. Plants and other photosynthetic organisms (some protists and bacteria) have chlorophyll and associated molecules, which absorb sunlight energy and deliver it into energy and electron carrier molecules. Photosynthetic organisms absorb CO2 from the atmosphere and convert it into carbohydrates such as sugar, using the energy and electrons from the carrier molecules. In this way, photosynthesis creates food molecules and removes CO2 from the air. Not all of this living matter enters the food chain right away. At any given time, about 4 percent of the carbon that is removed from the air by photosynthesis is stored up—about a third of this in vegetation and about two-thirds in the soil. Most of the living matter travels through the food web via herbivores and carnivores. Plants and animals respire. Respiration puts CO2 back into the atmosphere. When plants and animals die, decomposers consume their food molecules; the respiration of decomposers also puts CO2 back into the atmosphere. Other biological processes also put carbon back into the atmosphere. Anaerobic decomposers in wetlands release methane (CH4) into the atmosphere, where it quickly reacts with oxygen and becomes CO2 . Before this happens, methane is an even more potent greenhouse gas than CO2 . In addition, many plant leaves release isoprene compounds into the air. These compounds help to stabilize their photosynthesis under hot, dry conditions. These volatile molecules react with hydroxyl radicals in the atmosphere and form haze, which is eventually rinsed from the atmosphere by rain. Most ocean absorption of CO2 occurs as a result of photosynthesis, but some occurs because the water itself absorbs CO2 , converting it to carbonic acid. The excess carbonic acid has caused a measurable worldwide increase in ocean acidity.

Long-Term Carbon Cycle Both on land and in the oceans, some of the carbon from the food web enters long-term storage, in ways such as the following. ●●

●●

Soil decomposers do not return all of the carbon to the atmosphere; some accumulates as humus in soil. In the oceans, bodies of many dead organisms accumulate on the sea floor. Their calcium

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102 carbon cycle  102

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Sinks and Sources of Carbon   on Earth (Gigatons of CO2 Equivalent per Year) Sinks (removing CO2 from atmosphere) Land processes

59.3

Ocean processes

92.2

Total

151.5

Sources (putting CO2 into atmosphere) Land processes

55.5

Ocean processes

90.5

Fossil fuels*

6.4

Changes in vegetation

1.2

Total

Net Release of CO2 into Atmosphere

153.6

2.1

*Includes all industrial processes Note: Adapted from Normile

●●

●●

carbonate (limestone) shells may accumulate over millions of years to form limestone. In addition, at certain times in the past, the bodies of dead organisms have accumulated. Organic molecules from forests and to a certain extent peat bogs have accumulated and been trapped in geological deposits. After being subjected to high temperature and pressure by the rocks above and below them, these deposits have become coal. Shallow sea deposits, primarily of microbes, have been similarly transformed into oil. Much ancient organic matter has also been stored as natural gas, which consists mostly of methane. In many continental shelves, methane molecules are frozen with water in the form of methane hydrates or clathrates. The methane does not become a gas because of the pressure of ocean waters above the continental shelves. Occasionally, however, methane “burps” have occurred and released methane into the atmosphere. No large methane releases are known to have occurred during human history.

In these ways, ecosystems provide “biological carbon pumps” that transfer carbon from short-term to long-term organic storage.

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In addition, the silicate rocks of Earth’s crust remove CO2 from the air. CO2 reacts with calcium silicate (CaSiO3) to produce limestone (CaCO3) and quartz (SiO2). This reaction occurs more rapidly under conditions of high soil erosion. In the past, during times of severe greenhouse effect on Earth (such as the Permian extinction), there was much soil erosion, which allowed this reaction to remove some of the CO2 from the air. Limestone formation is also stimulated by the acids produced by decomposers. Therefore, vegetation cover enhances the rate of geological CO2 removal from the atmosphere. Limestone deposits can hence have either a biological or a geological origin, and both of these processes remove CO2 from the atmosphere. Over both long and short terms, biological and geological processes have favored slightly more CO2 removal from the atmosphere (carbon sinks) than CO2 release into the atmosphere (carbon sources). Natural processes in the land and oceans remove about 151.5 gigatons of carbon from the atmosphere each year (see table). Natural processes in the land and oceans release about 146 gigatons of carbon per year, with the result that natural processes remove about 5.5 gigatons of carbon per year. (A gigaton is a billion metric tons, which are roughly the same as English tons. In order to allow comparisons between CO2 and organic carbon, these calculations are done in carbon dioxide equivalents, rather than using just the weight of the carbon atom.) Occasional major perturbations of the long-term carbon cycle have occurred during the history of Earth, for example the following. ●●

●●

●●

The Permian extinction, mentioned previously, brought the Paleozoic era to a close about 251 million years ago. Volcanic eruptions released much CO2 into the air, and acid rain killed much of the vegetation, the decomposition of which released even more CO2 into the air. An asteroid hit Earth during the Cretaceous extinction, about 65 million years ago, bringing the Mesozoic era to a close. Massive decomposition of vegetation released much CO2 into the atmosphere at that time. About 55 million years ago, between the Paleocene and Eocene epochs of the Cenozoic era, a period of global warming (the “Paleocene-Eocene Thermal Maximum”) lasted about 100,000 years. It may have been caused by a massive emergence of methane from continental shelf clathrates (even though the Republican congressman

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Carboniferous period, biodiversity in  103 Dana Rohrabacher speculated in 2007 that it may have been due to dinosaur flatulence). Methane releases may have occurred in the Permian and Cretaceous extinctions as well.

Human Effects on the Carbon Cycle The most important human effect on the carbon cycle is the release of CO2 from the burning of fossil fuels for industry and transportation. This CO2 , together with CO2 produced by other industrial processes, releases about 6.4 gigatons of CO2 into the atmosphere per year. In addition, the destruction of natural habitats causes the release of another 1.2 gigatons of CO2 per year. The total, 7.6 gigatons of CO2 , released by human activity exceeds the 5.5 gigatons per year that natural processes absorb by 2.1 gigatons. This additional 2.1 gigatons of CO2 per year is what has caused atmospheric CO2 levels to increase by about one-third since the beginning of the Industrial Revolution (as well as widespread deforestation and land degradation) and is causing atmospheric CO2 to accumulate by just less than 2 parts per million (ppm) each year. The resulting greenhouse effect, if left unabated, will not create so much heat that humans cannot tolerate it, but it will greatly disrupt human economic and social activities. Tree plantations cannot remove CO2 from the air as effectively as natural forests, nor can croplands do so as effectively as can natural grasslands. Natural forests and grasslands have many plant species, each of which removes CO2 from the air in a different way (up in the canopy or down in the shade, for example) and at different times of year, while plantations and croplands each have only one way of removing CO2 from the atmosphere. Loss of plant biodiversity can even slow down the decomposition of leaf litter. Therefore, one of the most important reasons humans need to protect biodiversity is that it is essential to the proper functioning of the carbon cycle. See also biogeochemical cycles; Cretaceous extinction; greenhouse effect; nitrogen cycle; Permian extinction. Further Reading Bonan, Gordon B. “Forests and climate change: Forcings, feedbacks, and the climate benefits of forests.” Science 320 (2008): 1,444–1,449. Field, Christopher B., et al. “Primary production of the biosphere: Integrating terrestrial and oceanic components.” Science 281 (1998): 237–240. Hättenschwiler, Stephan, et al. “Biodiversity and litter decomposition in terrestrial ecosystems.” Annual

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Review of Ecology, Evolution, and Systematics 36 (2005): 191–218. Imhoff, M. L., et al. “Global patterns in human consumption of net primary production.” Nature 429 (2004): 870–873. Normile, Dennis. “Round and round: A guide to the carbon cycle.” Science 325 (2009): 1,642–1,643. Vitousek, Peter M., et al. “Human appropriation of the products of photosynthesis.” BioScience 36 (1986): 368–373.

Carboniferous period, biodiversity in 

The Carboniferous period (360 to 290 million years ago) was the fifth period of the Paleozoic era, following the Devonian period. In North America, the earlier Mississippian time, with extensive marine limestone deposits, is distinguished from the later Pennsylvanian time, with extensive coal deposits derived from terrestrial forests, within the Carboniferous period. Climate. In land that is now in the northern continents, climatic conditions were very warm and wet with shallow lakes and seas. These conditions were perfect for the growth of extensive swamps, from which coal deposits formed. This is why most of the coal and oil deposits are found today in the Northern Hemisphere. Much of the land that is now in the southern continents had cold polar conditions. Glaciations on the large southern continent caused intermittent reductions in sea level during the Carboniferous period. Some researchers have suggested that the atmosphere contained up to 35 percent oxygen gas, in contrast to today’s 21 percent (see table on page 104). This would have resulted from the extensive growth of plants, which produced oxygen and which accumulated into thick deposits of peat (later to become coal) rather than decomposing. The high concentration of oxygen would explain how some animals, particularly flying insects, could grow so large during this period: The abundant oxygen would have penetrated their breathing tubes, and the denser atmosphere would have supported their flight. Such high levels of oxygen would also have promoted spontaneous combustion, especially under dry conditions. During the Carboniferous period, almost all organisms lived in wet conditions. Despite this, many of the plants showed evidence of fire damage. Continents. The land that is today the northern continents (such as Europe and North America) formed the continent of Laurasia, which was near the equator, which created warm climates. The land that is today the southern continents (such as Africa and South America) formed the continent of

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104 Carboniferous period, biodiversity in  104

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Multicellular Biodiversity in the Carboniferous Period Conditions Atmospheric oxygen

63% above modern level

Atmospheric carbon dioxide

2.3 times modern level

Global temperature

same as today

Sea level

260 feet (80 m) higher than today

Approximate Number of Families* Continental

200

Marine

450

Total

650

Examples of Marine Animals Arcaheocidaris sp.

crinoid echinoderm

Breviphillipsida sampsoni

trilobite

Caridosuctor sp.

lobe-finned fish

Conularia quadrisulcata

cnidarian

Euomphalus sp.

gastropod mollusk

Euproops rotundatus

horseshoe crab

Gigantoproductus giganteus

brachiopod

Haplolepis sp.

bony fish

Nucula sp.

bivalve mollusk

Prodromites sp.

ammonite mollusk

Stethacanthus mirabilis

shark

Examples of Continental Animals Archaeothyris florensis

reptile

Arthropleura sp.

millipede

Branchiosaurus sp.

amphibian

Ctenodus sp.

lungfish

Diplovertebron sp.

reptilelike amphibian

Eoblattina temporis

cockroach

Eophrynus prestvichi

spider relative

Hylonomus lyelli

reptile

Megalocephalus sp.

reptilelike amphibian

Meganeura monyi

dragonfly

Rhizodus hibberti

lobe-finned fish

Examples of Land Plants Calamites cistiiformis

giant horsetail

Cordaites sp.

conifer

Lepidodendron selaginoides

giant clubmoss tree

Neoropteris attenuata

seed fern

Psaronius sp.

tree fern

Walchia piniformis

conifer

*Based on Benton

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Carboniferous period, biodiversity in 105 Gondwanaland, much of which was over the South Pole. During the later part of the carboniferous, laurasia collided with Godwanaland. the resulting geological forces produced mountain ranges even in the middle of tectonic plates, such as the appalachian Mountains of north america. the land that is now Siberia collided with eastern europe to create what are now the Ural Mountains. the worldwide ocean (Panthalassic Ocean) was not divided by continents, as it is today. Marine life. all modern groups of marine organisms existed during the carboniferous except aquatic mammals (see figure). ●



Invertebrates. Several modern lineages of crustaceans are first known from the carboniferous period. they had not yet evolved the pincer claws that are so common in modern crustaceans. Brachiopods remained more common than the superficially similar bivalves. the largest brachiopods (though only four inches [10 cm] in diameter) lived at this time. Shelled cephalopod mollusks (relatives of today’s chambered nautilus) remained common. trilobites persisted, but there were fewer species of them than during their Ordovician peak of diversity. Vertebrates. Perhaps as a result of the extinction of the placoderm (armored fishes) at the end of the Silurian, sharks proliferated in diversity during the carboniferous. the shark Stethacanthus mirabilis had an anvilshaped dorsal fi n, the function of which is unknown. Bony fishes continued to proliferate in the seas.





would not work well for tree-sized plants on earth today but functioned well in the very wet conditions of the carboniferous. the fi rst seed plants evolved, possibly in drier upland regions, during this time. Before the carboniferous period, land plants grew only in wetlands, but now some grew on moist hillsides. the seed plants became more common, and the seedless trees began their slide toward extinction during a period of drier weather. the seed ferns (now extinct) were not ferns, but seed plants with fern-shaped leaves. By the end of the carboniferous, the fi rst true conifers had evolved, fully adapted to growing on dry hillsides. there were no flowering plants and were no plants such as grasses or shrubs that could grow in very dry conditions. Invertebrates. insects fi rst proliferated during the carboniferous. examples include Meganeura, a dragonfly with a two-anda-half-foot (75-cm) wingspan (see figure below). the fi rst cockroaches evolved during this period. Other arthropods included relatives of spiders; some millipedes, such as Arthropleura, were six feet (almost two m) long. Vertebrates. lungfi shes and lobe-fi nned fishes (such as the 24-foot-[7-m-]) long Rhizodus hibberti) became less common as amphibians became more numerous and diverse. One lineage of amphibians

Continental life. extensive swamps fi lled the shallow seas and lakes of the carboniferous period in the tropical areas. ●

Plants. large trees had been rare in the Devonian period, but trees up to 130 feet (40 m) in height became abundant in the carboniferous. Most of these were tree-sized versions of modern clubmosses (such as Lepidodendron), ferns (such as Psaronius, which had fronds almost five feet [1.5 m] long), and horsetails (such as Calamites). these trees had systems of water transport and sexual reproduction that

xviii+598_Biodiversity_F.indd 105

One of the largest arthropods of the Carboniferous period was the dragonfly Meganeura, with a wingspan of almost two feet (more than 60 cm). The higher oxygen content of the denser air in the Carboniferous period allowed large flying insects to evolve.

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106 carnivorous plants  106

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­ eveloped reptilelike characteristics. By the d end of the Carboniferous period, the first reptiles, with hard-shelled eggs that could be laid on dry land, evolved. Hylonomus may have been the ancestor of lizards, while Archaeothyris may have been the ancestor of the mammal-like reptiles. There were not yet any dinosaurs, mammals, or birds. Extinctions. The Carboniferous period is not recognized to contain one of the major extinction events. A worldwide period of warmer, drier climate near the end of the Carboniferous created conditions that favored the spread and diversification of seed plants and reptiles. See also conifers; fishes; insects; seed plants. Further Reading Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. ———. “Four feet on the ground.” In: Gould, Stephen J., ed. The Book of Life: An Illustrated History of the Evolution of Life on Earth. New York: Norton, 2001. Béthoux, Olivier, and Frank Wieland. “Evidence for Carboniferous origin of the order Mantodea (Insecta: Dictyoptera) gained from forewing morphology.” Zoological Journal of the Linnaean Society 156 (2009): 79–113. Clarkson, E. N. K. “Carboniferous crustaceans.” Geology Today 1 (2008): 11–15. Dudley, Robert. “Atmospheric oxygen, giant Paleozoic insects and the evolution of aerial locomotor performance.” Journal of Experimental Biology 201 (1998): 1,043–1,050. Gastaldo, Robert A., et al. “Community heterogeneity of Early Pennsylvania peat mires.” Geology 32 (2004): 693–696. Gugliotta, Guy. “Forest primeval.” Smithsonian, July 2009, 14–16. Smithson, T. R. “The earliest known reptile.” Nature 342 (1989): 676–678.

carnivorous plants  Carnivorous plants are

flowering plants that trap and digest animals, primarily insects. Since these plants are photosynthetic, they do not use the animals as sources of food energy but rather as sources of minerals. Carnivorous plants live in wet conditions in which the water is usually acidic as well as nutrient poor. These conditions include bogs, tropical rain forests, and pine barrens. Carnivorous plants trap insects in several different ways.

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The leaf of the carnivorous plant Drosera capensis entangles an insect in sap. The leaf produces digestive enzymes and absorbs molecules from the insects.  (Noah Elhardt; Wikipedia)

●●

●●

●●

●●

The most famous is the Venus flytrap (Dionaea muscipula), in which the insect trips over a fiber that causes the leaf to fold up and trap it. The upper surface of the folded leaf secretes digestive enzymes, then absorbs molecules from the digested insect. Many carnivorous plants such as sundews (Drosera rotundifolia) and butterworts (Pinguicula vulgaris) (see figure) have sticky hairs on the leaf or stem surfaces. The surface cells secrete enzymes that digest the entangled insects. Many carnivorous plants such as pitcher plants (Sarracenia purpurea) and cobra lilies (Darlingtonia californica) have leaves that form a vertical cylinder. Hairs on the inside of the cylinder point downward to a pool of digestive juices. Insects fall in and are digested, and their molecules are absorbed. Many carnivorous plants such as bladderworts (Utricularia vulgaris) have small underwater bladders with a door that

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Carson, Rachel Louise 107 Major Groups of Carnivorous Plants Family

Genus

Bromeliaceae

Brocchinia

Bromeliaceae

Catopsis

Byblidaceae

Byblis

Cephalotus

Common Name

Number of Species

Location

5

tropical

21

tropical

rainbow plant

5

tropical

Cephalotaceae

pitcher plant

1

tropical

Droseraceae

Aldrovandra

waterwheel

1

temperate

Droseraceae

Dionaea

Venus flytrap

1

temperate

Droseraceae

Drosera

sundews

152

temperate

Drosophyllaceae

Drosophyllum

sundew

1

temperate

Lentibularieaceae

Genislea

corkscrew

20

temperate

Lentibulariaceae

Pinguicula

butterwort

79

temperate

Lentibulariaceae

Utricularia

bladderwort

220

temperate

Nepenthaceae

Nepenthes

pitcher plant

90

Roridulaceae

Roridula

bug plant

2

temperate

Sarraceniaceae

Darlingtonia

cobra lily

1

temperate

Sarraceniaceae

Heliamphora

sun pitcher

7

tropical

Sarraceniaceae

Sarracenia

pitcher plant

10

opens quickly and sucks in small aquatic invertebrates. Plants of separate evolutionary lineages (see table) have converged upon some of these same adaptations. For example, both the dicot pitcher plants and some monocot bromeliads trap insects in pools of water. Carnivorous plants are particularly exciting subjects for evolutionary studies, a fact recognized ever since Charles Darwin devoted an entire book to them. An entire community of organisms, including insect larvae (often mosquitoes), protists, and bacteria, may live in a pitcher plant’s pool. These organisms decompose the insects that fall into the pool of water. The wastes produced by these organisms are what directly feed the pitcher plant. The insect larvae in the pool hatch into adults that fly away unharmed. It is, after all, the nitrogenous molecules, not the insects themselves, that are useful to the carnivorous plants. One pitcher plant, Nepenthes lowii, is shaped somewhat like a chamberpot, and shrews have been observed to defecate in it (this is not a joke), which provides nitrogen fertilizer to the plant just as effectively as would the bodies of insects.

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tropical

temperate

See also bogs, life in; convergence; Darwin, Charles; flowering plants (angiosperms); tropical rain forests and deforestation. Further Reading Botanical Society of America. “Carnivorous plants/insectivorous plants.” Available online. URL: http://www. botany.org/Carnivorous_Plants/. Accessed August 8, 2011. Darwin, Charles. Insectivorous Plants. Honolulu: University Press of the Pacific, 1875/2002. Pietropaolo, James, and Patricia Pietropaolo. Carnivorous Plants of the World. Portland, Ore.: Timber Press, 2005. Zimmer, Carl. “Fatal attraction.” National Geographic (March 2010): 80–95.

Carson, Rachel Louise  (1907–1964)  American  Biologist  Rachel Carson is famous for having brought together the research that demonstrated the devastating effects of pesticide use upon humans, wild animals, and entire ecosystems. As a scientist and superb writer, she was able to make a case that was not only scientifically convincing but

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108 Carson, Rachel Louise 108 e­ motionally compelling in her 1962 book Silent Spring, which remains one of the classics of popular science and nature literature. Born on May 27, 1907, Carson grew up with an interest in nature. She earned a Ph.D. in marine zoology in 1932 (see figure). She wrote radio scripts for the U.S. Fish and Wildlife Service during the depression era and after 1936 was in charge of all Fish and Wildlife Service publications. She wrote pamphlets about conservation, which had become a major concern of the U.S. federal government. On her own time, she wrote popular books about nature for a general readership (such as The Sea Around Us) and books for children. She resigned her government position to become a full-time writer in 1952. Carson became increasingly concerned about the effects of pesticides on the human and natural environments. She amassed numerous references from scientific literature to use in Silent Spring. She not only demonstrated that pesticides were dangerous to the humans who used them or happened to

first entry get in the way of the spray but that they also had calamitous effects on populations of wild animals such as birds (hence the title of her book). Not only that, but even when pesticides were used in low concentrations, the food web could concentrate them until the tissues of top predators contained high levels of pesticide, a process called biomagnification. This was particularly true of DDT, which was a long-lasting pesticide. DDT interfered with calcium metabolism and caused birds at the top of the food chain, such as pelicans and eagles, to lay eggs that cracked open. Largely as a result of the use of DDT, birds such as the bald eagle were threatened with extinction. Furthermore, the profligate use of pesticides encouraged pest populations to evolve resistance to them, requiring the use of larger and larger amounts of pesticide to achieve less and less effect. Silent Spring was vigorously attacked by the corporations that manufactured pesticides. Carson was, however, able to maintain her case during tes-

Rachel Carson conducts marine biology research with her colleague Bob Hines in 1952.  (United States Fish and Wildlife Service and NCTC Archives/Museum)

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cladistics  109 timony to the U.S. Congress in 1963. Carson died of cancer in 1964 but lived to see the beginning of legislation that restricted the use of pesticides to safer levels and situations. She would have been very pleased to know that the use of DDT was banned in the United States in 1972 and that the bald eagle made a considerable recovery in the three decades following this ban. She would not be pleased, however, to see that pesticides are still used heavily in the United States, especially where migrant farmworkers are exposed to them, and that DDT, while not used in the United States, is manufactured in the United States, and used in other countries. As the book by Angus Wright explains, the heavy use of pesticides in regions of Mexico that supply winter vegetables to American supermarkets has a devastating effect on the health of the peasants who raise the vegetables. In 2007, a resolution of respect for Rachel Carson was introduced into the U.S. Senate. Such resolutions require a unanimous vote. There was one dissenting vote for this resolution (Tom Coburn, Republican of Oklahoma). He claimed that Carson’s attack on DDT resulted in the deaths of millions of African children. In African countries, DDT had been banned in the 1990s for agricultural use, but not for the control of mosquitoes that spread malaria. In Silent Spring, Carson had not called for a complete ban on pesticides but for their limited and focused use. It appears that today Rachel Carson still faces a campaign of misinformation. See also biomagnification; pollution; resistance, evolution of. Further Reading Carson, Rachel. The Sea Around Us. New York: Oxford University Press, 1951/2003. ———. Silent Spring. New York: Houghton Mifflin, 1962/2002. Lear, Linda. Rachel Carson: Witness for Nature. New York: Henry Holt, 1997. Lytle, Mark Hamilton. The Gentle Subversive: Rachel Carson, Silent Spring, and the Rise of the Environmental Movement. New York: Oxford University Press, 2007. Matthiessen, Peter, ed. Courage for the Earth: Writers, Scientists, and Activists Celebrate the Life and Writing of Rachel Carson. New York: Mariner, 2007. Wright, Angus. The Death of Ramón González: The Modern Agricultural Dilemma, Rev. ed. Austin: University of Texas Press, 2005.

chimpanzees  See primates. chordates  See animals. cladistics  Cladistics is the modern, evolution-based method of classifying biodiversity. It is a technique that classifies organisms on the basis of shared derived characters, which are similarities that they have inherited from a common ancestor. This method assumes that two species with a greater number of shared derived characters are more closely related than two species that have fewer shared derived characters. The common ancestor of two species represents a branch point (Greek clados means “branch”) in the evolutionary histories of these species. Cladistic analysis can be applied to any set of evolutionary lineages, not just to species. Cladistic analysis is also called phylogenetic analysis. This method was developed in 1950 by the German entomologist Willi Hennig. A similar method, developed by the American botanist Warren Wagner, contributed methodologies that are now part of cladistic analysis. Cladistic analysis generates clusters of branches entirely on the basis of the characters of species. The diagram that represents the branching pattern is called a cladogram. The older systems of classification, in contrast, attempted to reconstruct the evolutionary history of the organisms in question. By making no a priori evolutionary assumptions, cladistic analysis generates a set of possible evolutionary relationships and allows the investigator to choose the one that most closely matches the data of modern organisms or, if known, the data from the fossil record. Grouping the species objectively on the basis of similarities has two advantages over older systems of classification: ●●

cartilaginous fishes  See fishes. ●●

chaparral  See shrublands.

xviii+598_Biodiversity_F.indd 109

All the species are placed at the tips of the branches rather than at branch points. Modern green algae and modern flowering plants are descendants of a common ancestor, but the lineage that led to green algae has undergone less evolutionary modification than the lineage that led to flowering plants. Green algae and flowering plants are at separate branch tips of the cladogram. The ancestral population of organisms from which both green algae and flowering plants are descended no longer exists. Cladistics allows a more objective approach to classification than the traditional systems. The cladogram can be generated by

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110110 cladistics 

first entry

mathematical rules. This is often done by a computer. The investigator’s preferences do not influence the results. As a result of this approach, cladists will not say that one modern group evolved from another modern group. Consider the example of green algae and flowering plants. If one could actually have looked at their common ancestor, it would have looked like green algae. Cladists will not generally say that flowering plants “evolved from” green algae. They will say that green algae and flowering plants evolved from a common ancestor. Choosing the traits. The investigator must choose which traits are to be used in the analysis. Some traits are ancestral (plesiomorphies), and some are derived (apomorphies). There are four categories of traits: 1. Shared ancestral traits (symplesiomorphy). Ancestral traits are shared by almost all of the species in the analysis; ancestral traits cannot be used to distinguish among the species. In a cladistic analysis of flowering plants, for example, chlorophyll would not be a useful trait, since almost all flowering plants have chlorophyll in their leaves, a trait they inherited from their common ancestor. Most human characteristics are symplesiomorphies shared with other apes. 2. Unique traits (autapomorphy). Characteristics that are totally unique to one species also cannot be used to distinguish among the species. Consider a cladistic analysis of flowering plants in which one of the species is a parasitic plant, lacking chlorophyll in its leaves. The lack of chlorophyll is not a useful trait for this analysis, since only one of the species has this trait. An example from human evolution would be the unique skull characteristics, such as the projecting face and strong bite, of the Neanderthals. 3. Convergences (homoplasy). In many cases, a trait may evolve more than once. This could happen in either of two ways. First, the trait may have evolved into a more advanced form, then reverted back to the primitive form, during the course of evolution. This would cause a species to resemble a distantly related species that had retained the ancestral form all along. Second, two species with separate origins may have evolved the same trait. The evolutionary biologist Caro-Beth Stewart calls homoplasy the “ultimate trickster” of cladistics. Consider examples of homoplasy from plants, from nonhuman animals, and from humans: ●●

A cladistic analysis of flowering plants may include two parasitic plant species that lack chlorophyll, one of them a parasitic relative of heath plants (such as genus Pterospora), the other a parasitic relative of morning glo-

xviii+598_Biodiversity_F.indd 110

●●

●●

ries (genus Cuscuta). The common ancestor of these two plants had chlorophyll. The chlorophyll was lost in two separate evolutionary events. It would be incorrect to classify Pterospora and Cuscuta together into one group, with the other heath and morning glory plants into another group. A cladistic analysis of vertebrates would include both mammals and reptiles. All mammals except monotremes have live birth. Most reptiles lay eggs, but some snakes have live birth. No biologist would classify live-bearing snakes together with the mammals, and the monotremes together with the reptiles. Live birth evolved more than once: in the ancestors of certain snakes and in the ancestors of most mammals. Increased brain size evolved independently in Homo erectus, Neanderthals, and the lineage that led to modern humans.

It is generally easier for convergence to occur in the loss of an old adaptation (e.g., the loss of chlorophyll) than in the acquisition of a new one. Traits that result from convergence are called analogous to each other. In contrast, traits that are inherited from a common ancestor are considered to be homologous to each other. Convergence represents a problem for cladistics, just as it does for older methods of evolutionary classification. 4. Shared derived traits (synapomorphy). These are the traits that evolutionary scientists try to use in cladistic analysis. A cladistic analysis requires the choice of traits that distinguish different lineages: The species within each lineage shares the traits with one another, but not with species in other lineages. Examples of synapomorphies include hair (which all mammals, and only mammals, possess) and feathers (which all birds, and only birds, possess). It is generally easy to eliminate ancestral and unique traits from a phylogenetic analysis. The recognition and elimination of homoplasy can sometimes be difficult. Evolutionary scientists use more than one trait in a cladistic analysis. Not only must the traits be shared derived traits, they must be independent of one another. To consider leaf length and leaf width as two traits would be incorrect, since longer leaves are usually wider as well. Rather than two traits, these may be just two ways of measuring leaf size. The above examples used easily visible characteristics to classify organisms into groups. The characteristics need not be visible. In fact, many cladistic analyses use DNA sequence information. Suppose a scientist has segments of DNA from three species. If the segment of DNA is 100 nucleo-

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cladistics tides in length, this allows 100 characters to be used to test each cladogram. nearly every phylogenetic study includes at least one analysis that uses Dna nucleotides as traits. it is no easier to use Dna than to use visible characters in cladistic analysis. the reason is that one cannot compare just any old piece of Dna of one species with any old piece of Dna in another, any more than one can make comparisons of just any visible trait. Just as visible traits must be homologous, so the Dna segments must be homologous. the investigator must compare the same gene in all the species in the analysis. Further complications arise when one considers that some mutations exchange one nucleotide for another, while other mutations add or delete nucleotides, or reverse segments, or even move segments to different places. Usually, researchers use certain well-studied Dna sequences rather than trying to figure out a new one for themselves. in comparisons among plants, matK (the gene for an enzyme that acts upon the amino acid tyrosine) and

111

rbcl (the gene for the large subunit of the enzyme rubisco) are frequently used. Some analyses use noncoding Dna for phylogenetic analysis. Researchers may use transposable elements because homoplasy is very unlikely to occur with them. it is very unlikely that the same transposable element would evolve twice: it would neither insert itself in the same location in the chromosomes of two different species nor transfer to a new location without gaining or losing a few nucleotides in the process. Other analyses use short or long interspersed sequences in the noncoding Dna. the figure uses the presence or absence of 20 segments of noncoding Dna to construct a cladogram of mammals. cows and deer are clustered together because they share all the segments for which information is available. Whales and hippos are clustered together because they share 15 of the 17 segments for which information is available. Whales and cows are not clustered closely together because they share only nine of the 17 segments for which information is

This cladogram is based on 20 noncoding sequences (“locations”) in the genomes of six mammal species. The “1” refers to the presence, and the “0” to the absence, of the sequence. The camel (the outgroup) has none of the 20 sequences and is less related to any of the others than they are to one another. Pigs form a clade separate from the remaining four species; they have sequences 19 and 20, while the others do not. The others all have sequences 10 and 12. Cattle and deer share four sequences that none of the others have, whereas whales and hippos share four sequences that none of the others have. This cladogram is meant to show patterns, not degrees, of relationship. Therefore, the horizontal line lengths are arbitrary.  (Based on data from Nikaido, et al.)

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112112 cladistics  available. Camels are not closely related to cows, as they have none of the 11 DNA segments that cows possess. Choosing the best cladogram. A computer can generate many possible cladograms for any set of species that are being compared. Which of these cladograms is the correct one? The correct one is the one that most closely matches what actually happened during evolutionary history. Nobody can know exactly what happened during evolutionary history; cladists must make an assumption about which cladogram is best. They often make the assumption of parsimony, that is, they choose the simplest explanation. To do this, they choose the cladogram that requires the fewest number of character changes. Consider this simplified example in the classification of dogs, cats, and lions. Since each group has two branches, one could classify them in three ways: 1. [Dogs] [Cats, Lions] 2. [Dogs, Cats] [Lions] 3. [Dogs, Lions] [Cats] Cats and lions both have retractable claws; dogs do not. Cladograms 2 and 3 require that retractable claws should have evolved twice, separately in cats and lions. Therefore, cladogram 1 is the most parsimonious. It would not be safe to draw a conclusion based upon just one characteristic (in this case, retractable claws). Cladograms based on any of a number of other characteristics would lead to the same conclusion: Cats and lions form part of the feline group, while dogs are part of a separate (canine) group. From this, one would conclude that cats and lions shared a common ancestor that lived much more recently than the common ancestor of canines and felines. It is easy enough to compare the three cladograms that are possible with three species. However, as more species are compared, the analysis becomes exponentially more difficult. When comparing even a slightly larger number of species, the calculations become so complex that they can be performed only by a computer. As the number of species in the analysis increases, even a computer cannot sort through all the possibilities. For 10 species, there are more than 2 million possible cladograms; for 50 species, there are 3 × 1076 possible cladograms. To provide some idea of how large a number this is, consider that the universe has existed for less than 1018 seconds! The computer must randomly generate a subset of several hundred possible cladograms and make comparisons among them. Even when a cladistic analysis compares only a few hundred of the possible cladograms, there may

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first entry be a large number of almost equally parsimonious ones. The computer must then generate a consensus tree that preserves the patterns that the best cladograms share with one another. Applying cladistics to classification. A cladistic approach to classification would group organisms together on the basis of the branch points in the cladogram. A clade (whether it corresponds to a genus, a family, an order, a class, a phylum, or a kingdom) must consist of all species that share a common ancestor, and only those species. Such a clade is called monophyletic (see figure on page 113). Cladists will not accept a genus, family, order, class, phylum, or kingdom that includes only some of the species that have evolved from a common ancestor. Such a group is called paraphyletic. Cladists most vigorously reject taxonomic groups that both omit some species that share a common ancestor and include some species that do not, a group referred to as polyphyletic. A cladistic approach can lead to a different system of classification than what is traditionally recognized, as in these examples. ●●

●●

“Monkey” is a paraphyletic category. The New World monkeys diverged from the Old World lineage, which includes Old World monkeys and all of the apes. To a cladist, either a human is a monkey, or else there is no such thing as a monkey. “Reptile” is a paraphyletic category. Terrestrial vertebrates are traditionally classified into reptiles, birds, and mammals. Reptiles are cold-blooded and have scales, birds are warm-blooded and have feathers, and mammals are warm-blooded and have hair and milk. This sounds like a straightforward classification based upon characteristics: classes Reptilia, Aves, and Mammalia. Cladists point out that several lineages of reptiles branched off from one another to produce separate lineages such as turtles, lizards, tuataras, more than one branch of dinosaurs, and therapsids. Mammals evolved from therapsids, and birds from dinosaurs. Reptiles, birds, and mammals are not separate clades, or branches. “Reptile” is therefore a paraphyletic group that contains some, but not all, of the species descended from the group’s common ancestor. Strict cladists insist that either the term reptile should not be used at all, or else the term reptile should include birds and mammals. To a cladist, the term dinosaur includes birds, and birds are dinosaurs. One can always tell a cladist because he or she

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cladistics

113

will refer to the big lumbering beasts of the Mesozoic era as “nonavian dinosaurs” rather than simply as dinosaurs. to a cladist, either a human is a reptile, or else there is no such thing as a reptile. ● “Fish” is a paraphyletic category. Vertebrates include fishes, amphibians, reptiles, mammals, and birds. the reptile clade (which includes birds and mammals) and the amphibian clade share a common ancestor, but the amphibian-reptile clade The flowering plants (angiosperms) are a monophyletic group that consists branched off from the lobe- of all the species descended from a common ancestor; within the angiofi nned fishes, which is just one sperms, the monocots are a monophyletic group. branch of several branches that are usually called “fishes”; the othto the grouping patterns that had been proposed ers are the ray-fi nned fishes, cartilaginous previous to the development of cladistics. One fishes, hagfishes, and lampreys. “Fishes” is example is within the walnuts (genus Juglans). For therefore also a paraphyletic group. cladisat least a century, botanists have recognized four tically speaking, then, there is no such thing major groups of trees in this genus, based upon leaf as a fish, unless by fi sh one includes amphiband fruit characteristics, as well as upon the geograians and reptiles (which includes birds and phy of where the trees grew: mammals). to a cladist, either a human is a fish, or else there is no such thing as a fish. ● the black walnuts of north and South america, section Rhysocaryon (16 species) Some cladists, in fact, insist that scientists ● the asian butternuts, section Cardiocaryon should not even bother with the linnaean sys(three species) tem. instead of kingdoms, phyla, classes, orders, ● the butternut of eastern north america, secfamilies, and genera, scientists should refer only tion Trachycaryon (one species) to clades. this approach is called the PhyloCode. ● the eruasian walnut, section Dioscaryon Most people, from common experience and also (one species) from the biology classes they took in school, tend to think of the old-fashioned classifications such the botanist alice Stanford and colleagues peras fi sh, amphibian, reptile, bird, and mammal. the formed cladistic analyses upon the walnuts using new classifications are unfamiliar and confusing three different regions of Dna: the matK gene, an to most lay people. What many science teachers itS (internal transcribed spacer, a type of noncoddo is accept the evolutionary insights of cladistic ing Dna), and RFlP (restriction fragment length analysis but do not attempt cladistic consistency in polymorphism Dna). they did not base their terminology. results on just one region of Dna, but on a consenCladistics confi rms evolution. the grouping sus of three regions. the result was the same four patterns produced by one cladistic analysis often groupings of walnut species. cladistics, therefore, closely resemble the grouping patterns produced by often confi rms that the evolutionary classifications another. For example, a cladistic analysis that uses that had been previously produced were not the visible characteristics usually comes out almost the mere product of evolutionists’ imaginations. comsame as a cladistic analysis that uses Dna. this puters, which have no imagination, produce the is highly unlikely to happen by chance and almost same groupings. certainly means that the resulting classifi cation this result is similar to what happened when represents what really happened in the evolutioncharles Darwin published On the Origin of Speary history of the organisms. cies. Before Darwin’s theory, in fact before the Moreover, the grouping patterns produced by acceptance of any form of evolution, scientists cladistic analyses usually bear a close resemblance had been classifying organisms by the linnaean

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114114 cladistics

first entry

what the pattern of evolutionary branching was for these viruses. He then performed cladistic analyses using Dna base sequences. the resulting cladogram closely matched the evolutionary pattern that had actually occurred. cladistics has also proven its worth in the study of evolutionary medicine. cladograms regularly appear in articles published in such journals as the Journal of Emerging Infectious Diseases, published by the national institutes of Health. epidemiologists The dicots are a paraphyletic group of flowering plants because the mono- routinely perform cladistic analycot lineage is excluded from it. The term dicot is used descriptively but is ses on strains of diseases in order not a phylogenetic classification. to determine which strains are most closely related to which othsystem, based on what seemed to them to be the ers in the hope of deducing where new strains of most “natural” groupings. Darwin said that these diseases originated. this knowledge helps in the “natural” groupings were, in fact, the product production of vaccines, to control the spread of of common descent and that scientists, to their the disease, and to predict the emergence of new amazement, had been studying evolution all along diseases. it was cladistic analysis that allowed epiwithout knowing it. demiologists to identify the strain of anthrax that cladists pay close attention to the occasional was used in bioterrorist attacks in the United States differences between cladistic and traditional clasin 2001. cladistics is also important to epidemiolosifi cation systems. One signifi cant example of gists who want to know from which animal species these differences is the reclassification of the flowa human disease may have evolved. cladistics was ering plants. traditionally, all flowering plants the method that allowed researchers to determine were classified as either monocots or dicots. More that HiV came from chimpanzees. cladistics has recent analysis indicates that the monocots are a proven not only a revolutionary technique within monophyletic group, but the dicots are not. the evolutionary science but has allowed evolutionary monocots are one branch from within the dicots. science to produce practical benefits to humankind. therefore, dicot is a paraphyletic group (see figure). See also biological classification; cladistics has shown the monocot-dicot dichotconvergence. omy that every college biology student learns is an Further reading oversimplification. cracraft, Joel, and Michael J. Donoghue. Assembling the Perhaps the main advantage of cladistics in Tree of Life. new york: Oxford University Press, evolutionary science is that it allows investigations 2004. to proceed without having detailed knowledge of Hillis, Daniel M., et al. “experimental phylogenies: Genwhich ancient species, represented today by fossils, eration of a known phylogeny.” Science 255 (1992): were or were not ancestral to which modern spe589–592. cies. For example, the existence of Homo habilis nikaido, M., a. P. Rooney, and n. Okada. “Phylogenetic about 2 million years ago is well known. However, relationships among cetartiodactyls based on inserscientists cannot know if H. habilis represented the tions of short and long interspersed elements: Hippoactual ancestral population from which the modern potamuses are the closest extant relatives of whales.” human species evolved or whether modern humans Proceedings of the National Academy of Sciences USA evolved from another population similar to H. habi96 (1999): 10,261–10,266. lis. With cladistics, research can continue despite Stanford, alice M., Rachel Harden, and clifford R. Parks. this uncertainty. “Phylogeny and biogeography of Juglans (Juglandathe cladistic method has received some expericeae) based on matK and itS sequence data.” Amerimental confi rmation. the evolutionary microbiolocan Journal of Botany 87 (2000): 872–882. gist Daniel Hillis grew cultures of viruses in his Stewart, caro-Beth. “the powers and pitfalls of parsilaboratory, allowing them to undergo mutations and mony.” Nature 361 (1993): 603–607. evolve into different lineages. He knew precisely

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cloud forests  115

cloud forests  Cloud forests are high-elevation tropical forests. Being tropical, they do not experience seasonal shifts in temperature, but because of their high elevation, they experience cool temperatures, especially cold nights. As a result, the forest trees are small. Cloud forests do not receive a great deal of rain but are typically shrouded in mist. As a result, cloud forests have lianas and epiphytes at least as profuse as those of the tropical rain forests. Orchids and bromeliads cluster on the branches of cloud forest trees.

Many animal species live in cloud forests, which are particularly famous for amphibians that live in pools of water at the bases of bromeliad leaves. Cloud forests experience cool but not deeply freezing temperatures. This means the conditions are favorable for both temperate and tropical families of woody plants. Cloud forests that are close to temperate zones, such as those of Mexico and of Yunnan in southern China, contain trees of woody plant families, such as the oak and walnut families, that dominate deciduous forests, and even some of the same

Examples of Cloud Forest Tree Species Species

Common Name

Plant Family

Acer saccharum

Sugar maple

Aceraceae (maple)

Carya ovata

Shagbark hickory

Juglandaceae (walnut)

Juglans pyriformis

Mexican walnut

Juglandaceae (walnut)

Liquidambar macrophylla

Sweetgum

Altiginaceae (sweetgums)

Quercus sartorii

Sartor’s oak

Fagaceae (oak/beech)

Ulmus mexicana

Mexican elm

Ulmaceae (elm)

Quercus copeyensis

Barcino oak

Fagaceae (oak/beech)

Quercus costaricensis

Costa Rican oak

Fagaceae (oak/beech)

Quercus seemannii

Seemann’s oak

Fagaceae (oak/beech)

Persea caerulea

Mountain avocado

Lauraceae (laurel)

Mexico

Costa Rica

Podocarp conifer

Podocarpus macrostachyus Sapium pachystachys

Yos

Euphorbiaceae (spurge)

Colombia and Ecuador Clusia flaviflora

Clusiaceae

Hedyosmum cumbalense

Chloranthaceae

Myrcianthes fragrans

Myristicaceae

Weinmannia glabra

Cunoniaceae

Borneo and Sumatra Adinandra acuminata

Theaceae (tea)

Leptospermum flavescens

Myrtaceae (myrtle)

Quercus lineata

Fagaceae (oak/beech)

Quercus lowii

Fagaceae (oak/beech)

Quercus treubiana

Fagaceae (oak/beech)

Ternstroemia denticulata

Theaceae (tea)

Yunnan, China Cyclobalanopsis glauca

Blue oak

Fagaceae (oak/beech)

Lithocarpus hancei

Tanbark oak

Fagaceae (oak/beech)

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116116 coevolution  species, such as shagbark hickory and sugar maple (see table on page 115). Cloud forests near the equator, such as those in Ecuador, have many trees in families of tropical origin, although oaks live in the cloud forests of Borneo and Sumatra (see table). In some areas of tropical mountains, conditions such as a fire cycle maintain grasslands, such as the Andean páramo, rather than forest. Cloud forests are particularly vulnerable to the greenhouse effect. Even a slight increase in temperature or change in weather patterns can cause the cloud layer to form at a greater altitude, too high to provide the constant drip of water upon which the plants and animals depend. The golden toad (Bufo periglenes) of Central America appears to have become extinct because the cloud forests are no longer cloudy enough. See also disturbances, ecological; greenhouse effect and biodiversity; tropical rain forests and deforestation. Further Reading Churchill, S. P., et al. Biodiversity and Conservation of Neotropical Montane Forests. Bronx, N.Y.: New York Botanical Garden, 1995. Gomes, Laurens G. L., et al. “Tolerance of frugivorous birds to habitat disturbance in a tropical cloud forest.” Biological Conservation 141 (2008): 860–871. Hamilton, Lawrence S., et al. Tropical Montane Cloud Forests. New York: Springer, 1995. Pounds, J. A., et al. “Biological response to climate change on a tropical mountain.” Nature 398 (1999): 611–615. Shi, J., and H. Zhu. “Tree species composition and diversity of tropical mountain cloud forest in the Yunnan, southwestern China.” Ecological Research 24 (2009): 83–92. Tennesen, Michael. “Fog forests.” Discover, April 2009, 60–65.

coevolution  Coevolution occurs when the evolution of one species influences and is influenced by the evolution of another species. Every species has experienced coevolution, since every species exists in a web of ecological relationships. In the general sense, every species coevolves with every other species. In the specific sense, the term coevolution is usually restricted to important and specific relationships between species rather than the diffuse background of ecological relationships. For example, many plants have evolved the ability to compensate for the loss of tissue to herbivores, and herbivores have evolved the ability to digest plants, but this interaction is usually considered too diffuse to qualify as coevolution. Plants also evolved the ability to produce toxins, and herbivores evolved the ability to detoxify them. This can be considered coevolution

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first entry Types of Symbiotic Interactions Type of Interaction

Effect on Host

Effect on Other Species

Parasitism

Harmful

Beneficial

Commensalism

Unaffected

Beneficial

Mutualism

Beneficial

Beneficial

because the toxins and the ability to detoxify them are both often specific to certain groups of plants and herbivores. In coevolution, natural selection favors those individuals within a population that most effectively resist or cooperate beneficially with individuals of another species. In many cases, coevolution has produced symbiotic relationships between species (symbiosis), in which the life processes of individuals within one species are closely linked to those of individuals of another species (see table). The following are examples, rather than a thorough analysis, of coevolution.

Coevolution of Plants and Herbivores During the 1950s, ecologists such as Gottfried Fraenkel began to ask, why is the world green? Insects are capable of massive population growth, and by now they should have eaten every bit of green leaf on the planet. Part of the reason this has not happened is that many insects die during the winter, and their populations must grow again the following spring. Still, even the winterless tropical forests are green. Why? The answer lies with coevolution. Plants produce a great variety of secondary compounds in their tissues, especially their leaves. Secondary compounds have no primary metabolic role in organisms; they usually serve a defensive role instead. Many secondary plant compounds are famous for the uses to which humans put them. The active ingredients of spices and of many pharmaceuticals as well as many miscellaneous compounds such as caffeine are all secondary compounds of plants. Some of the chemicals, such as tannins, are digestion inhibitors, while many others are mildly to strongly poisonous. In some cases, plant secondary compounds can work in ways other than as toxins. Compounds in the needles of some conifers function as inhibitors of insect growth, so that insects that eat them cannot reach maturity. Some plants produce compounds that aphids mistake for predator alarm signals; this scares the aphids away. Other plants release chemicals into the air when herbivorous insects chew on them, and these chemicals attract wasps that then lay their eggs on the herbivores. Most plants have evolved chemical defenses against

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coevolution  117 herbivores. Because of coevolution, the world is not a big salad bowl. Plants usually produce the greatest amounts of secondary compounds in their leaves, as the stems are tougher (and often defended by thorns or spines), while roots are underground, where herbivorous animals are fewer. Leaves need to be relatively free of defensive spines and to be somewhat soft because they have to release water and oxygen into, and absorb carbon dioxide and light from, their environment. Some plants have relatively little toxic defense against herbivores. These plants are usually the ones that can grow back quickly after being eaten. Grasses, for example, have few toxic compounds in their leaves, but they grow back quickly from underground structures after being grazed. Grass leaves have high levels of silicon dioxide, which makes them tough. Only specialized grazing animals can chew and digest them. Other plants get by without secondary compounds because they live for only a short time and vanish from the scene after reproducing. Chemical defenses are costly. Some plants may produce fewer chemical defenses in years of abundant rainfall, when they can more easily afford to grow new leaves to replace those lost to herbivores. In some cases, plants wait until the herbivores begin to eat them, then undergo a rapid response and produce toxins. In some cases, plants respond to drought by producing chemicals that make them more toxic. They may respond to drought and to herbivory by some of the same reactions. In all these and other ways, herbivores have influenced plant evolution. Herbivores have evolved ways of eating plant tissue despite these defenses. Some animals consume massive quantities of herbage, get what little nutrition they can from it, and evacuate the rest. These animals (such as caterpillars, koalas, and sloths), deriving little energy from their food, are generally lethargic. Other animals can tolerate the toxins of specific plants and even specialize upon them. The caterpillar of the monarch butterfly (Danaus plexippus) eats milkweeds (genus Asclepias), which have chemicals that interfere with heartbeats, but they sequester the poisons in special sacs. They even use the chemical for their own defense: Having stored up the milkweed poison, they are now themselves poisonous to their predators. Caterpillars of Heliconius butterflies similarly use toxic compounds from the passionflower vines (genus Passiflora) upon which they feed. Humans eat tissues of plants as spices. The fact that spices contain potent chemicals prevents humans from eating very much plant tissue. The human attraction to spices may have evolved because some spices have antimicrobial activity. In all these and other ways, plants have influenced herbivore evolution.

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Plants and herbivores are participating in what has been called an arms race, in which increased plant defense selects for increased ability of the herbivore to tolerate or to avoid the plant defense and increased herbivore success selects for increased plant defense. Since plant-herbivore coevolution occurs over a long time period, the only thing similar to experimental confirmation is that on some islands plants do not have strong defenses. For example, a stingless nettle has evolved in Hawaii, which has no native browsing mammals. Evolution of defense against herbivores has occurred separately in every evolutionary lineage of plants. Therefore, hardly any two plant defenses are the same. So vast is the diversity of plant chemical defenses that these chemicals are sometimes used to assist in the evolutionary classification of plants.

Coevolution of Predators and Prey Predators are animals that kill entire organisms for food. Usually, their prey is other animals, but animals that eat seeds are usually called seed predators because a seed contains an entire plant. The evolution of predators has been overwhelmingly influenced by their search for prey. They tend to have greater intelligence, sensory acuteness, and agility than prey. Some predators have evolved pack behavior. The evolution of the prey has been just as strongly influenced by the need to avoid or resist predators. In some cases, this involves sensory acuteness, agility, and herd behavior, just as it does with predators. Some prey form large herds in which the members can watch out for one another; in some flocks of birds and schools of fish, the coordinated and sudden movements of the members can disorient and confuse the predators. In some cases, the prey animals have evolved to simply become too big for most predators to be able to handle. The evolution of predators constantly influences the evolution of prey, and vice versa, because individuals that are slower, less intelligent, or less able to function as part of the group are more likely to be eaten or to not eat. Seed predators have evolved the ability to find and sometimes store and retrieve seeds. The fact that seed predators, such as squirrels, fail to retrieve all the seeds they store is what makes them effective dispersers of seeds to new locations. As such, they often constitute a net benefit to the plant, some of whose seeds they eat. Seeds are a rich source of food for predators as well as for the embryonic plants inside of them. Seed plants have evolved, in turn, to resist seed predators, at least the ones such as weevils that offer them no benefit. Many seeds are mildly or strongly toxic. For example, while the apple fruit is delicious and nutritious, the seeds contain cyanide. This encourages the evolution of animals that will eat

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118118 coevolution 

first entry

“Ghosts of Biodiversity Past”

S

pecies evolve in response to one another, a process known as coevolution. This has been one of the most important ways that the astonishing biodiversity of Earth has come into existence. Many adaptations of one species make sense only in relation to another. But what happens if one of the coevolutionary partners becomes extinct? The surviving species may continue to manifest its adaptations, perhaps for thousands of years, even though the adaptations are now meaningless. The adaptations of the surviving species now become puzzling, “ghosts of biodiversity past.” In order for coevolutionary adaptations to continue, even when the other partner is a ghost, the adaptations must not cost so much that natural selection would get rid of them quickly. Also, the ghost must have become extinct recently, otherwise natural selection, operating over long periods of time, would have eliminated the coevolutionary adaptations even if they were not very costly. Several species of trees in North America appear to participate in a coevolutionary relationship in which the partner has become extinct. First, consider some examples of trees that produce fruits that no wild animal appears to eat. Bois d’arcs. These small trees are noted for their very strong wood and have been planted widely across North America as fencerow windbreaks. Like other trees in the mulberry family, Maclura pomifera has separate male and female trees, and the females produce composite fruits that consist of a cluster of ber-

ries. While mulberries are small, sweet, and edible by many species of birds and mammals (including humans), the fruits of the bois-d’arc are large (up to seven inches [or 15 cm] in diameter), green, hard, and sticky. (These trees are also called Osage oranges, because the fruits look a bit like oranges and grow wild in the tribal lands of the Osage tribe, and hedge-apples, because the fruits look a bit like apples and the trees were planted as hedges.) While not highly poisonous, the fruits are definitely repulsive and difficult to digest. Squirrels consume the seeds, but this is not dispersal; they kill the seeds rather than dispersing them. The fruits commonly fall to the ground and rot; several of the fruit’s dozens of seeds grow, resulting in a clump of trunks that grow together. In some cases, the trunks fuse to form what appears to be a single trunk. It is rare to see a single-trunked bois d’arc tree in the wild. (Single-trunked bois d’arc trees are common, but these were planted in fields that were subsequently abandoned and are not really wild trees.) Another consequence of the absence of a disperser is that wild bois d’arcs are found only in river valleys in Oklahoma, Texas, Arkansas, and nearby areas. Without dispersers, the only direction for such large fruits to roll is downhill, into river valleys. Had they not been planted widely across eastern North America, they might eventually have become extinct as the last fruit rolled into the sea. Avocados. Wild avocados (Persea americana) are not nearly as large as the

the apple but pass the seeds unharmed through their digestive tracts, obtaining nutrition from the fruit but not from the seeds. Many fruits have a laxative effect on animals, which encourages the animals to evacuate the seeds before they die in the intestines. Perhaps the most interesting way in which plants have evolved in response to seed predators is mast seeding. Many trees produce large seed crops every few years and few seeds at other times. In this way,

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ones in supermarkets, but they are still large enough that no extant species of animal swallows them whole. Many animals can nibble at the nutritious fruit, but the seeds are simply left near the parent in most cases. Which large animal might have eaten these fruits in the past? Honey locusts. Gleditsia triacanthos, a tree in the bean family, produces very long, spiral seed pods. No native species of mammal regularly eats these pods, even though they are juicy and sweet when young. Once cattle were introduced to North America, many of them ate these pods when available. Honey locusts have been widely planted as urban trees and have escaped again into the wild. There appears to be a similar lack of dispersal in the mesquite, a bush in the bean family that also produces sweet pods, though much smaller than those of the honey locust. In each of these examples, it is probable that the true disperser would have been an animal large enough to swallow the fruit whole, leaving the seeds intact—the way birds do with mulberries, for example. While there are no native mammals large enough to swallow these fruits today, there were many such mammals about 13,000 years ago, at the end of the Pleistocene epoch. The mammals became extinct for reasons that are not entirely clear. The trees that produce these fruits have not become extinct—a few of their seeds germinate even without adequate dispersal—but their populations have suffered from the extinction of the large Pleistocene

the seed predator populations do not build up; when the trees produce a huge (mast) crop, the predator populations cannot consume them all. Not only has coevolution occurred between plants and the animals that both eat and disperse their seeds, it has produced a radiation of species within each. Many pines have seeds with wings and that blow in the wind, but some have wingless seeds that are stored and eaten by crows and jays. A prolif-

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coevolution  119

mammals. Mammals that the Europeans brought to North America sometimes eat the fruits. For example, horses eat boisd’arc fruits, which is why they are also called horse apples. Other examples of fruits that no longer have dispersers may be papayas, mangos, melons, gourds, and watermelons. There are numerous fruits in Africa and Asia that are consumed and the seeds dispersed by animals (such as elephants) similar to the ones that became extinct in the Americas. Some of the fruits are inedible to most animals, but the now-extinct specialist dispersers may have had, as African and Asian fruit dispersers do today, intestinal bacteria that break down otherwise toxic products. Elephants eat clay, which adsorbs toxins from the digestive system. Might mammoths and mastodons have had similar adaptations that allowed them to consume fruits such as bois-d’arc? There are also some flowers whose pollinators appear to be extinct. Pawpaws (Asimina triloba), a small wild fruit tree of the eastern deciduous forest of North America, persist primarily by the spread and resprouting of roots and underground stems. No native pollinator appears to be reliable. Recently, native pollinator populations have declined precipitously, which threatens many native plant species with ultimate extinction. This may especially be true of large cacti in the deserts of southwestern North America, which rely on bats to pollinate their flowers. Thus, very soon these cacti may become ghosts of biodiversity past. There are also stems whose characteristics make sense only as adaptations to animals that no longer exist. The

bois d’arc also has large thorns, widely spaced on the branches, which appear totally ineffective at defending the leaves against the animals that eat them today, such as deer. Perhaps the thorns as well as the fruits are the leftover responses to the now-extinct herbivores. Wild honey locust trees have three-pointed thorns (hence the name tri-acanthos) bristling from their trunks. Hawthorns (genus Crataegus) have thorns even longer and more widely spaced than those of bois d’arc. Evolutionary biologists estimate that 10 percent of the woody plant species in New Zealand have a particularly tangled method of branching that protected them at one time from browsing by moas, giant birds that were driven into extinction by the first Maori inhabitants. The Pleistocene extinction occurred, as mentioned earlier, about 13,000 years ago. This is not long enough for trees to evolve some other mechanism of dispersal. One would expect that, eventually, the unnecessarily large fruits would no longer be produced, as mutant forms of the trees produced fruits that could be easily dispersed by wind or water. This may have happened in the case of the honey locust. An apparently new species of locust, the swamp locust Gleditsia aquatica, has evolved in southern North America, perhaps from a Gleditsia triacanthos ancestor. It produces much smaller pods that float easily in water. There are also some animal examples of the ghosts of biodiversity past. Pronghorns in the western grassland run much faster than necessary to escape modern predators, but prior to the Pleistocene extinction, they were pursued by the American cheetah, which was probably as fast as its barely-surviving

eration of both pine and jay species occurred in the Miocene epoch, which some evolutionary scientists attribute to coevolution between them.

Coevolution of Flowering Plants and Pollinators Pollination is necessary for sexual reproduction in seed plants. The pollen must be carried from the male organs (male cones of conifers, or stamens of

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African counterpart, the fastest animal in the world. As the ecologist Paul Martin wrote, “We live on a continent of ghosts, their prehistoric presence hinted at by sweettasting pods of mesquite [and] honey locust.” As the destruction of wild habitats by humans continues at a rapid pace, humans may be inaugurating the sixth of the mass extinctions in the history of the world. Sometimes, when two species are partners, human activities cause the extinction of one partner but not the other. Starting in the 19th century, scientists began to understand that the present is the key to understanding the past. To understand what happened in the past, look at what is happening today in the natural world. However, it is just as true that the past is the key to understanding the present. This is just one of the many meanings that emerge from the brilliant statement made by Theodosius Dobzhansky, one of the founders of modern evolutionary science: “Nothing in biology makes sense except in the light of evolution.” See also coevolution; herbivory; mass extinctions; Pleistocene extinction; pollination; seed dispersal.

Further Reading Barlow, Connie. The Ghosts of Evolution: Nonsensical Fruit, Missing Partners, and Other Ecological Anachronisms. New York: Basic Books, 2000. Buchmann, Stephen L., and Gary Paul Nabhan. The Forgotten Pollinators. Washington, D.C.: Island Press, 1996. Janzen, Daniel H., and Paul S. Martin. “Neotropical anachronisms: The fruits the gomphotheres ate.” Science 215 (1982): 19–27.

flowers) to the female organs (female cones of conifers, or the pistils of flowers). The pollen lands upon the surface of the female cone or the stigma of the flower’s pistil and grows a tube down to the immature seed. In the ancestors of flowering plants, pollen was carried from one plant to another primarily by the wind. Modern conifers continue to rely on wind pollination. The earliest flowering plants relied on

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120 coevolution  120 animals (usually insects) to carry pollen from one plant to another. Very soon after the evolution of these early insect-pollinated flowers, some flowering plants reverted to wind pollination, and many flowering plants today rely on wind pollination. The evolution of wind pollination is not coevolution, since the wind is not an organism. Flowers that rely on wind pollination cannot control where their pollen goes and have characteristics such as the following. ●●

●● ●● ●●

Their petals are reduced or absent, as petals would only get in the way of the transportation of pollen by the wind from stamens of one flower to pistils of other flowers. They produce massive amounts of pollen, since most of the pollen misses its target. The stigmatic surfaces are large, to increase the chance of the pollen hitting its target. The flowers of many wind-pollinated trees, such as oaks, open in the early spring, before the leaves of deciduous plants emerge. Otherwise, leaves would slow down the wind, and pollen might stick, uselessly, to the leaves.

In contrast, flowers that are pollinated by animals have characteristics such as the following. ●● ●● ●● ●●

Their petals and nectar attract the animals. They produce less pollen, since animals can carry the pollen directly to another flower. The stigmatic surfaces are not usually large. Their flowers may open at a later time during the growing season.

Flowers often attract pollinators with a variety of rewards: Nectar is high in calories; pollen is a high-protein food; in some cases, flowers in cold climates offer a warm spot (by concentrating sunlight and blocking wind) for the pollinators to get in from the cold. In some cases, flowers produce extra pollen that is sterile and intended specifically to feed the pollinators. In many cases, flower characteristics attract and offer rewards to specific kinds of pollinators. Red tubular flowers, such as those of trumpet creepers, Campsis radicans, attract hummingbirds, whose long beaks and tongues fit into the tube, while they exclude animals that are too large to crawl into the tube and do not have long tongues (for example, bumblebees). Hummingbirds may have evolved a preference for red because it helped them find flowers, and the flowers may have evolved red pigment production because it brought pollinators to them. In contrast, red flowers do not strongly attract bees, which cannot see red. Moths and butterflies have

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first entry long tongues and often visit tubular flowers. Some flowers have closed petals and a landing platform; only large bees can push their way into the flower. In these and many other examples, coevolution has produced characteristics that benefit both species: The pollinators have evolved the ability to find and exploit these flowers as food sources, and the flowers benefit from being pollinated. In other cases, flowers attract pollinators by deception. Many species of flowers have dark reddish petals and produce the putrid scent of rotten meat, which attracts flies as pollinators. A few species of orchids attract male wasps by imitating the appearance and chemical characteristics of female wasps. The male wasps attempt to mate with the flower but succeed only in either getting pollen stuck to them from stamens or rubbing pollen off onto the stigmas. In these examples, the flowers benefit, but the insects do not. It is questionable whether these adaptations were produced by coevolution. Natural selection favored flowers that most closely imitated dead meat or female wasps. However, the evolution of the flies and wasps was primarily influenced by the search for food and mates, not by the flowers. In some cases, insects obtain nectar from flowers without pollinating them. Some flowers have tubes that are too small for large bees to enter, but the large bees chew a hole from the outside and drink the nectar. Such nectar thieves are quite common. Whether or not the pollinator benefits from the relationships, the pollination relationships just mentioned are specific. Only certain wasp species will respond to the orchid that fakes the female wasp. While the specificity is not always absolute (hummingbirds sometimes drink nectar from flowers that are not red, and bees sometimes visit red flowers), it does assure that, in most cases, the animal carries pollen from one flower to another flower of the same species. An indiscriminate animal carrying pollen to a flower of a different species would not benefit either of the plants. In fact, it would not even be a pollinator. Coevolution that leads to specific pollination relationships rather than indiscriminate ones helps the plants transfer their pollen more efficiently and may help the pollinators find a more reliable food source. In other cases, flowers are open to a wider variety of pollinators. Many flowers are shallow, their stamens and pistils open to any insect that can fly or crawl in. In these cases, the plant population may be locally dense, so that pollen is seldom carried to the wrong species or the pollinators are relatively faithful to one species even when not forced to be by the flower structure.

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coevolution  121 Once coevolution had begun between flowering plants and insects 120 million years ago, at the beginning of the Cretaceous period, it resulted in an astonishing diversification of flowering plants. A floral innovation that allowed even a slight change in which insects pollinated it would cause an almost immediate isolation of the new form from the rest of the population, starting it on the road to becoming a new species of flowering plant. This is probably the reason that each flowering plant family usually contains a considerable variety of growth forms and environmental adaptations but all of its species have similar flowers: The family itself began its evolution as a partner in a new coevolutionary pollination relationship. Today there are nearly 250,000 species of flowering plants. Hymenopterans (bees and wasps) and lepidopterans (butterflies and moths) had existed since the Paleozoic era, and their diversification was not stimulated so much by flowers as the diversification of flowers was stimulated by them.

Coevolution Leading from Parasitism to Commensalism The preceding discussion focused how coevolution influenced general relationships among groups of species. Coevolution has also produced symbiotic species relationships, in which one species depends upon another. Parasitism occurs when individuals of one species (the parasite) obtain their living from individuals of another species (the host). Some parasites are occasional visitors, such as mosquitoes; some, such as lice, may live on the host a long time; some, such as intestinal worms, live inside the host; and some microbial parasites live among and even in the host cells. Parasites have a negative impact on the host, either by consuming directly from it, by consuming some of its food (as when intestinal worms harm the host’s nutrition), by producing toxic waste products (as do many bacterial and viral parasites, such as cholera and bubonic plague), or by causing the host’s own immune system to have harmful effects on the host. The evolution of parasites has been strongly influenced by the hosts. For example, the life cycles of fleas that live on rabbits are coordinated with hormone levels in the rabbits’ blood, which ensures that the young fleas hatch at the same time as the baby rabbits are born. The evolution of the hosts has been influenced by parasites; the very existence of immune systems may be considered proof of this. In contrast, a commensalistic relationship is one in which the commensal obtains its living from the host, but the host is indifferent to its presence. (This is why, according to some biologists, commensalism is not true symbiosis, but represents an intermediate condition between parasitism and mutualism.) The

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human body contains trillions of commensalistic microorganisms, primarily on the skin and in the digestive tract. In fact, there are 10 times as many bacteria as there are human cells in the human body. The commensals consume materials that the body does not need. The worst thing they do is produce disagreeable odors. They are commensalistic not out of goodwill toward humans but because the body’s defenses keep them in check. People with compromised immune systems (such as from HIV) may be infected and killed by microbes that would otherwise have been commensalistic. Coevolution may select parasites that are more effective and hosts that have adaptations that will limit, resist, or eliminate the parasite. If the host species’ evolution is successful in causing the parasite to become harmless to it, the relationship is no longer parasitism, but commensalism. Similarly, in many but not all cases, the parasites actually benefit from not harming the host; if the parasite kills the host, it has killed its habitat and must find another. Natural selection often favors the evolution of milder and milder parasites. This does not happen with parasites, such as cholera bacteria, that disperse to new hosts rapidly or impersonally (in the case of cholera, through sewage). However, when a parasite must disperse to a new host by personal contact among hosts (as with smallpox), the parasite benefits when the host remains well enough to walk around and infect other people. The ebola virus is one of the deadliest diseases known to humankind, so deadly that it has never had a chance to spread through more than a small group of people at any one time. Coevolution, therefore, can cause host species to become more resistant and parasite populations to become milder. Many diseases, such as smallpox, were evolving toward milder forms even before the introduction of modern medical practices. Some diseases have, in fact, disappeared, perhaps because the parasitic relationship evolved into a completely commensalistic one. This process, also called balanced pathogenicity, has been directly measured during the course of a disease outbreak in rabbits. Commensalism can be produced by coevolution, but once it has been attained, it does not involve coevolution any longer. Natural selection may prevent the relationship from slipping back into parasitism.

Coevolution Leading to Mutualism Another kind of symbiosis is mutualism, in which both species benefit. In some cases, the activities of commensals can evolve into mutualism. Most human intestinal bacteria are commensals. Some of them are mutualists because they provide a benefit to humans. The presence of some kinds of intestinal

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122 coevolution  122 bacteria may prevent the growth of parasitic bacteria. Some of the more than 400 species of bacteria that live in the human intestine are mutualistic: They digest some foods that the intestine by itself cannot, making as much as 20 percent more calories available for absorption. Some of these bacteria produce vitamin B, which is to them a waste product. Bacteria on the skin and in body orifices may prevent infection by parasitic bacteria and fungi. Nonhuman examples of beneficial internal microbes abound. Cows cannot digest grass; it is the bacteria in their stomachs that digest it (and get food for themselves in the process). Many termites cannot digest wood; it is the microbes in their intestines or their nests that digest it. The microbes in cow and termite guts may well have begun as parasites or commensals and evolved a mutualistic function. Insectivorous birds may benefit from associating with grazing animals in a pasture; the large animal stirs up insects that the birds eat. The bird commensals benefit, and the large animal hosts are unaffected. Some birds have evolved an extra step. They eat parasites from the skins of the large host animals, which turns the relationship into mutualism, but even this mutualism can be mixed with parasitism. Yellow-billed oxpeckers (Buphagus africanus) eat ticks from mammals in the savannas of Africa, but they also drink blood from wounds, including some that they cause. Scientists may have observed an example of coevolution in the process of turning parasitism into mutualism. Fungi infect and reduce the growth and reproduction of grasses such as Festuca arundinacea and Lolium perenne. This sounds like parasitism. The infected grass smells bad to grazing animals such as cows, which avoid it, thus benefiting the grass. The cows that fail to avoid this grass suffer numerous physical ailments and may become lame from limb damage. What began as a parasitic infection of the grass may be evolving into a mutualistic protection for the grass. Over the long term, however, the grasses infected by fungi do not appear to grow any more than do the grasses without fungi, for both the herbivores and the fungi reduce the growth of the grasses. Mutualism need not evolve through the stages of parasitism and commensalism. It may evolve from antagonistic or casual associations, as in the following examples. ●●

Big fish usually eat little fish. However, little fish can eat parasites from the big fish. If the big fish evolve behavior patterns in which they allow the little fish to come close to them, even to search around inside their mouths, and if the little fish evolve behavior

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first entry

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patterns to trust them, a mutualism may result: The big fish are relieved of their parasite load, and the little fish get food. Such cleaning mutualisms are common, especially in coral reef ecosystems. Ants crawl on many kinds of plants looking for prey. This may have the effect of helping the plant by killing its herbivores. The plant may, in turn, benefit by rewarding the ants, encouraging them to stay. Acacia trees of tropical dry forests are protected by ants, which kill herbivores and even vines that may threaten the acacias. The acacias, in turn, feed the ants with nectar and special morsels of protein and fat. In some cases, the mutualism has evolved so far that the ants and trees depend upon one another for survival. Leaf cutter ants in tropical forests cannot eat leaves, but they can eat fungi that decompose the leaves. What may once have been a casual association, in which the ants preferred molded leaves, has evolved into an intricate mutualism in which the ants gather leaves, chew them up, and raise underground fungus gardens on the compost. As with the acacias and ants, the leaf-cutter ants and fungi have evolved a mutual dependence: Neither can survive without the other. Human agriculture may have begun as a casual association between gatherers and wild plants and evolved into the biggest mutualism in the world.

Some mutualists are so intimate that they have begun the process of melding into single organisms. Zooxanthellae are single-celled algae that live in the skins of aquatic invertebrates. Nitrogen-fixing bacteria and mycorrhizal fungi live in the roots of plants, most notably many leguminous plants (beans, peas, clover, vetch, alfalfa, locust), as well as alders, cycads, and casuarinas. Riftia pachyptila, a vestimentiferan worm that lives in deep sea volcanic vents, is more than three feet (1 m) in length, but it does not eat: It has no mouth, gut, or anus. It has specialized compartments in which symbiotic sulfur bacteria live, which live off of the hydrogen sulfide from the vents and then become food for the worm. Some mutualists, such as the bacteria that obtain nitrogen in sponges, are passed from one generation of the host to another when it reproduces. Some organisms have gone all the way, melding mutualistically into unified creatures. The cells of all photosynthetic eukaryotes contain chloroplasts, and almost all eukaryotic cells contain mitochondria, the evolutionary descendants of mutualistic bacteria. In fact, the evolution of mutualism may have made the

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commensalism  123 evolutionary advancement of life beyond the bacterial stage possible. The evolutionary biologist Lynn Margulis points out that the formation of mutualisms has been a major process in the evolution of biodiversity. The evolution of adaptations to the physical environment might have produced only a few species. Just how many ways are there for a plant or an animal to adapt to desert conditions? The greatest number of evolutionary innovations, from the huge array of plant chemicals to the astonishing diversity of flowers and even the symbioses that keep human cells alive, have resulted from coevolution of organisms in response to one another. See also Essay: “Ghosts of Biodiversity Past;” biodiversity, resources for medicine; herbivory; pollination; predation; seed dispersal; symbiogenesis. Further Reading Bäckhed, Fredrik, et al. “Host-bacterial mutualism in the human intestine.” Science 307 (2005): 1,915–1,920. Barbosa, Pedro, and Ignacio Castellanos, eds. Ecology of Predator-Prey Interactions. New York: Oxford University Press, 2005. Birkle, L. M., et al. “Microbial genotype and insect fitness in an aphid-bacterial symbiosis.” Functional Ecology 18 (2004): 598–604. Currie, Cameron R., et al. “Coevolved crypts and exocrine glands support mutualistic bacteria in fungus-growing ants.” Science 311 (2006): 81–83. Dawkins, Richard, and J. R. Krebs. “Arms races between and within species.” Proceedings of the Royal Society of London B (Biology) 205 (1979): 489–511. Fisher, Jeffrey A. The Plague Makers: How We Are Creating Catastrophic New Epidemics—And What We Must Do to Avert Them. New York: Simon & Schuster, 1994. Fraenckel, Gottfried S., et al. “Effect of soybean inhibitors on growth of Tribolium confusum.” Agriculture and Food Chemistry 2 (1954): 410–411. Gill, Steven R., et al. “Metagenomic analysis of the human distal gut microbiome.” Science 312 (2006): 1,355–1,359. Janzen, Daniel H. “Co-evolution of mutualism between ants and acacias in Central America.” Evolution 20 (1966): 249–275. ———. “Why fruits rot, seeds mold, and meat spoils.” American Naturalist 111 (1977): 691–713. Kiers, E. Toby, and R. Ford Denison. “Sanctions, cooperation, and the stability of the plant-rhizosphere mutualisms.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 215–236. Koenig, Walter D., and Johannes M. H. Knops. “The mystery of masting in trees.” American Scientist 93 (2005): 340–347.

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Pichersky, Eran. “Plant scents.” American Scientist 92 (2004): 514–521. Proctor, Michael, Peter Yeo, and Andrew Lack. The Natural History of Pollination. Portland, Ore.: Timber Press, 1996. Ruby, Edward, Brian Henderson, and Margaret McFallNgai. “We get by with a little help from our (little) friends.” Science 303 (2004): 1,305–1,307. Sachs, Jessica Snyder. Good Germs, Bad Germs: Health and Survival in a Bacterial World. New York: Hill & Wang, 2007. Saikkonen, K., et al. “Fungal endophytes: A continuum of interactions with host plants.” Annual Review of Ecology, Evolution, and Systematics 29 (1998): 319–343. Scarborough, Claire L., Julia Ferrari, and H. C. J. Godfray. “Aphid protected from pathogen by endosymbiont.” Science 310 (2005): 1,781. Schoonoven, Louis M., Joop J. A. Van Loon, and Marcel Dicke. Insect-Plant Biology, 2nd Edition. New York: Oxford University Press, 2006. Sessions, Laura A., and Steven D. Johnson. “The flower and the fly.” Natural History (March 2005): 58–63. Sherman, Paul W., and J. Billing. “Darwinian gastronomy: Why we use spices.” BioScience 49 (1999): 453–463. Thomas, Frédéric, François Renaud, and Jean-François Guégan, eds. Parasitism and Ecosystems. New York: Oxford University Press, 2005. Thompson, John N. The Coevolutionary Process. Chicago: University of Chicago Press, 1994. Vega, Fernando E., and Meredith Blackwell, eds. InsectFungal Associations. New York: Oxford University Press, 2005. Wills, Christopher. Yellow Fever, Black Goddess: The Coevolution of People and Plagues. Reading, Mass.: Addison-Wesley, 1996. Wilson, Michael. Microbial Inhabitants of Humans: Their Ecology and Role in Health and Disease. New York: Cambridge University Press, 2005. Wu, Licheng, et al. “Recognition of host immune activation by Pseudomonas aeruginosa.” Science 309 (2005): 774–777.

commensalism  Commensalism is a symbiotic

relationship between two species in which the commensal derives part or all of its livelihood from the host, but without harming the host. The most abundant commensals are the microbes and small organisms that live on or in the bodies of larger multicellular organisms. Animal bodies, including human bodies, have millions of bacteria on the skin, millions of bacteria in the mouth and throat, and trillions of bacteria in the intestines. Commensalistic bacteria associated with the human body outnumber human cells 10 to one. Mites are found in the hair follicles of nearly all

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124 communities, ecological  124 human beings, no matter how thoroughly they wash. They consume oils from the follicles. Some commensals even remain in suspended animation until the host dies. The nematode Pristionchus pacificus does not become active until the beetle on which it lives has died, at which time it eats the bacteria and fungi that decompose the dead beetle. Humans are also surrounded by commensals. A mattress can have 2 million microscopic mites eating the oils and skin flakes produced by their human hosts. They are so small they can go right through pillowcases and sheets. One-tenth of the weight of a six-year-old pillow may consist of skin flakes, living mites, dead mites, and mite dung. Different portions of a multicellular body may support different ecological communities of commensals. Skin bacteria are almost entirely different from intestinal bacteria. Even the bacterial communities on the inside and the outside of the elbow differ from each other. A study of the skin of six healthy people found 182 bacterial species of 91 genera on the forearms. Only four of the species were found on all six people, and the original species were no longer present 10 months later. Some species of commensals are transient. Their populations build up quickly and are washed away. Other species are permanent and live deeply in even well-washed skin. The most common skin bacteria are in the genus Pseudomonas, which are also common in soil and water. Close ecological relationships of larger organisms can also be considered commensalistic. When vines grow on the branches of trees, their leaves may intercept the sunlight that the tree’s own leaves have not used or may grow on a dead branch; the additional weight of the vines may be negligible. The vine benefits because it does not produce much of its own woody tissue. Many bird species (most famously cattle egrets, Bubulcus ibis) follow grazing animals and eat the insects stirred up by the movement of the grazers. The birds benefit because they do not have to expend their own energy stirring up the insects. In a similar fashion, commensalistic birds may follow army ants and eat the insects stirred up by the ants. In North America, the black vulture (Coragyps atratus) is a commensalistic partner of the turkey vulture (Cathartes aura). Turkey vultures, with welldeveloped scent recognition and good eyesight, are very good at finding carrion. Black vultures do not have well-developed scent recognition, and they usually follow turkey vultures. The black vultures wait until the turkey vultures have finished eating, then clean up the leftovers. The border between commensalism and other ecological relationships is unclear and shifting. Most microbes on and in the human body are potentially parasitic; they are commensals only because the

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first entry human body defends itself from them. If the human immune system is weakened by illness, the erstwhile commensals become parasites. If the human body dies, they become decomposers. The commensalistic vines described earlier can quickly become competitors of the tree on which they grow if their leaves cast shade on the tree’s leaves, if they become too heavy, or if their roots compete with those of the tree. The dust mites described previously, living in pillows or the carpet, might be considered decomposers. They can be harmful to those people who have allergic reactions to their waste products. Consider the example of barnacles growing on whales. If the barnacles are sufficiently uncommon, the whale may not notice them, and the barnacles get a free ride to areas with new food supplies. If the barnacle populations build up on the whales, they may irritate the whale, slow it down, or even allow infections to occur. See also coevolution; mutualism; parasitism. Further Reading Fierer, Noah, et al. “The influence of sex, handedness, and washing on the diversity of hand surface bacteria.” Proceedings of the National Academy of Sciences USA 105 (2008): 17,994–17,999. ———, et al. “Forensic identification using skin bacterial communities.” Proceedings of the National Academy of Sciences USA 107 (2010): 6,477–6,481. Gao, Z., et al. “Molecular analysis of human forearm superficial skin bacterial biota.” Proceedings of the National Academy of Sciences USA 104 (2007): 2,927–2,932. Pennisi, Elizabeth. “Bacteria are picky about their homes on human skin.” Science 320 (2008): 1,001.

communities, ecological  An ecological community is all of the interacting organisms in the same place at the same time. Because the web of interacting organisms extends nearly unbroken across the entire Earth, the only well-defined community is that of the entire biosphere of Earth. (Even this has been called into question by those who claim that bacteria, called “space plankton,” can survive inside rocks thrown into outer space by asteroid impacts.) However, organisms may form recognizable clumps of interactions in which there are more interactions within the clump than between them. These clumps are ecological communities. What Are Ecological Communities? More than a century ago, ecologists such as Frederic Clements maintained that ecological communities were distinct entities (superorganisms) with their own life cycles. These communities even received

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communities, ecological  125 Latin names: A forest of Quercus oaks was a Quercetum, and a woodland of Pinus pines was a Pinetum. Ecologists such as Henry Gleason and Robert Whittaker demonstrated that each species of plant had its own distributional range. The distinction between one ecological community and another is, according to this view, gradual, rather than being discrete like the body of an organism. Strictly speaking, there is no such thing as a forest. “Forest” is the name humans give to a set of species of plants, animals, and microorganisms that grow together and interact. Animals, in particular, can be members of more than one ecological community. If a disturbance, such as a fire, wipes away a community, other species of plants, animals, and microorganisms live in the new environment created by the fire. Because of ecological changes that occur during the subsequent decades, the original set of species may, in fact, return, but it was the individual plants and animals within each species that grew back—not the forest. More recently, some ecologists have begun to reexamine the extent to which ecological communities are associations of organisms that live in the same habitat conditions. While none of them have gone back to the Clementsian view, they have emphasized the species interactions that occur much more strongly within than between communities. It is true that animals readily move from one ecological community to another, but most of them spend most of their time in one type of ecological community. The web of community interactions can even help to define the border of a community, indistinct as it is. One example is the transition from tundra to boreal or subalpine forest. The forest trees live in areas where the temperature is warm enough that their branches will not usually be killed by the winter wind and the permafrost is not near the surface of the soil. However, the trees themselves influence the environmental conditions. Their dark needles absorb sunlight and increase the temperature where they live. In this way, the boreal or subalpine community itself can increase its range northward or up a mountain. Perhaps the most realistic view of an ecological community is that it is a clump of frequent ecological interactions among species imperfectly but significantly separated from other such clumps. Adjacent ecological communities overlap in areas known as ecotones. An example is the transition from tundra to boreal or subalpine forest already mentioned. Each ecotone consists of loosely defined zones. Between a forest and grassland, for example, there is an ecotonal area dominated by saplings of shade-intolerant trees, an area influenced by the shade of the forest and litter from the trees in a way the center of the grassland is not. A terrestrial community, such as a forest, may intergrade into

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an aquatic community, such as a lake. Some plants grow in the mud at the lake margin. Others, such as cattails, sedges, and rushes, specialize in the littoral zone, in which emergent plants are rooted underwater but have their leaves and flowers primarily above the water’s surface. Each aquatic plant species specializes on a different water depth—water lilies grow farther out in the water than do cattails. Some plants live underwater or float on top of it. The plant species Hottonia inflata, for example, has finely dissected leaves that absorb dissolved carbon dioxide and bicarbonate from the water, but it floats because the peduncle (which bears the flowers) encloses a bubble of air. Ecological succession typically occurs in these ecotonal zones, such as when the wetland fills with soil and decaying plant material. Since interactions can take place on all scales, from a few inches to many miles, it is impossible to define the spatial extent of an ecological community. To a mosquito larva, a tree hole is the world, while wolves can range over a wide area, moving between forests and grasslands. For ease of discussion, this encyclopedia uses the following rough scale of community identity to define its entries: a community is large and distinct enough to be separately identified on ecological maps (see figures on pages 126 and 127). The following ecological communities have entries in this encyclopedia: ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●●

bogs boreal and subalpine forests cloud forests continental shelves coral reefs deep oceans deserts, cool deserts, polar deserts, warm grasslands and savannas marshes and swamps rivers, streams, ponds, and lakes shrublands temperate coniferous forests temperate deciduous forests temperate dry forests temperate rain forests tropical rain forests tropical seasonal forests tundra

Levels of Diversity within Communities Biodiversity within ecological communities can be considered at three scales: ●●

Alpha diversity results from the species that live and interact in a single location.

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126 communities, ecological 126 ●



Beta diversity results from the change of species that occurs over the course of a few feet or meters. Gamma diversity results from the species differences between locations that are around a mile or kilometer apart.

as these defi nitions suggest, there is no clear way to distinguish the three levels of community diversity. alpha diversity consists of the species that are in a single location. these species coexist and interact because they specialize on different ways of making a living within the community. Within a deciduous forest, for example, some trees, such as maples, dominate the canopy, while others, such as dogwoods, specialize in shaded conditions and flourish in the understory. Smaller shrubs, such as spicebush, and herbs, such as snakeroot, grow underneath them. Shrubs may specialize on using the light that reaches the forest floor in the early spring, before the forest canopy casts shade. in a field of weeds or a desert, the plant species may all receive full sunlight but dominate different layers of soil or flourish at different times of the year. in the colorado Desert of california, shrubs have deep roots, while cactuses have shallow but widespread roots. tiny wildflowers grow only during the brief spring rains and have very small root systems. the herbivorous animals may specialize on different species of plants or on eating

first entry the plants in different ways: Some chew entire leaves, some eat photosynthetic cells inside the leaves, some tap the pressurized fluid within the phloem, and some specialize on the roots of plants. the predators may also specialize. Birds may specialize on seeds or on insects. Parasites specialize on hosts to different degrees: Some parasitic wasps may search for a single species of caterpillar or leaf bud on which to lay their eggs, while mistletoe plants may grow on many different species of trees. Some animals pollinate a wide variety of plants, and others are limited to a narrow range of choices. Other animals specialize on eating fruits without harming the seeds, which they disperse to a new location. Detritivores eat dead organic matter, mostly the leaves and stems of plants. Within each general category of organism (plant, herbivore, predator, parasite, pollinator, detritivore), specialization allows individuals of a species to flourish by avoiding direct competition with other species that have a similar way of making a living. each location within each general type of ecological community has its own unique set of species interactions, which is constantly changing over the seasons and over the years. another way in which species coexistence can enhance alpha diversity is through mutualism. Some species create habitats for other species with which they have a mutually beneficial ecological relationship. although mites are frequently found on plants, some leaves produce acarodomatia (mite-houses)

This world map shows the approximate locations of the major ecological communities.

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communities, ecological  127

This map of the United States shows the approximate locations of the major ecological communities.

that encourage the presence of a resident population of mites, which may help to protect the leaves from herbivore damage. Beta diversity consists of species that inhabit different, adjacent microhabitats. Every habitat, such as a forest or grassland, contains microhabitats, which usually are home to some species that are not found in other parts of the habitat. These microhabitats are considered part of the ecological community, since individuals of many species move in and out of them freely. One or more microhabitats can be created by something as simple as a large rock. A single rock can create a strikingly different set of environmental conditions upon which some plant and animal species may depend. A large rock in a forest, for example, is likely to discourage the growth of large trees, and the result is a sunny, warm, dry microhabitat, which lizards prefer to the surrounding forest.

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On the other hand, crevices in rocks may be cooler and wetter than the surrounding forest. In the Black Hills of South Dakota, for example, ponderosa pines cast moderate shade on the relatively dry forest floor. Prickly pear cactus lives in the sunny spots on these rocks, right alongside ferns that specialize in the shaded crevices. Neither the cacti nor the ferns could thrive in the surrounding soil. Rocks also allow very little soil accumulation, and small plant species with shallow roots (or mosses and lichens that have no roots at all) can grow on rock surfaces and in crevices without interference from the roots of larger plants. A large rock in dry grassland may have the opposite effect on environmental conditions by creating shaded, moist conditions otherwise absent from the grassland. Consider granite boulders in the foothills of the Sierra Nevada of California. The grassland is dominated by grasses and forbs that flourish briefly

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128 communities, ecological  128 before the onset of the long summer drought, but some grass and forb species are found only near or on the rocks. The tiny succulent plant Crassula erecta grows only in the shallow pockets of soil created by mosses, while the tiny grass Lamarckia aurea grows in slightly deeper pockets of soil adjacent to them. The wildflower Mimulus dudleyi grows only in the shallow crevices on these rock surfaces. The only shade-tolerant wildflower species in these grasslands, Pholistoma membranaceum, grows in the shade between boulders. Another wildflower, Phacelia cicutaria, grows almost nowhere else except at the bases of boulders, where water running off the rock surfaces creates a zone of increased moisture. In these same foothills, blue oaks (Quercus douglasii) grow only on hillsides where the boulders are common. Researchers have shown that grasses use water from the soil and can thereby cause oak seedlings to die. Perhaps the oaks grow around boulders because grasses do not grow well there, and the boulders allow water and tree roots to penetrate deeper into the soil. Grazing mammals eat oak leaves and damage seedlings. Perhaps the animals do not graze in boulder fields as much as on smooth, grassy hillsides. Edaphic conditions refer to the material in which a plant grows, usually but not always soil. It can also refer to rocks on which plants grow or the floating mat of moss that covers a bog. Normal, rich soil is a complex structure of many components. Edaphic conditions, such as unusual soils, can cause an almost entirely different ecological community to dominate over a small area. Rocky or sandy soils are both drier and poorer in nutrients than normal soils. In Michigan, areas of rich loam soil alternate with poor sandy soils left by glaciers when they melted. Beech-maple forests dominate the rich soils, while jack pines dominate the sandy soils. Jack pines are more commonly found in the poorer soils of the boreal forest. Hemlocks (Tsuga canadensis) are often found on poor, rocky soils in the eastern deciduous forest. In parts of Illinois, normal soils also alternate with sand deposits. Black oaks dominate the normal soils, but the sand deposits are so nutrient-poor and dry that no trees at all grow on them. Instead, grasses that are more typical of the western prairies and even beavertail cacti grow there. Along the coast of northern California, tall conifers such as redwoods dominate the normal soils. In some small areas, the soils are very shallow and acidic. In these places, rather than tall redwoods, there are “pygmy forests” of short bishop pines, tiny cypresses, and plants such as rhododendron bushes that are typical of acidic soils. The trees resemble bonsai trees because, just as bonsai trees do, they grow in very poor soils.

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first entry Some soils contain toxic minerals that inhibit the growth of most plants. For example, soils derived from serpentine rock contain high levels of chromium and nickel. These rocks resemble those of Earth’s mantle rather than the continental crust, and they have been lifted up by the movement of the continental plates. Therefore, serpentine deposits are common near California’s San Andreas Fault. Some species of plants, or varieties of plants within species, are able to grow in these toxic soils. There is a cost to this adaptation, however. These plants grow more slowly in normal soils than do normal plants. This is what restricts such plants to the patches of toxic soil. Another unusual soil is diatomaceous earth, an almost perfectly white, powdery soil formed from rock that is made of the shells of billions of diatoms (single-celled protists) that accumulated on the bottoms of ancient oceans. In the Purísima Hills north of Lompoc, California, large deposits of this white dirt support a forest of bishop pines (Pinus muricata). Although this tree species is common (maintained by a fire cycle) farther north from this location, it is found nowhere else in the immediate vicinity. The surrounding community is chaparral, which also depends on a fire cycle. The soil factors that allow this unusual plant community have not been identified. Some microhabitats are created by very smallscale disturbances. In the shortgrass prairies of western North America, grass roots densely pack the soil, and other plants seldom have a chance to grow among the grasses. When bison or prairie dogs disturb the grasses, other species of plants can grow there, such as Sphaeralcea coccinea. In the badlands of the South Dakota grasslands, soil erosion may also reduce competition from grasses enough that wildflowers such as Oenothera caespitosa can grow. Even a hole in a tree can create a microhabitat. Many animal species depend on tree holes for parts of their lives. Birds may require these holes for nesting, while insect larvae may be unable to live anywhere else. While animals (due to their mobility) specialize on microhabitats less than do plants, the diversity of animal species may depend heavily on the presence of microhabitats that interrupt the dominant species and create openings where they can locate a greater range of food plants and where prey may be easier to capture. Gamma diversity in a community results from smaller, adjacent ecological communities. They are mixed together enough that it is not useful to distinguish them as separate communities. These differences usually result from major features of the landscape, such as mountains. In the North-

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communities, ecological  129

Oak trees (Quercus douglasii) grow on the northeastfacing slopes of the foothills of the Sierra Nevada in California, while grasses, which can tolerate drier conditions, grow on the southwest-facing slopes.  (Stanley A. Rice)

ern Hemisphere, the northeast slopes of mountains receive less direct sunlight and are therefore cooler and wetter than the southwest slopes. In many cases, a forest may grow on the northeast slope, while grassland or desert dominates the southwest slope of the same mountain (see figure). Where two watersheds come together, wetter conditions may allow the growth of plant species that could not tolerate drier conditions. In the chaparral of the coastal mountains of California, live oaks (such as Quercus agrifolia) and the California bay (Umbellularia californica) are found primarily in such conjoined watersheds, both because of the greater availability of soil moisture and the fact that fires, which are essential for the maintenance of the chaparral, are less likely to burn in these slightly wetter areas. Gamma diversity intergrades seamlessly into the differences between ecological communities. Because of the striking environmental differences between water and land, aquatic habitats are usually considered separate communities, even when they are very small. A single mountain produces cooler, wetter conditions on the northeast side than the southwest side, but it usually takes a whole range of mountains to produce a rain shadow (see figure on page 130), in which most of the precipitation falls on the windward slopes of the mountains, or to create temperature differences large enough to allow the persistence of subalpine forests and alpine tundra. Communities may differ strikingly from one another not only in the number of species but in their relative abundances. Typically, communities that have few species (occupying disturbed or extreme habitats) are dominated by one or a few species, while the species within diverse communities are much more equal in their relative abundances.

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Individuals within each species are often located at random with respect to one another. Departures from random distribution reveal some underlying community process. Most often, individuals within a species may be clumped together— that is, they tend to be found close to one another more often than they are distant from one another. This pattern could result from limited dispersal of offspring, such as seeds that do not travel far from the parent plant, or from specialization on patchy resources in the habitat, such as tree seedlings clumping in a patch of sunlight on the forest floor. Occasionally, individuals within a species are more evenly dispersed through the community than one would expect from a random pattern. One example of this is the apparently regular spacing of desert shrubs. This pattern may result from competition between the root system of each shrub and that of the next shrub for access to scarce water and nutrient resources. Within ecological communities, one species may influence the distribution patterns of another. There is disagreement regarding how important competition is in determining the species composition of ecological communities. The ecologist Steven Hubbell studied the distribution of tree species on Barro Colorado Island in the Panama Canal area and found that they were randomly distributed with respect to one another; dispersal, speciation, and extinction were sufficient to explain which kind of tree grew where. In other cases, however, competition plays a vital role in determining which species are present in a community. During the process of ecological succession, long-lived, shade-tolerant plants that produce fewer, larger offspring (seeds) replace shortlived, shade-intolerant plants that produce more, smaller offspring due to the competitive superiority of the former. The vital role of competition in the successional development of ecological communities, however, applies more to the general characteristics of the plants rather than to the species of the plant. The ecologist Tadami Fukashi and colleagues experimentally manipulated the species composition of grasslands, then allowed secondary succession to occur. The result was a convergence upon similar types of woodlands, but each woodland had its own set of species. Competition, therefore, often influences the set of traits but not the actual species composition of the species that make up an ecological community.

Ecological Interactions in Communities Ecological interactions (such as herbivory and predation) not only influence where many of the species live within an ecological community, but the populations of one species can influence those of

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130 communities, ecological  130

first entry

The Sierra Nevada create a rain shadow in California. Most of the rain and snow falls on the Pacific slope, creating lush meadows and forests of giant sequoias (right). After the wind has reached the eastern side of the mountains, it is dry, and desert conditions prevail, as seen in this eastward view from the top of Mount Whitney (left). Both the meadow and the desert are at about the same elevation.  (Stanley A. Rice)

another species. The result may be a trophic cascade. Predators may reduce the populations of herbivores on which they prey; in turn, the plants that would otherwise be eaten by the herbivores can grow more. Predators can therefore increase the growth of plants. In general, a trophic cascade occurs when an organism at one level of the food chain promotes the growth of an organism two levels below it. The result is that species within an ecological community appear to keep one another under control. This concept is often called the “balance of nature.” The balance of nature, though real, is very approximate, and populations of wild species (especially predators and prey) experience large fluctuations. The web of relationships (trophic, competitive, symbiotic) in an ecological community can be astoundingly complex. In the Origin of Species, Charles Darwin provided an example of the complex web of relationships found in even the “simplest” ecological community, a pasture in England. Red clover depends upon bumblebees for pollination, and therefore the production of seeds. Field mice

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destroy bumblebee nests, and cats eat mice. Darwin concluded, Hence it is quite credible that the presence of [cats] in large numbers in a district might determine, through the intervention first of mice and then of bees, the frequency of certain flowers in that district!

In this manner, Darwin described the ecological complexity within which all evolution occurs. See also biodiversity, patterns of; bogs, life in; boreal and subalpine forests; cloud forests; competition, ecological; continental shelves, biodiversity on; coral reefs; deep oceans, biodiversity in; deserts, cool; deserts, polar; deserts, warm; grasslands and savannas; herbivory; marshes and swamps; mutualism; parasitism; pollination; rivers, streams, ponds, and lakes; shrublands; succession, ecological; temperate coniferous forests; temperate deciduous forests; temperate dry forests; temperate rain forests; tropical rain

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competition, ecological  131 forests and deforestation; tropical seasonal forests; tundra. Further Reading Amarasekare, Priyanga. “Spatial dynamics of foodwebs.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 479–500. Begon, Michael, Colin R. Townsend, and John L. Harper. “The nature of the community: Patterns in space and time.” Ch. 16 in Ecology: From Individuals to Ecosystems, 4th ed. Oxford: Blackwell Publishing, 2006. Black, R. Alan, and Richard N. Mack. “Tsuga canadensis in Ohio: Synecological and phytogeographical relationships.” Plant Ecology 32 (1976): 11–19. Bukovinszky, Tibor, et al. “Direct and indirect effects of resource quality on food web structure.” Science 319 (2008): 804–807. Clarke, K. R., and R. M. Warwick. “Quantifying structural redundancy in ecological communities.” Oecologia 113 (1998): 278–289. Côté, Steeve D., et al. “Ecological impacts of deer overabundance.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 113–148. Dunne, Jennifer A., et al. “Compilation and network analyses of Cambrian food webs.” Public Library of Science Biology 6 (2008): e102. Available online. URL: http:// www.plosbiology.org/article/info:doi/10.1371/journal. pbio.0060102. Accessed August 4, 2011. Farber, Paul Lawrence. Finding Order in Nature: The Naturalist Tradition from Linnaeus to E. O. Wilson. Baltimore: Johns Hopkins University Press, 2000. Finke, Deborah L., and William E. Snyder. “Niche partitioning increases resource exploitation by diverse communities.” Science 321 (2008): 1,488–1,490. Fukashi, Tadami, et al. “Species divergence and trait convergence in experimental plant community assembly.” Ecology Letters 8 (2005): 1,283–1,290. George, L. O., and F. A. Bazzaz. “The fern understory as an ecological filter: Emergence and establishment of canopy tree seedlings.” Ecology 80 (1999): 833–845. Gilbert, B., and M. J. Lechowicz. “Neutrality, niches, and dispersal in a temperate forest understory.” Proceedings of the National Academy of Sciences USA 101 (2004): 7,651–7,656. Gordon, Doria R., and Kevin J. Rice. “Competitive suppression of Quercus douglasii (Fagaceae) seedling emergence and growth.” American Journal of Botany 87 (2000): 986–994. Hairston, Nelson G., Frederick E. Smith, and Lawrence B. Slobodkin. “Community structure, population control and competition.” American Naturalist 94 (1960): 421–425. Hubbell, Steven P. The Unified Neutral Theory of Biodiversity and Biogeography. Princeton, N.J.: Princeton University Press, 2001.

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Kraft, Nathan J. B., Renato Valencia, and David D. Ackerly. “Functional traits and niche-based tree community assembly in an Amazonian forest.” Science 322 (2008): 580–582. Kuchler, A. W. Potential Natural Vegetation of the Conterminous United States. American Geographical Society, Special Publication No. 36, 1964. Lankau, Richard A., and Sharon Y. Strauss. “Mutual feedbacks maintain both genetic and species diversity in a plant community.” Science 317 (2007): 1,561– 1,563. Petraitis, Peter S., et al. “Experimental confirmation of multiple community states in a marine ecosystem.” Oecologia 161 (2009): 139–148. Slobodkin, Lawrence B., Frederick E. Smith, and Nelson G. Hairston. “Regulation in terrestrial ecosystems, and the implied balance of nature.” American Naturalist 101 (1967): 109–124. Stokstad, Erik. “On the origin of ecological structure.” Science 326 (2009): 33–35. Strauss, Sharon Y., and Rebecca E. Irwin. “Ecological and evolutionary consequences of multispecies plant-animal interactions.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 435–466. Thébault, Elisa, and Colin Fontaine. “Stability of ecological communities and the architecture of mutualistic and trophic networks.” Science 329 (2010): 853–856. Volkov, I., et al. “Neutral theory and relative species abundance in ecology.” Nature 424 (2003): 1,017–1,028. Wardle, D. A. “Ecological linkages between above­ ground and belowground biota.” Science 304 (2004): 1,629–1,633. Whittaker, Robert H. Communities and Ecosystems, 2nd ed. New York: Macmillan, 1975.

competition, ecological  Ecological competition occurs when organisms use similar resources and when these resources are in limited supply. Competition is an essential component of natural selection. Charles Darwin called it “struggle for existence,” a phrase now seldom used because competition need not be a visible struggle. Competition may result in some individuals growing larger and leaving more offspring than others, and it may result in the deaths of some individuals. Darwin explained how competition results in natural selection, in which the population evolves to resemble the successful competitors. Ecologists generally distinguish between two mechanisms of competition. When a flush of new resources becomes available, populations may grow quickly, and the winners of this kind of competition (scramble competition) are those that can preempt the resources most quickly. When a flush of resources

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132 competition, ecological  132 is not available, some individuals can do something that inhibits the growth of other individuals (interference competition). Examples of interference competition include the production of poisons by plants that enter the soil (allelopathy) and aggression of one animal against another. Competition can occur between individuals within populations of the same species (intraspecific competition). Food can be in short supply in animal populations, as can access to light and soil in plant populations. The shortage of resources contributes to the deaths of most offspring in most populations of plants and animals. Particularly in plant populations, the individuals that (by good luck or superior characteristics) obtain more resources can grow much larger than individuals that do not. Intraspecific competition can also occur for access to mates. Since plants have more plasticity of growth than do animals, dense plant populations frequently contain a large number of small individuals, while in animal populations these individuals would probably die. While very high densities can have negative effects on individuals within populations, there can also be beneficial effects of moderate crowding. While a large population of prey might be more easily spotted by a predator, it might also be able to defend itself more effectively than an isolated individual. For example, a herd of animals can carry out defensive maneuvers to ward off predators and protect the young. Among plants, an isolated individual in a bare field might suffer the consequences of soil erosion and hot dry winds, from which a moderate density of other plants might be able to shield it. The benefits of moderate population density relative to low population density were first pointed out by the ecologist Warder C. Allee and are called the Allee effect. Intraspecific competition is often more severe than competition between members of different species, which is called interspecific competition. This is because individuals within the same species may use almost exactly the same resources, while members of different species use different resources. Different species can coexist and avoid competition not only by using different resources but by using the same resources differently. This idea was conceptualized by the ecologist G. Evelyn Hutchinson in the 20th century as an “n-dimensional hyperspace.” Each individual uses numerous resources, and each of these resources can be represented as an axis in a multidimensional hyperspace. Such a conceptual hyperspace is most commonly called a niche. Coexistence is possible if different species occupy niches that do not overlap much. The application of this concept has been limited, however, because no species and no individual occupies an unchang-

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first entry ing niche of resources. Phenotypic plasticity allows organisms to adjust to the availability or the shortage of resources, within their genetic limits. Plants that grow best in bright light can adjust their chlorophyll production and leaf area in a way that allows them to survive in shade. Predators may specialize on a certain type of prey but can switch to another if the preferred prey population becomes critically small. Even broad categories such as herbivore and carnivore have a certain amount of flexibility. Most carnivores are actually omnivores that can substitute plant sources for scarce meat to a certain extent. It would surprise most people to learn that herbivores can become carnivores if the opportunity presents itself. People who raise chickens know that they have to use double layers of wire to keep deer from eating the chicks. All of these examples of flexibility indicate that hyperspaces and niches are diffuse concepts and therefore of limited use in explaining interspecific competition. Among the ways that species that use the same resource may reduce the degree of competition among them are: ●●

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In a dense mixture of several plant species, individuals of some species (for instance, of larger plants) may grow faster than and cast shade over the smaller plants of other species. Evolutionary adaptations, however, can allow some of the smaller plants to either avoid or tolerate competition. For example, some of the smaller plant species may have evolved specialized characteristics of shade tolerance. They can therefore survive and reproduce in the shade of the larger plants, rather than competing with them for the light. Alternatively, the smaller plants may become active earlier in the spring and complete most of their growth and reproduction before the larger plants have grown up and cast shade over them. Consider a certain mixture of plant species in which all the species depend on the same pollinators. If these plant species bloomed simultaneously, not only might there not be enough pollinators to visit all of them, but the pollinators might transfer pollen among rather than within species. If each plant species blooms at a different time, however, both of these competition-related problems are avoided. Lions, hyenas, and vultures all eat wildebeest meat. They avoid competition, however, because the lion kills the wildebeest and eats first, the hyenas clean up the leftovers, and vultures consume the rotting meat the

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competition, ecological  133 hyenas do not want. Some biologists speculate that early species of humans, such as Homo ergaster, avoided competition with lions and hyenas because they used stone tools to break open bones and consume bone marrow from animals killed by lions, after the hyenas had finished with them. A species that competes with another for resources may benefit from making the resources unfit for use by the competing species. For instance: ●●

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Many species of plants (such as walnut trees and California sage bushes) release toxic chemicals into their immediate environment. In some cases, these toxic chemicals (allelochemicals) may inhibit the growth of other plants. Bacteria and fungi may release toxic chemicals as they putrefy foods, thereby preventing animals from consuming the food items upon which they are growing. This is the principal reason that meats and fruits smell bad when they rot: The bacteria and fungi are protecting themselves by preventing animals from eating the food in which they are already living.

Sometimes, competition can displace individuals of a species from their optimal habitat into one for which they are not as well suited. This occurs because competition is usually most intense where resources are most abundant, not where they are most scarce. Three examples follow. ●●

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In general, competition is stronger among species in tropical rain forests than in temperate forests and in temperate forests than in boreal forests. In many cases in the Northern Hemisphere, northern species will survive in southern climates if they are transplanted and if they are protected from competition; their southern distribution is limited by competition. In contrast, the northern distribution of most Northern Hemisphere species is limited by the ability to survive cold winter conditions. Barnacles that live on rocks in the intertidal zone of the seashore must close their shells and cannot obtain food while exposed to low tide. The lower portion of the intertidal zone is inundated by ocean water more of the time than the upper portion; for the barnacle species living on rocks, the lower portion of the zone represents higher resources. Research by the ecologist Joseph Connell

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●●

showed that Balanus barnacles dominate the lower intertidal; they cannot survive well in the upper intertidal zone, but they are the superior competitors in the lower intertidal zone. Chthamalus barnacles dominate the upper intertidal, even though they survive well when transplanted into the lower zone and are protected from competition. For both kinds of barnacles, dry conditions determine the upper limit of growth, and for Chthamalus, competition determines the lower limit of growth. The knotweed Polygonum pensylvanicum grows in recently disturbed areas in the midwestern United States. Living in a disturbed area is itself a way of escaping competition. The knotweed, however, escapes competition from other weeds by growing in wet areas that other weeds cannot tolerate as well. When grown in isolation, knotweeds prefer the same moderately moist conditions that the other weeds prefer, but it cannot compete with them.

Interference competition may perpetuate the effects of a chance event. In the shade of boulders or of live oaks in the arid hills of Southern California, populations of the herb Pholistoma auritum may become established. Once established, this herb produces allelochemicals that inhibit the growth of grasses that commonly grow in the shade of oak trees. The initial establishment of the population under some oaks and not under others may have been a chance event. Competition can also cause a species to use its resources in a way that is not optimal. Many fruits entice animals to eat them and to disperse their seeds to new locations. They do this by making the fruits soft, sweet, colorful, and flavorful. The fruits have these characteristics only after the seed is mature. Plants discourage animals from eating unripe fruits by making these fruits hard, green, and distasteful. However, frugivorous animals that consume the fruits first will get more food resources than an animal of the same or different species that waits until the fruits are fully ripe. Frugivorous animals therefore frequently consume fruits that are not fully ripe. In some cases, as with parrots, they need to eat dirt, which helps to inactivate toxins from the unripe fruits. Recurring disturbances can maintain conditions in which some species remain free from competition for long periods of time. One common example is an overgrazed pasture. In the south central United States, weeds such as milkweed (Asclepias viridis), spurge (Euphorbia marginata), and bull nettle (Cnidoscolus texanus) would normally be smothered by

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134 competition, ecological  134 competition from grasses. Cattle will not eat these plants, which are either poisonous or have irritating hairs. The cattle eat the grasses, which liberates resources that the weeds use. One of the resources for which there is the most competition is access to mates. This competition leads to sexual selection, a process also first described by Darwin. Many species of birds have evolved astonishing coloration and courtship behaviors, and primate species have evolved intricate social interactions, all as mechanisms that reward individuals most successful in the competition for mates. Even plants compete for mates. In many plant species that have separate male and female individuals (such as cottonwoods and hollies), the male flowers open earlier than the female flowers. The first male flowers to open after the female flowers may be able to pollinate a large number of them. The risk of being the first male flower to open is that the flower may open too early. Competition has contributed to the evolution of biodiversity also by allowing the evolution of species that tolerate harsh conditions. There are many thousands of species that tolerate cold, dry, salty, or toxic conditions, where they encounter less competition. Examples range from desert kangaroo rats, which obtain nearly all their moisture from the dew that condenses on the plants that they eat, to Tidestromia oblongifolia, a plant that lives nearly alone in the bottom of Death Valley, to fishes that live in water so cold they are supercooled and run the risk of freezing solid if they touch a rock. The champions are the extremophile microbes. Some algae live in salt slush, while many bacteria live in superheated water or extreme acidity or tolerate high levels of nuclear radiation. Although they appear simple, extremophiles have amazing biochemical adaptations. One reason they do this is that they have persisted in those places from the Archaean era, when the entire Earth had those conditions, but they also persist because it allows them an escape from competition. While competition, or the avoidance of it, has stimulated the evolution of many species, it can also prevent evolution. In a forest with woodpeckers, any other kind of bird that attempts to make a living by extracting insects from inside tree bark may have a difficult time competing with the woodpeckers. On the Galápagos Islands, however, there are no woodpeckers. One of the species of Darwin’s finches, the woodpecker finch, uses cactus spines to extract insects from bark. It has evolved into a new species, with its own “niche,” because the woodpecker way of making a living was an unfilled occupation in the natural economy of the islands. The Galápagos Islands are a laboratory of evolution

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first entry precisely because the immigrant species have been free from competition long enough to evolve new adaptations. Because organisms specialize on different sets of resources at different times, the resources of the biological world are used more efficiently than would be the case if all species competed for exactly the same resources. Some species live on the resources that other species have left. The avoidance of competition allows the world to have a greater weight, number, and diversity of organisms than it would otherwise have. However, each organism specializes on its peculiar set of resources not in order to help the world but to maximize its own reproductive success or fitness.

Competition and Ecological Communities Disagreement continues on the extent to which competition influences the species composition of entire ecological communities. Can competition actually keep some species out of an ecological community? The evolutionary scientist Jared Diamond studied birds on islands in Southeast Asia and determined that the black honey-eater (Myzomela pammelaena) did not coexist with the black sunbird (Nectarinia sericea) on the same islands. He claimed that there are “assembly rules” that determine which species are compatible and which are not. If two species (such as these two birds) are too similar in the way they obtain resources, one will out-compete the other. In contrast, the ecologist Daniel Simberloff said that the distribution of most bird species on these islands was random with respect to one another. Diamond’s response was that although the initial colonization of each island by any bird species may have been a random event, subsequent competition eliminated inferior competitors as well as newly arrived species on an island that already contained a species too similar to it. One ecological process that would seem to be largely dependent on competition is ecological succession. The species that dominate ecological communities late in the process of succession are mostly the superior competitors, yet there is also a random element in this process. The ecologist Tadami Fukashi and colleagues manipulated experimental grasslands and allowed them to undergo secondary succession. All the fields showed the same pattern of convergence upon forests (dominance by large, longlived, shade-tolerant plants), but the actual species composition of the resulting forest depended strongly upon the initial composition of the grassland. They concluded that there were competition-based assembly rules for plant traits but not for plant species. In many cases, the species that first colonizes a new habitat—for example, a newly created volcanic

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conifers  135 island—is the winner in competition against species that arrive later, even if these species are not as similar to one another as black honey-eaters and black sunbirds. The ecologist Peter Petraitis and colleagues have shown that rocky seashores in Maine can be dominated either by seaweeds or by mussels, depending on which of them were able to colonize newly exposed rock surfaces more quickly. The winner in ecological competition is, therefore, frequently the species that arrives first. See also communities, ecological; natural selection. Further Reading Bais, H. P., et al. “Allelopathy and exotic plant invasion: From molecules and genes to species interactions.” Science 301 (2003): 1,377–1,380. Connell, Joseph H. “The influence of interspecific competition and other factors on the distribution of the barnacle Chthamalus stellatus.” Ecology 42 (1961): 710–723. ———. “Diversity and the coevolution of competitors, or the ghost of competition past. Oikos 35 (1980): 131–138. ———. “On the prevalence and relative importance of interspecific competition: Evidence from field experiments. American Naturalist 122 (1983): 661–696. ———. “Apparent versus ‘real’ competition in plants.” In Perspectives on Plant Competition, edited by J. B. Grace and David Tilman, pp. 9–26. New York: Academic Press, 1990. Diamond, Jared M. “Assembly of species communities.” In Ecology and Evolution of Communities, edited by Martin L. Cody and Jared M. Diamond, pp. 342– 444. Cambridge, Mass.: Harvard University Press, 1975. Ebert, E., et al. “Dose effects and density-dependent regulation in two microparasites of Daphnia magna.” Oecologia 122 (2000): 200–209. Fukashi, Tadami, et al. “Species divergence and trait convergence in experimental plant community assembly.” Ecology Letters 8 (2005): 1,283–1,290. Gause, G. F. The Struggle for Existence. Baltimore: Williams and Wilkins, 1934. Hutchinson, G. Evelyn. “Concluding remarks.” Cold Spring Harbor Symposium on Quantitative Biology 22 (1957): 415–427. Janzen, Daniel H. “Why fruits rot, seeds mold, and meat spoils.” American Naturalist 111 (1977): 691–713. Muller, Cornelius H. “The role of chemical inhibition (allelopathy) in vegetational composition.” Bulletin of the Torrey Botanical Club 93 (1966): 332–351. Parker, V. Thomas, and Cornelius H. Muller. “Allelopathic dominance by a tree-associated herb in a California annual grassland.” Oecologia 37 (1979): 315–320.

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Parrish, Judy A. D., and Fakhri A. Bazzaz. “Underground niche separation in successional plants.” Ecology 57 (1976): 1,281–1,288. Petraitis, Peter S., et al. “Experimental confirmation of multiple community states in a marine ecosystem.” Oecologia 161 (2009): 139–148. Reeve, J. D., et al. “Scramble competition in the southern pine beetle, Dendroctonus frontalis.” Ecological Entomology 23 (1998): 433–443. Stoll, P., and D. Prati. “Intraspecific aggregation alters interspecific interactions in experimental plant communities.” Ecology 82 (2001): 319–327. Stowe, L. G. “Allelopathy and its influence on the distribution of plants in an Illinois old-field.” Journal of Ecology 67 (1979): 1,065–1,085. Watkinson, A. R., and J. L. Harper. “The demography of a sand dune annual: Vulpia fasciculata. I. The natural regulation of populations.” Journal of Ecology 66 (1978): 15–33.

conifers  Conifers are seed plants that produce

pollen in staminate (male) cones and seeds in pistillate (female) cones. A cone is a compact branch that produces short, thick leaves called bracts, underneath which pollen or seeds develop (see figure on page 136). The terms male and female strictly refer to the pollen and to the unfertilized seeds. Conifers are trees or shrubs, not vines or herbaceous plants. Conifers are one of the evolutionary lineages, along with cycads, ginkgoes, and Gnetales (and some extinct lineages) often considered to be gymnosperms (Greek for naked seed), so called because the seeds are not completely surrounded by parental tissue while they develop. Conifers usually produce female cones near the tips of branches and near the top of the tree and male cones farther back on the branch or nearer to the base of the tree. This arrangement maximizes the chances for the wind to carry pollen from the staminate cones of one tree to the pistillate cones of another. If the staminate cones were above the pistillate cones, most of the pollen would fall on the pistillate cones of the same tree. Conifers are pollinated by wind. Most conifers have needlelike or scalelike leaves. They evolved during the Mesozoic era in relatively cold and dry regions, and they still live in such places, though they are not found in deserts. Their small, thick leaves expose relatively little surface area to desiccation. This is an especially important adaptation during the long, cold winters that most conifers experience, for example in the boreal and subalpine forests. Needlelike leaves also absorb light from all directions, which may also be useful for trees that grow in mountainous areas with many exposed rock surfaces. These leaves have a photosynthetic rate

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Pines, such as these ponderosa pines in the Black Hills of South Dakota (Pinus ponderosa), produce pollen in male cones (left) and seeds in female cones (right, here shown at their pollen-receptive stage).  (Stanley A. Rice)

about half that of the thin, broad leaves found on deciduous trees. Over a leaf’s lifetime, however, an evergreen leaf with a low photosynthetic rate may produce as much food as a deciduous leaf with a high photosynthetic rate. Conifers reproduce slowly. When the staminate cones release pollen, wind blows some of it to small, tender, purplish pistillate cones of another tree. The pollen grains germinate, grow tubes into the pistillate cone tissue, penetrate the ovules (immature seeds) inside, and deposit a sperm nucleus that fuses with the egg. The growth of the tubes takes about a year, and the eggs are not fertilized until the pistillate cone has grown to be much larger and green. Only in the third year do the pistillate cones become hard and brown, at which time the bracts open and release mature seeds into the wind. Some conifers have undergone coevolution with birds such as nutcrackers that pry open the cones, remove the seeds, and then store them in caches in surrounding rocks. The stored seeds that the birds misplace grow into new trees. The cones of these trees, such as the whitebark pine (Pinus albicaulis; see figure on page 137), produce sticky resin that prevents other animals from getting the seeds. Even though they reproduce slowly, some conifers can grow rapidly. Some pines that are adapted to a fire cycle, such as the bishop pine (Pinus muricata) of coastal California, can produce cones in just a few years after the trees germinate. In many regions that are dominated by temperate deciduous forest, pines grow rapidly in recently disturbed areas. The pines cannot germinate and grow in shade; shadetolerant deciduous trees grow up underneath them and replace them. Conifers such as podocarps and auracarians that most closely resemble the primitive ones that evolved in the Mesozoic era live in the Southern Hemisphere.

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The evolutionary lineages that have undergone more change and diversification are very common in the Northern Hemisphere. Some important families of conifers are: Podocarpaceae. Podocarps live in continents of the Southern Hemisphere. Some of the kauri trees (Agathis australis) of New Zealand have trunks that are 15 feet (5 m) thick at 150 feet (30 m) above the ground. Araucariaceae. Araucarians also live in the Southern Hemisphere. They include the monkey puzzle trees (Araucaria araucana) of Chile, whose relatively wide, flat needles are very sharp and stiff; the Norfolk Island Pine (Araucaria heterophylla) of the Australian region; and the Wollemi pine (Wollemia nobilis), which was known only from the fossil record until its recent discovery in a national park in Australia. Taxaceae. The yews (genus Taxus) are often understory trees or shrubs of moist forests in the Northern Hemisphere. Their soft needles are relatively flat. The female seeds do not develop in cones but exposed on branches. The seed coat often has a red swelling called an aril, which attracts animals that eat and disperse them. Taxodiaceae. The sequoia family contains the largest trees in the world. The most massive trees in the world are the giant sequoia trees (Sequoiadendron giganteum) of the Sierra Nevadas of California. The General Sherman Tree in Sequoia National Park has a trunk that is 36 feet (12 m) thick at the base and still 14 feet (more than 4 m) thick at a height of 180 feet (60 m). The coast redwoods (Sequoia sempervirens) of southern Oregon and northern California are the tallest trees in the world; 26 of them are known to exceed 360 feet (120 m) in height. The dawn redwood (Metasequoia glyp-

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conifers  137 tostroboides) was thought to be extinct until it was found growing in the mountains of China during the 20th century. Bald cypresses (Taxodium distichum), so called because they are deciduous, are important swamp trees in the southeastern United States. Cupressaceae. Most of the cypresses, cedars, and junipers have short, waxy needles or scales that press against the branches. Species such as the incense cedar (Calocedrus decurrens) of the Sierra Nevadas are relatives of conifers that dominated ancient temperate coniferous forests. The Jomon Sugi tree of Yakushima Island (Cryptomeria japonica) is one of the largest trees in Japan. Juniper shrubs (genus Juniperus) are the most drought-tolerant conifers in North America. The pistillate cones of junipers remain fleshy when mature and look like berries. Birds eat these cones and disperse the seeds. Pinaceae. Trees of this family dominate thousands of square miles. It is one of two plant families

(the other is the grass family) visible by humans from outer space. Important genera in the pine family include the following: ●●

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The seeds of whitebark pines (Pinus albicaulis) are dispersed to new locations by Clark’s nutcrackers (Nucifraga columbiana) in the subalpine forests of California. The birds plant the seeds and eat some of them later, but some of the seeds grow into new trees. The pines (like several other subalpine pine species) produce thick sap that prevents squirrels from eating the seeds; only nutcracker birds can open them.  (Stanley A. Rice)

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Spruces (genus Picea) have pistillate cones that hang downward and needles inserted individually on the stems. Spruces dominate the boreal and most subalpine forests. Firs (genus Abies) have pistillate cones that point upward, and each of their individually inserted needles has a woody peg. Hundreds of species of pines (genus Pinus) have relatively long needles in clusters of two to five, wrapped with a membrane at the base. (The exception is Pinus monophylla of the Great Basin mountains of North America, which has just a single needle in each bundle.) Pines, firs, and Douglas firs (Pseudotsuga menziesii) dominate the montane forests of the American West. Pines such as the foxtail pine (Pinus flexilis) dominate dry subalpine forests of the Rocky Mountains and the Sierra Nevadas. Larches (genus Larix) are deciduous and live in moist areas of the boreal forests. The hemlocks (genus Tsuga) are often small trees associated with coniferous or hardwood forests in Eurasia and North America.

The oldest trees in the world are the bristlecone pines (Pinus longeava) of the White Mountains of California. They live not only at high elevation but in the rain shadow of the Sierra Nevadas. They tolerate cold, dry conditions by growing very slowly. Each new layer of wood may be only a third of a millimeter (a few hundredths of an inch) thick, and the needles may survive for several decades (see figure on page 138). Their very long record of tree rings makes them very useful in the study of past climate. Many bristlecone pines exceed 4,000 years of age. Many conifers are called “softwoods” because they produce light wood and are the mainstay of the timber industry. Timber companies manage many thousands of square miles of pine plantations, some of which have been bred for rapid and uniform growth. Some conifer species are very rare. This includes the dawn redwood of China and Torreya taxifolia, a tree relative of the yew that lives near the border of Florida and Georgia. Their populations consist of only some 2,000 trees. Several species of pines that live only in certain coastal forests of California are also rare. Their cones will not open unless a fire burns the forest. The Torrey pine (Pinus torreyi) is found only in a few patches near San Diego, and the

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Bristlecone pines (Pinus longeava) in the White Mountains of California grow very slowly for thousands of years. The trunk of this tree, which is probably more than 4,000 years old, is more than a meter in diameter.  (Stanley A. Rice)

Monterey pine (Pinus radiata) only in a few patches near the Monterey Peninsula. Though rare in its native habitat, the Monterey pine has become an aggressively invasive species in New Zealand, where it was planted for timber production. See also boreal and subalpine forests; disturbances, ecological; seed plants; succession, ecological; temperate coniferous forests; temperate deciduous forests. Further Reading American Conifer Society. “Conifer Society Home Page.” Available online. URL: http://www.conifersociety.org. Accessed July 9, 2010. Dickie, Ian A., et al. “Co-invasion by Pinus and its mycorrhizal fungi.” New Phytologist 187 (2010): 475–484. Farjos, Aljon. A Natural History of Conifers. Portland, Oreg.: Timber Press, 2008. Gymnosperm Database. “Gymnosperm Database.” Available online. URL: http://www.conifers.org. Accessed July 9, 2010.

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Lanner, Ronald M. The Bristlecone Book: A Natural History of the World’s Oldest Trees. Missoula, Mont.: Mountain Press, 2007. ———. The Piñon Pine: A Natural and Cultural History. Reno: University of Nevada Press, 1981. Llorens, Laura, et al. “Water-use responses of living fossil conifers to CO2 enrichment in a simulated Cretaceous polar environment.” Annals of Botany 104 (2009): 179. Schwartz, Mark W., et al. “Population persistence in Florida Torreya: Comparing modeled projections of a declining coniferous tree.” Conservation Biology 14 (2000): 1,023–1,033.

Connell, Joseph  See competition, ecological. conservation biology  Conservation biology is the interdisciplinary study of all levels of biodiversity, from populations to large-scale ecological communities, with the aim to rescue them from

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conservation biology  139 human destruction and to do so, if possible, without harming human economic activities. Conservation biology therefore not only includes many biological disciplines (from genetics to ecology) but also human sciences such as economics, political science, and history. It is a very broad and urgent area of scientific study. For many of its component sciences, the main question is “How can people understand the way the world works?” But for conservation biology, the main question is “What can people do to save the natural world?” In order to accomplish this, conservation biologists must bring together information and concepts from all of these fields. More information about conservation biology is available in numerous entries in this encyclopedia. Most of the biographical entries in this encyclopedia are on people who have had or continue to have a major impact on conservation. Population genetics and reproduction. Conservation biologists do not just save species but must save populations of species that contain enough genetic variability. Genetic variation allows the population to avoid the negative effects of inbreeding and provides the basis for further evolutionary adjustments to environmental changes. It is also necessary to determine how successfully the populations are reproducing. For example, the Oklahoma subspecies of the seaside alder (Alnus maritima ssp. oklahomensis) consists of a few thousand large shrubs, each of which may produce hundreds of seeds in a typical year. However, few of these seeds germinate, and almost none of them grow into new shrubs. Therefore, to preserve population genetic variation, nearly the entire population of shrubs must be protected. Habitat conservation. It is seldom possible to protect the entire range of any species. It is therefore necessary for conservation biologists to identify habitats within the species’ range that are relatively undisturbed, that are least likely to be threatened by human activity in the near future, and in which the species have sufficient genetic diversity. One of the major sources of habitat disruption is invasive species, which can greatly alter the habitat as they spread unchecked, even within protected habitats. The habitats that have highest conservation priority are the biodiversity hot spots, which contain a large number of endemic species (species found nowhere else). Because elements of the human landscape, such as cities, farms, and roads, break the species range into small fragments, a protected habitat should be as large as possible or connected by natural corridors that allow populations in one fragment to mingle with those in another. Sometimes a habitat might be split in such a way that amphibians need to go from one fragment to the other in order to

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complete their life cycle; in such cases corridors are particularly important. Examples of corridors that connect protected areas include: ●●

●●

the Yellowstone to Yukon Conservation Initiative, which connects habitats along a 2,000 mile (3,200 km) line the Mesoamerican Biological Corridor, which covers 80,000 square miles (208,000 square km), or 27 percent of Central America

Just setting aside a protected area, even if it is not a fragment, may not be enough to save the populations that live in it. If the protected area is long and narrow, it may be too exposed to humanaltered habitats. Many species can survive only deep within an undisturbed habitat, such as a forest, and cannot survive near the edge. This is known as the edge effect and has often resulted in “empty forest syndrome,” in which the common species survive but the rare species vanish. In some cases, economic interests so greatly threaten a habitat that protection is nearly impossible. In these cases, however, government agencies can require a developer to protect or even to attempt to re-create a similar habitat elsewhere. This process is known as mitigation banking and is usually used in the conservation of wetland areas. Extinction. One of the highest priorities of conservation biology is to prevent extinction. This is particularly important for keystone species, which influence the structure and function of entire ecological communities. Extinction of species may be prevented by saving their habitats, but this will prove ineffective if global warming causes the conditions of those habitats to change such that they are no longer suitable for the survival of the species they were intended to protect. Scientists expect global warming to cause the extinction of many species despite intense efforts at habitat conservation. The “sixth mass extinction” is currently under way, mainly as a result of habitat destruction, and global warming will only intensify it. Economic benefits and social justice. An emphasis on the economic benefits of wild habitats will help generate support for saving them and for reducing global warming as well. The benefits are not only for large corporations, such as pharmaceutical companies that can discover new drugs from plant leaves or frog skins in rain forests, but for the livelihood of native peoples that live in or near the natural habitats. Issues of large-scale social justice may also arise from the lack of habitat conservation. If a private corporation cuts down a hillside forest, is it liable for the damage to downslope villages if the deforestation allows floods and mudslides to occur?

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140 conservation biology  140 According to some political leaders, destruction of habitats are not only “crimes against nature” but against humans as well. Education. Conservation of biodiversity is possible only if people know why biodiversity is important, but even this is not enough. Students may learn in a classroom all about plants and animals yet not support or participate in the measures necessary to protect them. It is much more effective— as well as more enjoyable—for students to go out into natural habitats, explore their biodiversity, and think about the ecological processes occurring in them. Even the moderate discomfort of ticks and spiders may instill in them a greater sense of respect for nature. It is also important for issues of biodiversity conservation to be integrated into an entire educational curriculum, including topics such as history and literature, rather than to be isolated into a single class that a student might not take or later forget. Education is the source of future conservation biologists, but even more importantly, of a citizenry that understands the importance of conservation. Diplomacy. Biodiversity and other conservation issues do not respect national borders any more than do the animals that migrate or the seeds that blow over them. Meaningful conservation requires international cooperation. Conservation issues are, at one and the same time, the issues most easily brushed aside by diplomats who work on international issues and the issues that most seldom cause disagreement. Most nations agree that species must be saved, and most nations give these species little attention. The good news is that international conservation agreements between nations that have problems getting along may pave the way for agreements on the issues that cause the most friction between them. However unlikely a prospect this may be, conservation biologists are professionally optimistic that such agreements must at least be attempted. International agreements with narrowly defined goals, such as the Convention on International Trade in Endangered Species (CITES), have had more success than agreements that are broader in scope or have greater economic impact. For example, meaningful carbon emissions agreements remain elusive. The United Nations has established the Convention on Biological Diversity (CBD), an attempt to facilitate international agreements to protect endangered species. The CBD declared 2010 to be the International Year of Biodiversity. See also biodiversity, resources for agriculture; biodiversity, resources for medicine; ecosystem services; endangered species; extinction; federal government role in conservation (United States); greenhouse effect

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first entry and biodiversity; habitat fragmentation; integrated pest management (ipm); invasive species; mass extinctions; population genetics; restoration ecology. Further Reading Becker, Carlos Guilherme, et al. “Habitat split and the global decline of amphibians.” Science 318 (2007): 1,775–1,777. Bowen, B. W. “Preserving genes, species, or ecosystems? Healing the fractured foundations of conservation policy.” Molecular Ecology 8 (1999): S5–S10. Brooks, T. M., et al. “Global biodiversity conservation priorities.” Science 313 (2006): 58. Budd, Ann F., and John M. Pandolfi. “Evolutionary novelty is concentrated at the edge of coral species distributions.” Science 328 (2010): 1,558–1,561. Chan, K. M. “Value and advocacy in conservation biology: Crisis discipline or discipline in crisis?” Conservation Biology 22 (2008): 1–3. Costanza, Robert, et al. “The value of the world’s ecosystem services and natural capital.” Nature 387 (1997): 253–260. Crowder, Larry B., and Elliott A. Norse. Marine Conservation Biology: The Science of Maintaining the Sea’s Biodiversity. Washington, D.C.: Island Press, 2005. Gaston, Kevin J., et al. “The ecological performance of protected areas.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 93–113. Gibson, J. Phil, Stanley A. Rice, and Clare M. Stucke. “Comparison of population genetic diversity between a rare, narrowly distributed species and a common, widespread species of Alnus (Betulaceae). American Journal of Botany 95 (2008): 588–596. Kareiva, Peter, and M. Marvier. “Conserving biodiversity coldspots.” American Scientist 91 (2003): 344–351. Kennedy, Robert F., Jr. Crimes Against Nature. New York: HarperCollins, 2004. Koh, L. P., et al. “Species coextinctions and the biodiversity crisis.” Science 305 (2004): 1,632–1,634. Leroux, S. J., and F. K. Schmiegelow. “Biodiversity concordance and the importance of endemism.” Conservation Biology 21 (2007): 266–268. Luck, Gary W., Gretchen C. Daily, and Paul R. Ehrlich. “Population diversity and ecosystem services.” Trends in Ecology and Evolution 18 (2003): 331–336. Margules, C. R., and R. L. Pressey. “Systematic conservation planning.” Nature 405 (2000): 243–253. May, Robert L., and John Lawton. Extinction Rates. Oxford: Oxford University Press, 1995. McCallum, M. L. “Amphibian decline or extinction? Current declines dwarf background extinction rate.” Journal of Herpetology 41 (2008): 483–491. Mikkelson, G. M., et al. “Economic inequality predicts biodiversity loss.” Public Library of Science ONE 2 (2007): e444. Available online. URL: http://

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continental shelves, biodiversity on  141 www.plosone.org/article/info:doi/10.1371/journal. pone.0000444. Accessed August 4, 2011. Molnar, J., et al. “The sum is greater than the parts.” Conservation Biology 18 (2004): 1,670–1,671. Myers, Norman, et al. “Biodiversity hotspots for conservation priorities.” Nature 403 (2000): 853–858. Naidoo, R., et al. “Global mapping of ecosystem services and conservation priorities.” Proceedings of the National Academy of Sciences USA 105 (2008): 9,495–9,500. Orr, David W. Ecological Literacy: Education and the Transition to a Postmodern World. Albany: State University of New York Press, 1992. Primack, Richard B. Essentials of Conservation Biology. Sunderland, Mass.: Sinauer Associates, 2006. Rice, Stanley A., and J. Phil Gibson. “Is seedling establishment very rare in the Oklahoma seaside alder, Alnus maritima ssp. oklahomensis?” Oklahoma Native Plant Record 9 (2009): 59–63. Sachs, Jeffrey D., et al. “Biodiversity conservation and the millennium development goals.” Science 325 (2009): 1,502–1,503. Society for Conservation Biology. “Society for Conservation Biology.” Available online. URL: http://www.conbio. org. Accessed July 11, 2010. Terborgh, John. Requiem for Nature. Washington, D.C.: Island Press, 1999. Underwood, E. C., et al. “Protecting biodiversity when money matters: maximizing return on investment.” Public Library of Science ONE 3 (2008): e1515. Available online. URL: http://www.plosone.org/article/info:doi/10.1371/journal.pone.0001515. Accessed August 4, 2011. United Nations. “Convention on Biological Diversity.” Available online. URL: http://www.cbd.int. Accessed July 11, 2010. Wake, D. B., and V. T. Vredenburg. “Are we in the midst of the sixth mass extinction? A view from the world of amphibians.” Proceedings of the National Academy of Sciences USA 105 (2008): 11,466–11,473. Wilson, Edward O. “On the future of conservation biology.” Conservation Biology 14 (2000): 1–3. Wood, C. C., and M. R. Gross. “Elemental conservation units: Communicating extinction risk without dictating targets for protection.” Conservation Biology 22 (2008): 36–47. Woods Institute for the Environment. “Aldo Leopold Leadership Program.” Available online. URL: http://leopold leadership.stanford.edu/. Accessed July 11, 2010.

continental shelves, biodiversity on  Con-

tinental shelves are the undersea edges of continents. They are covered by shallow water and have at times of lower sea level in the past (for example, during the ice ages) been exposed as dry land. Therefore, con-

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tinental shelves often contain many fossils and even some archaeological deposits. Some terrestrial areas that were once continental shelves now exist in the middle of each continent. The edges of the continental shelves drop precipitously to the deep ocean floor. Large areas of continental shelf are found between Alaska and Siberia, off the coasts of Florida and Yucatán in the Gulf of Mexico, off the coast of Argentina, throughout the North Sea, in Hudson Bay, in much of Southeast Asia, and off the north coast of Australia. Continental shelves have abundant marine life because sunlight can penetrate the shallow water and because of mineral nutrients that erode from the continents. Excessive nutrient load from the continents, however, can cause eutrophication and reduce biodiversity. The most productive fishing banks are continental shelves. The shallow water supports not only visits from open ocean animals such as fishes and whales but also animals such as sea otters (Enhydra lutris) that do not venture far into the sea. Among the most diverse of the continental shelf habitats are: Kelp forests. Dense stands of kelp (brown algae) grow on many temperate continental shelves, especially near areas where nutrient-rich water rises from the deep oceans. Many of these seaweeds are anchored to the bottom and extend perhaps hundreds of feet up to the surface, held upright by bladders that contain gas (see figure on page 142). Species of Laminaria dominate kelp forests on both sides of the Atlantic Ocean and the coasts of China and Japan; Ecklonia dominates the kelp forests of Australia, New Zealand, and South Africa; Macrocystis primarily dominates the Pacific kelp forests. The northeastern Pacific Rim, from California to the Aleutian Islands, has the kelp forests with the greatest diversity of seaweed species. Kelp forests, like terrestrial forests, have microhabitats, such as canopy and shaded understory, with their own species of seaweeds and animals. Kelp forests provide examples of keystone species that operate up or down the food web. Kelp is a keystone species, not only forming (along with photosynthetic plankton) the base of the food web but also creating surfaces on which many animals (and other algae) live. However, top predators are also keystone species. Overfishing can remove predatory fishes that normally control populations of herbivorous animals. When predators such as sea otters become rare, populations of their prey (mostly sea urchins) explode and eat many of the kelp strands, particularly the young ones. In some cases, the result is “urchin barrens.” Coral reefs. Coral reefs have tremendous biodiversity not only because of the penetration of sunlight into warm waters, but because the coral animals themselves build the reefs. Seaweeds are

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142 continental shelves, biodiversity on  142

first entry marily to protect continental shelf and other marine areas. Protection of continental shelf areas has been more successful than the protection of deep sea areas because continental shelves are usually within a single nation’s jurisdiction.

Continental Shelves: Dangerously Abundant Sources of Oil

Kelp forests support abundant marine life, including many species of fishes.  (Earthgauge and Department of Commerce/NOAA)

rare in coral reefs because the corals themselves and other animals consume young seaweeds. Dense populations of small seaweeds can cover coral reefs when eutrophication occurs. If disturbance kills the corals, populations of starfish, which had formerly been controlled by the corals, may explode. Intertidal zone. The intertidal zone is the shoreline that is exposed to the air at low tide and covered by the ocean at high tide. Most permanent residents of the intertidal zone are invertebrates, such as barnacles and bivalves, that can close their shells when they are exposed to air. Competition is strongest in the lower intertidal zone, where the animals can obtain food from the ocean except during brief periods. Animals that cannot withstand temporary dry conditions, such as sea anemones, crabs, and echinoderms, may be abundant in tidepools, where seawater is trapped. Continental shelves need to be protected from pollution and from overharvesting of organisms such as fishes and kelp. Most preserved natural areas are on land, but in recent decades governments around the world have begun to establish marine biodiversity preserves in continental shelf areas as well as around deep sea volcanic islands. The largest marine preserve in the United States is off the coast of Hawaii. Several national parks exist pri-

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Many continental shelves contain vast supplies of oil. This is primarily because some of them have had shallow marine water for millions of years and are the repository of dead oil-rich phytoplankton that have accumulated during that time. Examples include the Gulf of Mexico and the North Sea. To many people, particularly those who reject all the scientific evidence related to global warming, these oil supplies represent an irresistible source of fuel for the indefinite future. In the United States, “Drill, baby, drill!” was a common conservative slogan. As industrial civilizations have burned more and more oil, drilling operations have moved into deeper water, where there is a greater risk of accidents. One such accident occurred on April 19, 2010. The Deepwater Horizon drilling rig, operated by a contractor for BP (British Petroleum), exploded. This allowed pressurized oil to gush into Gulf of Mexico waters unchecked for 87 days, until July 15. The flow of oil may have been 4.2 million gallons (16,000 cubic m) per day. BP was apparently unprepared to respond to any such disaster. Its response to the spill, coordinated by the U.S. Coast Guard, was primarily to use dispersants that allowed the components of the oil to no longer be visible in the hope that observers would ignore it. They also pumped some of the oil onto ships and burned some of it on the ocean surface. A great deal of natural gas as well as oil emerged from the leaking well. Long before the leak was capped, it was widely considered to be the worst environmental disaster in the history of the United States. Environmentalists countered the conservatives with their own slogan: “Spill, baby, spill!” Tarballs on beaches and birds coated with oil were the most famous yet probably the least significant ecological consequences of the spill. Millions of people felt helpless to respond and even attempted some symbolic but useless tactics, such as sending some of their hair to the Gulf coast to absorb the oil. As this encyclopedia goes to press, the U.S. Justice Department continues its investigation into whether criminal negligence was involved in the BP oil spill. It appears that the federal government (the Minerals Management Service of the Department of the Interior) deliberately overlooked dangerous problems with the drilling rig before its explosion in return for favors from BP and associated companies.

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convergence  143 The liability that the federal government may have along with BP, including the deaths of 11 rig workers, has not been determined. The long-term consequences will not be known for many years but include toxicity from the dispersed, invisible oil components (and from the chemicals used to disperse them) and the methane from the natural gas. Besides the direct environmental consequences, the Gulf Oil Spill of 2010 will contribute to the greenhouse effect directly (through the release of methane) and indirectly (as a result of continued economic reliance on continental shelf oil). See also competition, ecological; coral reefs; deep oceans, biodiversity in; federal government role in conservation (United States); greenhouse effect; keystone species. Further Reading Andrew, N. L. “Spatial heterogeneity, sea urchin grazing, and habitat structure on reefs in temperate Australia.” Ecology 74 (1993): 292–302. Begley, Sharon. “What the spill will kill.” Newsweek, June 14, 2010, 24–28. Carpenter, K. E., et al. “One-third of reef-building corals face elevated extinction risk from climate change and local impacts.” Science 321 (2008): 560–566. Carr, M. H. “Effects of macroalgal dynamics on recruitment of a temperate reef fish.” Ecology 75 (1994): 1,320–1,333. Dayton, P. K. “Ecology of kelp communities.” Annual Review of Ecology and Systematics 16 (1985): 215–245. Gell, F. R., and C. M. Roberts. “Benefits beyond boundaries: The fishery effects of marine reserves.” Trends in Ecology and Evolution 18 (2003): 448–455. Gold, Russell, and Ben Casselman. “Alarm was disabled before BP blast.” Wall Street Journal, July 24, 2010. Available online. URL: http://online.wsj.com/article/ SB1000142405274870329490457538516034249 0350.html?mod=WSJ_hps_MIDDLESecondNews. Accessed May 12, 2011. Graham, M. H., et al. “Deep-water kelp refugia as potential hotspots of tropical marine diversity and productivity.” Proceedings of the National Academy of Sciences USA 104 (2007): 16,576–16,580. Gulf Oil Spill. “New BP oil spill task force is headed by Criminal Division of Justice Department.” Available online. URL: http://www.gulfspilloil.com/new-bpoil-spill-task-force-is-headed-by-criminal-division-ofjustice-department. Accessed August 4, 2011. Halpern, B. S., et al. “Strong top-down control in Southern California kelp forest ecosystems.” Science 312 (2006): 1,230–1,232. Harrold, C., and D. C. Reed. “Food availability, sea urchin grazing and kelp forest community structure.” Ecology 66 (1985): 1,160–1,169.

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Hughes, T. P., et al. “Climate change, human impacts, and the resilience of coral reefs.” Science 301 (2003): 929–933. Jackson, J. B. C., et al. “Historical overfishing and the recent collapse of coastal ecosystems.” Science 293 (2002): 629–638. Lafferty, K. D. “Fishing for lobsters indirectly increases epidemics in sea urchins.” Ecological Applications 14 (2004): 1,566–1,573. Paddack, M. J., and J. A. Estes. “Kelp forest fish populations in marine reserves and adjacent exploited areas of Central California.” Ecological Applications 10 (2000): 855–870. Pearse, J. S., and A. H. Hines. “Expansion of a central California kelp forest following the mass mortality of sea urchins.” Marine Biology 51 (1987): 83–91. Sala, E., and M. H. Graham. “Community-wide distribution of predator-prey interaction strength in kelp forests.” Proceedings of the National Academy of Sciences USA 99 (2002): 3,678–3,683. Santelices, B. “The discovery of kelp forests in deepwater habitats of tropical regions.” Proceedings of the National Academy of Sciences USA 104 (2007): 19,163–19,164. Sotka, E. E., and Mark E. Hay. “Effects of herbivores, nutrient enrichment, and their interactions on macroalgal proliferation and coral growth.” Coral Reefs 28 (2009): 555–568. Steneck, R. S., et al. “Kelp forest ecosystems: Biodiversity, stability, resilience and future.” Environmental Conservation 29 (2002): 436–459.

convergence  Convergence occurs when similar

adaptations evolve in separate lineages of organisms. Convergent adaptations evolve separately (by convergent evolution), rather than being inherited from a common ancestor. Convergent evolution is responsible for a great deal of the biodiversity on Earth. Convergence can often be recognized because the organisms evolve the adaptation in different ways. This has been experimentally demonstrated in bacteria. Scientists grew some populations of the gut bacterium Escherichia coli in the absence of the sugar maltose, and they lost the genes that would allow them to use maltose as a food source. Then they were exposed to maltose again. The populations produced bacteria that had mutations that allowed them to metabolize the maltose. Each of these populations evolved a different set of mutations. The reinvention of the ability to use maltose was a convergence in the separate bacterial populations, but each population achieved this result in a different way. The following are just a few of the many thousands of possible examples from plants and from animals.

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first entry

Plant Convergences

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Plant adaptations to climatic conditions. Plants have evolved convergent adaptations to stressful environmental conditions, including these examples. ●●

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Bushes that live in dry climates have small leaves. Small leaves dissipate heat into the air more efficiently than do large leaves, which is important in hot, dry climates, where plants must restrict the amount of water they use in evaporative cooling. Small-leaved bushes have evolved within several different plant families, all of which have species with larger leaves. Small leaves are therefore a new adaptation in several different plant families. In some environments, these bushes are also adapted to sprouting or seed germination after periodic fires. Habitats that are dominated by bushes with small leaves and that experience periodic fires have evolved separately in California, Chile, the Mediterranean Basin, and South Africa. The succulent growth form, which allows water storage and CAM photosynthesis, has evolved in several plant families, for example the cactus and lily families in North American deserts, and the spurge family in South African deserts. The C4 form of photosynthesis may have evolved more than 45 different times. Several lineages of plants have evolved the ability to grow in toxic serpentine soil.

Plant adaptations to pollination methods. Plants have evolved convergent adaptations to the same pollination mechanisms, as in the following examples.

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Other examples of convergent evolution in plants include the following.

Flowers that attract hummingbirds as pollinators are usually tubular and red. The tubular red form of flower has evolved in many different plant families. In one instance, a single mutation changed yellow, bee-pollinated flowers into red, hummingbird-pollinated flowers and resulted in an immediate reproductive isolation of two populations, resulting in the evolution of two separate species. Different lineages of plants have evolved adaptations for wind pollination, in which the petals are reduced in size or lost, pollen production is increased, and the pollen-capturing surfaces of the flowers increase in size.

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Plant defenses. Plants have evolved convergent adaptations as defenses against herbivores, as in these examples.

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Spines and thorns have evolved many times in separate lineages of plants. Some plants have seeds with sharp spines that entangle in animal fur, causing the animal to disperse the seeds to a new location. Strikingly similar structures for animal fur dispersal have evolved in Tribulus terrestris, a dicot, and genus Cenchrus, a grass (see figure on page 145). Grasses and dicots evolved from a common ancestor, without spiny seeds, that lived more than 100 million years ago. The use of latex (a sticky, milky sap) as a defense against herbivores and as a way of sealing damaged areas has also evolved separately in several plant families. As a result, rubber latex is produced by a spurge (Hevea brasiliensis), a fig (Ficus elastica), and the dita bark tree, Alstonia, in the dogbane family. Chemical defense in plants has evolved thousands of times. Usually, each lineage of plant uses a different set of chemicals, which is why the plant kingdom produces such an astounding variety of pharmaceutical and spice substances. Some plant chemicals, such as limonene, reappear over and over, producing the lemon scent separately in lemons (a citrus), lemon basil and lemon balm (mints), lemon grass, and the conifer Thuja standishii. Onion scent has evolved separately in onions (Allium cepa), which are monocots, and in the salmwood tree, a dicot (Cordia alliadora).

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Parasitism has evolved separately in several lineages of flowering plants. These plants have lost their chlorophyll and obtain food from other plants. Examples include plants in the heath family (genera Pterospora and Monotropa), relatives of snapdragons (genus Epifagus), and plants in the orchid family (genus Corallorhiza). Within the genus Calochortus, the same flower shapes appear to have evolved in several different lineages: the cat’s ear form, which is hairy and has open petals; the mariposa form, which is cuplike; the fairy lantern form, which hangs down, with the petals together; and the star tulip form, with smooth spreading petals. At least three lineages of plants have separately evolved mutualisms with bacteria in their roots that convert nitrogen gas into

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convergence  145 ●●

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Both the puncture vine (left, Tribulus terrestris) and the sandbur (right, Cenchrus spinifex) produce seeds that entangle in the fur of mammals. The seeds look remarkably similar to one another, even though puncture vines (a dicot) and sandburs (a grass) have had separate evolutionary lineages for about 100 million years. They have independently evolved seeds with spines.  (Stanley A. Rice)

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nitrogen fertilizer: the legume family Fabaceae, alders (in the birch family Betulaceae), and Vitex keniensis (in the verbena family Verbenaceae). The bacteria involved in these mutualisms are different: Legumes have coevolved with bacteria such as Rhizobium, while alders have coevolved with Frankia bacteria. Strikingly similar leaf forms, so similar as to be almost indistinguishable, have evolved in Jacaranda mimosifolia (family Bignoniaceae) and the mimosa (Albizzia julibrissin of the Mimosoideae).

Animal Convergences Eyes. Eyes have evolved several times in the animal kingdom, as in these examples.

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Among the earliest eyes were the crystalline eyes of trilobites, which evolved separately from the compound eyes found in other arthropods and the calcitic eyes of certain echinoderms. Most arthropods have compound eyes, but some spiders (the jumping spiders that rely on acute vision) have a lens eye similar to that of vertebrates. Some shrimp have both compound and lens-type eyes. Eyes have evolved in three lineages of gastropod mollusks (snails and their relatives) separately from the eyes of cephalopods such as squid and octopus. Some marine worms have also evolved eyes. One group of coelenterates has evolved eyes. Vertebrates have also evolved eyes.

Each of these groups has eyes that receive visual information, but in different ways. For example, the eyes of the squid are nearly as complex as vertebrate eyes. In vertebrates, the nerve cells are in front of the retina, while in the squid they are behind the retina. Humans, other apes, and Old World monkeys have three-color vision; this type of vision has evolved independently in howler monkeys of the New World. All the above examples are true eyes, with lenses and retinas, as opposed to simple eyespots that detect the presence of light. Animal societies. Social evolution has converged in different lineages of animals, as in the following examples. ●●

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The “army ant” lifestyle may have evolved separately in Africa and South America, including the behavior of forming a living nest out of the ants’ own bodies that has a limited ability to regulate the internal temperature. In turn, seven different lineages of staphylinid beetles have evolved into army ant mimics, which can live among the ants without being recognized as intruders. The reproductive system in which one dominant female reproduces and the other females do not is well known in insects (ants, bees, and wasps). Three different lineages of coral reef shrimp have evolved a similar system. It is also found in one group of mammals, the naked mole rat. The insect and mammal lineages achieved this system differently, however. In ants, bees, and wasps, the males have only half the chromosomes of the females, and the difference between queens and workers results from being fed different foods as they develop. In mole rats, the males have the same number

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of ­chromosomes as females, and the dominant female inhibits reproduction in the other females by behavioral means.

electrolocating fishes, it is the cerebellum that has increased in size, not the cerebrum, as in vertebrates that rely on vision.

Animals finding their way in the dark. Different animal lineages have converged on alternatives to vision, as in these examples.

Animal body form and physiological adaptations. Different lineages of animals have converged upon similar body forms, as in the following.

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Echolocation has evolved several times independently. Bats emit sound waves and use the reflections of those sounds to create mental maps of their surroundings, including the locations of prey insects. Some kinds of fishes, and many cetaceans such as dolphins use a similar system in underwater locations that are too murky for vision to be of much use. Oilbirds in South America and swiftlets in Asia use echolocation also. In turn, some of the prey animals sought by these echolocators have evolved a defense mechanism: the production of rapid clicks to confuse the predators. This defense has evolved separately in the moths hunted by bats and the shad hunted by cetaceans. Electrolocation has also evolved independently, at least six times, in different lineages of fishes. These animals use electric currents generated by muscles to create a mental map of their surroundings, but the electric currents are different and come from different sets of muscles in the six lineages. They also use electrical signals for communication. Electrolocation can involve an increase in brain size, just as did the development of vision. In

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Marsupial mammals in Australia and placental mammals in the northern continents have undergone separate adaptive radiation but have converged upon some striking similarities of form (see table). Some of the convergences produce forms that are scarcely distinguishable (as in placental and marsupial mice), while others are convergences of function more than of appearance (as in deer and kangaroos). A similar convergence has occurred in the placental mammals that evolved in Africa and those that evolved in the northern continents (North America and Eurasia), which separated only after the beginning of the Cenozoic era. This convergence has occurred in separate lineages of grazing mammals, otters, insectivores, burrowers, and anteaters. Flight has evolved separately in insects, reptiles, birds, and mammals. Insect wings are outgrowths of the external skeleton. The flying reptiles, such as the pterosaurs of the Mesozoic era, had wings supported by one long finger. Birds have wings without fingers. Bats have wings with several fingers (see figure on page 147). The ability to glide evolved separately in the now-extinct kueli-

Convergences in Marsupial and Placental Mammals Adaptation

Marsupial

Placental

Burrowing form with poor eyesight

Marsupial mole

Mole

Burrowing form with good eyesight

Wombat

Badger

Long snout, eating ants

Numbat

Anteater

Small, eating seeds

Marsupial mouse

Mouse

Climbs trees

Cuscus

Lemur

Glides from trees

Flying phalanger

Flying squirrel

Small, hopping

Bandicoot

Rabbit

Large herbivore

Kangaroo

Deer

Feline form

Tasmanian cat

Bobcat

Canine form

Tasmanian wolf

Wolf

xviii+598_Biodiversity_F.indd 146

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convergence

147

Both bats and birds have wings, but wings evolved separately in bird and mammal lineages. Their separate evolutionary origin is revealed by their internal structure: Bat wings have finger bones, and bird wings do not.











neosaurs, in which extended ribs produced a gliding surface; flying squirrels, in which flaps of skin between the legs produce a gliding surface; and even flying snakes, in which the entire flattened body produces a gliding surface. there is even a species of gliding ant. the fishlike body form has evolved several times: in fishes, in aquatic reptiles of the Mesozoic era, and in dolphins and other cetaceans. Several different families of birds, on different continents and islands, have evolved the hummingbird body form and way of living: small bodies, long bills, and rapid fluttering of wings. this includes the hummingbirds of north and South america (family trochilidae), australian honeyeaters (family Meliphagidae), Hawaiian honeycreepers (family Drepanididae), and african sunbirds (family nectariniidae). this adaptation has also evolved in sphinx moths, which many people mistake for hummingbirds when they fi rst see them. Mammals in 11 families in three different orders, including some marsupials, have evolved the molelike lifestyle of digging through the soil, with big claws and reduced eyes. this adaptation has evolved eight times in rodents. earthworms (which are invertebrates) and caecilians (which are vertebrate amphibians) have separately evolved long, flexible bodies without limbs and the use of a hydrostatic skeleton (muscles pressing against water compartments) to move through the soil. One type of barnacle produces a shell made of calcium phosphate and protein, like the

xviii+598_Biodiversity_F.indd 147











● ●



bones of vertebrates, although most barnacles produce shells of calcium carbonate. insect species with a grasping foreleg (the praying mantis body form) have evolved in three separate insect orders. Both bombardier beetles and certain kinds of mites spray caustic liquids against animals that threaten them. However, it is not the same chemical in the two groups. Both dipterans and strepsipteran fl ies as well as african beetles have separately evolved halteres. Halteres are modified wings that function as balancing devices. in dipterans (such as the house fly), it is the hind wings that become halteres; in strepsipterans, it is the forewings; in some african beetles, it is the wing cover. cephalopod molluscs such as the octopus have evolved a closed circulatory system, in which the blood cells remain inside the vessels, independently of vertebrates. live birth has evolved separately in mammals, some reptiles, some bony fishes, and some sharks. Warm-bloodedness has evolved separately in birds, mammals, and tuna. arctic and antarctic fishes have separately evolved a very similar set of antifreeze proteins. Vultures, which are birds that have featherless heads and eat carrion, have evolved separately in the new World (the family cathartidae is related to storks) and the Old World (the family accipitridae is a type of hawk).

Physiological convergence has occurred in different lineages of humans. the ability of adults to

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148 convergence  148 digest lactose has evolved separately in Europeans and in some African tribes that live by herding cattle. Coevolution between animal species and other species. Similar types of coevolution have occurred in different sets of organisms, as in the following examples. ●●

●●

●●

●●

At least five different species of ants have evolved the ability to grow underground gardens of fungus. These ant gardens may represent an evolution of agriculture separate from humans. In 70 different lineages, insects and spiders have evolved characteristics that allow them to parasitize ant nests without being recognized as intruders. Bioluminescence, in which living tissues produce light, has evolved separately in insects and in vertebrates. In vertebrates, the light is usually produced by mutualistic bacteria that live in the vertebrate tissues. Bioluminescence may have evolved 30 separate times. In some vertebrates that eat plant material, bacteria in the digestive system digest the cellulose. The vertebrate then uses a mutant form of lysozyme to digest the bacteria. This adaptation has evolved separately in cows, langur monkeys, and hoatzin birds.

In many cases, convergent evolution does not require a total reinvention of an adaptation, as in these examples. ●●

●●

●●

Limonene has evolved separately in several lineages of plants (see above), but most flowering plants have terpene synthases, the enzymes that produce the immediate chemical precursors of limonene. The ornithologist N. I. Mundy explains that the evolution of similar color patterns in separate bird lineages has resulted from the modification of an underlying genetic pattern that they inherited from their common ancestor. Eyes have evolved perhaps 40 separate times in the evolutionary history of animals (see above). All these animals share an organizer gene, called pax, that stimulates the development of eyes. In each of these lineages, the actual structure of the eye has evolved separately. There is a marine worm that has compound eyes, like those of other invertebrates, but also has brain lobes that have photosensitive chemicals similar to those of vertebrate eyes. Apparently, vertebrate eyes

xviii+598_Biodiversity_F.indd 148

first entry evolved from invertebrate brain lobes rather than from invertebrate eyes. In modern organisms, scientists can recognize convergence because, despite the external similarities, the organisms are internally different and have achieved the convergence in different ways. In looking at fossils, scientists cannot always tell whether organisms shared a characteristic because they inherited it from a common ancestor or because they evolved it separately by convergence. This sometimes makes reconstructing fossil history difficult. Sometimes in the fossil record, a species appears to have become extinct, then reappears. Is it because the species was rare for a long time, then reappeared in greater abundance (what the paleontologist David Jablonski called Lazarus taxa, because it appeared to rise from the dead), or because another lineage evolved similar features by convergence and it just looked like a reappearance (what the paleontologist Douglas Erwin called Elvis taxa)? Every evolutionary scientist understands that there are many examples of convergent evolution. They differ in how much importance they give convergence in the overall pattern of the evolution of life. Some evolutionary scientists claim that evolution has so many different possible directions that the actual course taken by evolution is a matter of historical contingency, a viewpoint expressed by the evolutionary biologist Stephen Jay Gould. Gould said that evolution produced a bush of different forms, not a ladder leading upward to human perfection. These scientists consider convergence to be details that have occurred at the tips of the branches of the bush of life. Others, such as Simon Conway Morris, insist that convergence is so frequent that it constitutes one of the major features of evolution. They point out that even though there may be an almost infinite number of possible biological adaptations, there are only a limited number of strategies that work, and evolution keeps finding these strategies over and over. Conway Morris agrees with Gould that evolution is a bush, not a ladder, but in this bush, he says, many of the branches are parallel. Conway Morris cites the parallel evolution of large brains in cetaceans (such as dolphins) and humans. In the human lineage, there was a separate increase in brain size in the lineage that led to modern humans, the lineage that led to Neanderthals, and perhaps the lineages that led to Asian Homo erectus and the robust australopithecines. Agriculture and civilization in humans evolved separately in East Asia, the Middle East, and America. Intelligence does not always offer an evolutionary advantage, but when it does, one would expect that the large processing center for the nerves would be near the front end of the animal,

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coral reefs  149 where most of the sensory organs are located (a big brain in a head with eyes and nose). Conway Morris says that the evolution of intelligence is a rare event, but that if humans encounter an intelligent life form somewhere else in the universe, it would probably be something that they would recognize as a person, perhaps even as a human. This is why he refers to “inevitable humans in a lonely universe.” In convergent evolution, the same or similar solutions to environmental and social challenges evolve over and over again, contributing to the proliferation of species throughout evolutionary history. See also adaptive radiation; coevolution; mutualism; parasitism; speciation. Further Reading Conway Morris, Simon. Life’s Solution: Inevitable Humans in a Lonely Universe. Cambridge: Cambridge University Press, 2003. Mundy, N. I., et al. “Conserved genetic basis of a quantitative plumage trait involved in mate choice.” Science 303 (2004): 1,870–1,873. Summarized by Hoekstra, Hopi E. and Trevor Price. “Parallel evolution is in the genes.” Science 303 (2004): 1,779–1,781. Patterson, Thomas B., and Thomas J. Givnish. “Geographic cohesion, chromosomal evolution, parallel adaptive radiations, and consequent floral adaptations in Calochortus (Calochortaceae): Evidence from a cpDNA phylogeny.” New Phytologist 161 (2003): 253–264. Pichersky, Eran. “Plant scents.” American Scientist 92 (2004): 514–521. Shadwick, Robert E. “How tunas and lamnid sharks swim: An evolutionary convergence.” American Scientist 93 (2005): 524–531. Sheppard, Samuel K., et al. “Convergence of Campylobacter species: Implications for bacterial evolution.” Science 320 (2008): 237–239. Weinrech, Daniel M., et al. “Darwinian evolution can follow only very few mutational paths to fitter proteins.” Science 312 (2006): 111–114.

coral reefs  Coral reefs are reefs, or ridges, con-

structed from the accumulated limestone bodies of corals. New corals attach to the limestone shells of dead corals, further building the reefs. Some coralline algae also have limestone in their cell walls and contribute to reef formation. Some animals bore into the reefs, and parrotfish chew and spit out coral. The resulting coral sediments settle into reef fissures and strengthen the reefs. In ancient oceans, corals were not the only organisms that built reefs. Bryozoans and brachiopods also formed reefs, as did kinds of coral that are no longer common. Fringing reefs are attached to shoreline rocks and form shallow lagoons. Barrier reefs are sepa-

xviii+598_Biodiversity_F.indd 149

rated from shoreline rocks and form deep lagoons. If a reef forms a complete circle, it is a coral atoll. These reefs, full of crevices, provide a habitat for numerous other species. Because of their immense biodiversity, they have been called the “rain forests of the sea,” even though their diversity is less than that of rain forests. Coral reefs are most abundant in shallow tropical waters. The main reason is that corals grow best in water with bright sunlight. Although corals (which are animals in the phylum Cnidaria) can grab food with their stinging tentacles, most of their food comes from mutualistic single-celled algae (zooxanthellae) that live in their tissues and produce food by photosynthesis. Zooxanthellae create the many bright colors of corals, and the shapes of corals appear to be adaptations to exposing their zooxanthellae to light (see figure on page 150). Corals do not grow well if ocean water is diluted by freshwater, as occurs near the mouths of the Amazon and Ganges Rivers. Corals thrive in intermediate conditions of temperature and nutrients. If temperatures are too high, the corals lose their zooxanthellae, which causes them to become white. This is known as coral bleaching. The coral animals slowly starve. If nutrient levels are too high, algae overgrow the coral reefs. Most of the nutrient cycling occurs very close to the reef itself; nutrient levels in the water are low. The zooxanthellae use the carbon dioxide and the nitrogenous wastes of the corals inside the tissues of the corals themselves. Some corals, such as Oculina varicosa and Lophelia pertusa, live in deep water (more than 6,000 feet [2,000 m]) or on continental shelves as far north as Norway. However, they do not have zooxanthellae, and they grow more slowly. They therefore do not form large reefs. Because of the abundant coral growth, a complex ecological community, including as many as 4,000 fish species (about one-quarter of the total fish species in the sea), depends on the corals. Among the top resident predators in reefs are moray eels, in the fish family Muraenidae. Even larger predators such as sharks pass through, feeding on the abundant fishes. Because the zooxanthellae create many colors, colorful fish are well camouflaged in coral reefs. The coral reef community exists in a delicate balance of disturbance. Echinoderm larvae cannot settle and develop on intact reefs because the corals eat them. However, in disturbed reefs, echinoderm larvae can develop, and once they are large enough, they eat the corals. During World War II, many coral reefs were damaged by bombing. This tipped the balance in favor of echinoderms, especially Acanthaster planci, the crown-of-thorns starfish. Large numbers of starfish began to devastate the coral reefs.

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150 coral reefs  150

first entry

This coral reef, near Port Ghalib, Egypt, has abundant corals and colorful fishes.  (J. Hutsch)

Coral reefs are facing numerous environmental threats. They include: ●●

●● ●●

●● ●●

Eutrophication occurs when wind erosion brings in dust from land surfaces or when coastal communities discharge sewage. Some fishermen use explosives or cyanide to kill large numbers of fish. Many tropical fishes for aquaria come from coral reefs, particularly those that are unable to reproduce in captivity. Global warming is causing the water to become warm enough to bleach the corals. Carbon dioxide in the atmosphere is acidifying the water.

Coral bleaching and water acidification may be serious enough problems that coral reefs may be unable to survive by the end of the 21st century, except as small patches. The ocean biologist Nancy Knowlton predicts that coral reefs will no longer exist by the year 2100, and perhaps by 2050.

xviii+598_Biodiversity_F.indd 150

There are attempts to restore coral reefs that have been damaged. These include the construction of metallic frames on which coral larvae can settle and begin to form artificial reefs. The process may be encouraged by electric currents, which precipitate limestone onto the frames. While some of these efforts have been successful, they cannot prevail against the higher water temperatures and acidification associated with global climate change. See also animals; continental shelves, biodiversity in. Further Reading Bellwood, D. R., et al. “Functional versatility supports coral reef biodiversity.” Proceedings of the Royal Society of London B (Biology) 273 (2006): 101–107. Burt, J., et al. “Are artificial reefs surrogates of natural habitats for corals and fish in Dubai, United Arab Emirates?” Coral Reefs 28 (2009): 663–675. Carpenter, Kent E., et al. “One-third of reef-building corals face elevated extinction risk from climate change and local impacts.” Science 321 (2008): 560–566.

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Cretaceous extinction  151 Cheng, Y.-R., and C.-F. Dai. “Endosymbiotic copepods may feed on zooxanthellae from their coral host, Pocillopora darnicornis.” Coral Reefs 29 (2010): 13–18. Coral Reef Alliance. “Coral Reef Alliance.” Available online. URL: http://www.coral.org. Accessed July 8, 2010. Hobbs, Jean-Paul A., et al. “Rarity and extinction risk in coral reef angelfishes on isolated islands: Interrelationships among abundance, geographic range size, and specialization. Coral Reefs 29 (2010): 1–11. Hughes, T. P., et al. “Climate change, human impacts, and the resilience of coral reefs.” Science 301 (2003): 929–933. Knowlton, Nancy. “Coral reef biodiversity—habitat size matters.” Science 292 (2001): 1,493–1,495. Maragos, J. E., et al. “Coral reefs and biodiversity: A critical and threatened relationship.” Oceanography 9 (1996): 83–99. Mumby, Peter J. “Herbivory versus corallivory: Are parrotfish good or bad for Caribbean coral reefs?” Coral Reefs 29 (2009): 683–690. National Oceanic and Atmospheric Administration. “NOAA Coral Reef Conservation Program.” Available online. URL: http://coralreef.noaa.gov. Accessed July 8, 2010. Orr, J. C., et al. “Anthropogenic ocean acidification over the 21st century and its impact on calcifying organisms.” Nature 437 (2005): 681–686. Prada, C., et al. “Octocoral bleaching during unusual thermal stress.” Coral Reefs 29 (2010): 41–45. Selkoe, K. A., et al. “A map of human impacts to a ‘pristine’ coral reef ecosystem, the Papaha¯naumokua¯kea Marine National Monument.” Coral Reefs 28 (2009): 635–650. Sotka, E. E., and Mark E. Hay. “Effects of herbivores, nutrient enrichment, and their interactions on macroalgal proliferation and coral growth.” Coral Reefs 28 (2009): 555–568.

Cowles, Henry Chandler  See succession, ecological.

Cretaceous extinction  Some 65 million years ago, at the end of the Cretaceous period, one of the five mass extinctions of Earth history occurred. It was not the greatest of the mass extinctions (the Permian extinction resulted in the disappearance of more species) but has long been the subject of intense speculation and research because it was the most recent of the mass extinctions, and it involved the disappearance of the dinosaurs, the prehistoric animals that have attracted perhaps the most attention from scientists and the general public.

xviii+598_Biodiversity_F.indd 151

Part of the problem in explaining the Cretaceous extinction, as with the other mass extinctions, was that not all groups of organisms suffered the same rate of disappearance. The largest land animals were dinosaurs, all of which suffered extinction, and the large marine reptiles also became extinct. However, not all dinosaurs were large; even the small ones became extinct. Most mammals, amphibians, crocodiles, turtles, insects, and land plants survived the Cretaceous extinction. Among the marine mollusks, the ammonoids became extinct, but the nautiloids, which appeared to have had very similar ecological roles, did not. Birds survived, but only a few lineages of them. Some plankton, the floating microscopic organisms of the oceans, experienced a dramatic set of extinctions (for example, the foraminiferans), while others, such as diatoms, did not. Extinction rates were much higher on land (about 90 percent of species) than in freshwater (about 10 percent of species). There was also the question of whether the Cretaceous extinction was a single catastrophic event or the outcome of gradual declines toward extinction. Several lineages of dinosaurs were already in decline during the Cretaceous period; others were not. Although land plants survived the extinction, their populations were apparently set back by some catastrophe. At the end of the Cretaceous, ferns and fern spores were very numerous. Ferns often lived in areas from which the larger vegetation had been removed by some disturbance. The Cretaceous extinction appears to have been a catastrophic event. Some investigators noticed that a catastrophic collapse of the food chain could have resulted in the pattern of extinctions. The large reptiles (which may have had relatively rapid metabolisms) would need continual food, often in vast quantities. In contrast, many amphibians, reptiles with slow metabolisms such as crocodiles and turtles, and insects can hibernate until food resources again became available. The Cretaceous mammals were small and, despite their high metabolisms, might also have been able to hibernate, as many do today. Omnivores and carrion feeders usually survived the Cretaceous extinction. Plants could have survived as rootstocks or seeds. Some researchers speculated that plankton may have been less capable of surviving an interruption of conditions suitable for photosynthesis, although most plankton have resting phases that can resist very cold and dry conditions. There was, however, no agreement on what might have interrupted the food supply. Volcanic eruptions can have a massive impact on organisms around the world. The Indonesian volcano Tambora eruption in 1815 was followed by what has

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152 Cretaceous extinction  152 been called the “year without a summer” because the volcanic dust, propelled into the stratosphere where it could not be cleared by rain, blocked sunlight. It was the worst agricultural year on record; the resulting famine killed 65,000 people in Ireland alone. All this happened, even though the global temperature decreased by only about 2°F (1½°C). A “supervolcano” eruption occurred 74,000 years ago (Toba, in Sumatra). Evidence from Greenland ice cores, which preserve a record of global climate, suggests that this volcanic eruption was followed by six cold years. Clearly, massive volcanic eruptions could have interrupted the food chain at the end of the Cretaceous. There were massive volcanic eruptions (producing the Deccan Traps) at the end of the Cretaceous period. However, these eruptions do not appear to have been large enough to have, by themselves, caused the Cretaceous extinction. In a 1980 paper, the physicist Luis Alvarez and his son, the geologist Walter Alvarez, and their associates made a dramatic and risky proposal: that the Cretaceous extinction was caused by an extraterrestrial impact. Such an impact would, in fact, explain global extinctions. The impact itself would project dust high into the atmosphere and ignite fires that would add great clouds of smoke, both of which would darken the Earth, plunging it into wintry conditions disastrous for the food chain. Massive acid rain events might also have occurred as a result of the fires, especially if the rock underlying the impact contained sulfur. The shock to the crust could have set off volcanic eruptions and tsunamis (tidal waves), which would have contributed further to local and worldwide extinctions. Some researchers estimate that such an impact would have influenced climate around the world for up to 10,000 years afterward. Because the prevalence of uniformitarianism in geological science made paleontologists extremely hesitant to invoke processes that are not normally occurring on the Earth as explanations for events in the history of the Earth, the Alvarez suggestion was resisted at first. Nevertheless, their initial evidence was good, and more evidence later reinforced his proposal. The Alvarez team had not begun their research with the intention of explaining the Cretaceous extinction. They were more interested in determining accurate dates for the strata that spanned the Cretaceous-Tertiary interval. They expected that the rare element iridium might be useful in studying these strata. They found an astonishing “iridium anomaly” in rocks over a wide area right at the Cretaceous-Tertiary boundary: a transient and very high concentration of this element. Iridium is much more common in interplanetary particles and objects than

xviii+598_Biodiversity_F.indd 152

first entry on Earth. The iridium spike in the sedimentary layers at the end of the Cretaceous period strongly suggested an asteroid impact, but scientists sought corroboration. They found it. ●●

●● ●●

●●

Not only was iridium common in the last Cretaceous layers, but also microtektites, which are small glass spheres characteristic of the impact of an asteroid with terrestrial rocks that contain silicon. Shocked quartz grains, characteristic of powerful impacts, were also found. Sootlike carbon particles were also unusually common in the last Cretaceous deposits. Sediments in the Caribbean from the end of the Cretaceous suggest that a very large tsunami had struck coastal areas. Perhaps most important, scientists wanted to find the crater caused by the asteroid. If the impact had occurred in an area with abundant rainfall and erosion or in the ocean, it might have eroded away but still left some evidence. Just such evidence was found on the Yucatán Peninsula. The Chicxulub Crater has mostly filled in, but evidence of sedimentary layers shows that there was once a massive impact crater.

The Cretaceous extinction changed the face of biodiversity on Earth. After the large dinosaurs were gone, many large mammals evolved as well as many small ones. Even though fishes continue to be the most diverse group of vertebrates and there are still more reptile species than mammals, the Cenozoic era has become known as the “age of mammals.” Before the Cretaceous extinction, conifers dominated many forests, with flowering plants playing a minor role; afterward, their roles were reversed. Since the Cretaceous extinction, the only extensive coniferous forests have been in the cold regions of Earth. See also Cretaceous period, biodiversity in; Permian extinction. Further Reading Alvarez, Luis W., Walter Alvarez, Frank Asaro, and Helen V. Michel. “Extraterrestrial cause for the CretaceousTertiary extinction.” Science 208 (1980): 1,095–1,107. Alvarez, Walter. T. Rex and the Crater of Doom. Princeton, N.J.: Princeton University Press, 1997. Duncan, R. A., and D. G. Pyle. “Rapid eruption of the Deccan flood basalts at the Cretaceous/Tertiary boundary.” Nature 333 (1988): 841–843. Fawcett, A., et al. “Plants with double genomes might have had a better chance to survive the Cretaceous-Tertiary extinction event.” Proceedings of the National Academy of Sciences USA 106 (2009): 5,737–5,742.

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Cretaceous period, biodiversity in  153 Frankel, Charles. The End of the Dinosaurs: Chicxulub Crater and Mass Extinctions. Cambridge: Cambridge University Press, 1999. Labandeira, Conrad C., et al. “Impact of the terminal Cretaceous event on plant-insect associations.” Proceedings of the National Academy of Sciences USA 99 (2002): 2,061–2,066. Liangquan, L., and G. Keller. “Abrupt deep-sea warming at the end of the Cretaceous.” Geology 26 (1998): 995–998. Marshall, C. R., and Peter D. Ward. “Sudden and gradual molluscan extinctions in the latest Cretaceous of western European Tethys.” Science 274 (1996): 1,360–1,363. Morgan, J., et al. “Analyses of shocked quartz at the global K-P boundary indicate an origin from a single, highangle, oblique impact at Chicxulub.” Earth and Planetary Science Letters 251 (2006): 264–279. Poinar, George, Jr., and Roberta Poinar. What Bugged the Dinosaurs? Insects, Disease, and Death in the Cretaceous. Princeton, N.J.: Princeton University Press, 2008. Robertson, D. S., et al. “Survival in the first hours of the Cenozoic.” Bulletin of the Geological Society of America 116 (2004): 760–768. Sheehan, Peter M., and Thor A. Hansen. “Detritus feeding as a buffer to extinction at the end of the Cretaceous.” Geology 14 (1986): 868–870. Springer, M. S., et al. “Placental mammal diversification and the Cretaceous-Tertiary boundary.” Proceedings of the National Academy of Sciences USA 100 (2003): 1,056–1,061. Vajda, Vivi, et al. “Indication of global deforestation at the Cretaceous-Tertiary boundary by New Zealand fern spike.” Science 294 (2001): 1,700–1,702. ———, and S. McLoughlin. “Fungal proliferation at the Cretaceous-Tertiary boundary.” Science 303 (2004): 1,489–1,490. Wilf, Peter, and K. R. Johnson. “Land plant extinction at the end of the Cretaceous: A quantitative analysis of the North Dakota megafloral record.” Paleobiology 30 (2004): 347–368. ———, et al. “Decoupled plant and insect diversity after the end-Cretaceous extinction.” Science 313 (2006): 1,112–1,115.

Cretaceous period, biodiversity in  The

Cretaceous period (140 to 65 million years ago) was the third and final period of the Mesozoic era, following the Jurassic period. The Mesozoic era is also known as the age of dinosaurs, because dinosaurs were the largest land animals during that time. Dinosaurs became extinct during the Cretaceous extinction, which is one of the two most important mass extinctions in the history of Earth. The

xviii+598_Biodiversity_F.indd 153

Multicellular Biodiversity   in the Cretaceous Period Conditions Atmospheric oxygen

50% above modern level

Atmospheric carbon dioxide

4.9 times modern level

Global temperature

7°F (4°C) above modern level

Sea level

560 feet (170 m) higher than today

Approximate Number of Families* Continental

500

Marine

600

Total

1100

Examples of Marine Animals Aristonectes parvidens

plesiosaur reptile

Haccourtaster sp.

starfish

Hoploscaphites pumilis

ammonite mollusk

Keuppia levante

octopus (mollusk)

Maiaspondylus lindoei

ichthyosaur reptile

Micropycnodon kansasensis

bony fish

Mosasaurus missouriensis

mosasaur reptile

Pentaditrupa subtorquata

annelid

Prehepatus werneri

crab

Squalicorax falcatus

shark

Examples of Continental Animals Alphadon marshi

marsupial-like mammal

Anatotitan copei

hadrosaur dinosaur

Ankylosaurus magniventris

herbivorous dinosaur

Aurorachelys gaffneyi

turtle

Beelzebufo ampinga

frog

Confuciusornis sanctus

toothed bird

Conodella suciensis

snail

Costasaurus sp.

lizard

Crephanogaster rara

wasp

Deinosuchus sp.

crocodile (continues)

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154 Cretaceous period, biodiversity in  154 Multicellular Biodiversity   in the Cretaceous Period (continued) Eomaia scansoria

placental-like mammal

Gallornis straeleni

modern bird relative

Hesperornis regalis

flightless bird

Ichthyornis dispar

bird

Lapparentophis defrenni

snake

Pachycephalosaurus sp.

dinosaur

Purgatorius unio

primatelike mammal

Quetzalcoatlus northropi

pterosaur

Shuvuuia deserti

feathered dinosaur

Sphecomyrma freyi

ant

Triceratops horridus

herbivorous dinosaur

Tyrannosaurus rex

predatory dinosaur

Velociraptor mongoliensis

feathered dinosaur

first entry regions caused sea levels to fall, then rise again when the glaciers melted (see table on pages 153–154). Continents. The massive continent of Pangaea continued to break apart, mainly into what would become the northern continents and the southern continents of today. Africa and South America split apart, allowing the southern part of the Atlantic Ocean to form. The Alps formed in Europe. India broke free from Gondwanaland and became a separate continent. The continents began to assume their modern shapes and locations. The geographical isolation of plants and animals on the newly separated continents allowed the evolution of new species in the separate areas. Marine life. Overall marine species diversity increased greatly over that of the preceding Jurassic period (see figure on page 155). ●●

Examples of Land plants Alnus sp.

alder

Diospyros primaeva

ebony

Ginkgo apodes

ginkgo

Ettingshausenia cuneifolia

sycamore

Ephedrites sinensis

ephedra

Ficus ceratops

fig

Juglans sp.

walnut

Laurus plutonia

laurel

Magnolia sp.

magnolia

Picea sp.

spruce

Pinus belgica

pine

*Based on Benton

­Cretaceous period was named for the deposits of chalk (Latin creta) that were abundant in European strata. In North America, the Cretaceous is divided into marine Mississippian deposits and coal-rich Pennsylvanian deposits. Climate. The mild climate of the Jurassic period continued into the Cretaceous period. Swamps and shallow seas covered widespread areas. As continents continued to drift apart, the climate over much of the land became cooler and drier during the Cretaceous. Occasional glaciations in the Antarctic

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●●

Invertebrates. The invertebrate fauna of the oceans began to assume a modern appearance. Among the mollusks, species of octopus (without external shells) became more common than ammonites and other shelled cephalopods, and starfish became more common than stalked crinoids among the echinoderms. The crustaceans (such as crabs) that are most common today were also the dominant crustaceans of the Cretaceous. Vertebrates. Bony fishes and sharks continued to diversify, while jawless fishes continued to diminish. Very large aquatic reptiles, such as the mosasaurs and the elasmosaurs (plesiosaurs with very long necks), lived in the oceans. Ichthyosaurs, which were reptiles that looked like porpoises, became less common, perhaps because of competition from modern forms of fishes that were diversifying during the Cretaceous.

Continental life. Terrestrial forests were transformed by the appearance of the angiosperms, or flowering plants, at or just before the beginning of the Cretaceous. The replacement of gymnosperm forests by angiosperm trees strongly affected the dominant animals. ●●

Plants. Gymnosperms had dominated all previous Mesozoic forests. Flowering trees evolved in tropical regions. Once they had evolved, they had an explosive increase in diversity as a result of coevolution with insects. During the Cretaceous period, these trees displaced most of the gymnosperms toward the polar regions. The forests of tropical and temperate regions began to look like they do today. By the end of

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Cretaceous period, biodiversity in 155





the cretaceous period, temperate forests were probably dominated by angiosperms such as maples, beeches, birches, magnolias, and walnuts, although it is difficult to assign cretaceous fossils to modern genera. the gymnosperm forests consisted mostly of conifers such as pines and spruces in mountainous and northern regions, where they are found today. Invertebrates. all modern groups of insects appear to have evolved by the Jurassic period, although the evidence of Mesozoic butterfl ies and moths is unclear. What is clear is that insects exploded in diversity during the cretaceous, especially the fl ies, ants and wasps, and probably the butterfl ies and moths, as a result of coevolution with flowering plants. these many new species of insects were mostly pollinators or consumers of flowering plants. Vertebrates. Freshwater and land vertebrates continued to diversify. Many lineages produced large animals. For example, the frog Beelzebufo (whose name means “devil frog”) was 16 inches (40 cm) long. Snakes are fi rst known from the cretaceous period.

Dinosaurs such as hadrosaurs, which may have specialized in eating gymnosperms, were abundant worldwide at the beginning of the cretaceous. as angiosperm forests spread, new kinds of dinosaurs, such as ceratopsians, evolved that specialized on them. the gymnosperms and the dinosaurs that ate them were displaced into the polar regions, which were cold but not nearly as cold as today. Primitive birds may have driven flying reptiles, such as pterosaurs, toward extinction during the cretaceous, although some of the largest pterosaurs,

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Some animals of the Cretaceous period: (A) Ankylosaurus was a heavily armored dinosaur. (B) Oviraptor was a dinosaur that laid eggs in clutches and protected them. The first scientists to discover Oviraptor fossils believed that it had stolen the eggs from another dinosaur. (Oviraptor means “egg thief.”) Oviraptor, and many other dinosaurs, protected their eggs just as birds do. (C) Triceratops dinosaurs. (D) In the oceans, ichthyosaur reptiles resembled modern dolphins.

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156 crustaceans  156 such as Quetzalcoatlus, lived at this time. Many of the small predatory dinosaurs were feathered, as in the Jurassic period, but these fossils provided chemical evidence of feathers. A Shuvuuia had traces of the kind of keratin found in feathers, and Velociraptor had quill knobs on its bones. There were about 100 genera of Cretaceous dinosaurs that looked like modern birds. They had greater specialization to specific ways of living than did those of the Jurassic. For example, Hesperornis was a flightless, nearly wingless diving bird. Confuciusornis, like modern birds, had no teeth, but it was not ancestral to modern birds; the ancestors of modern birds, similar to Hesperornis and Ichthyornis, still had teeth. Ichthyornis could probably be mistaken for a gull, except for the teeth. Gallornis was similar to the common ancestor of all surviving birds. About 90 genera of mammals lived during the Cretaceous. They were small and represented by few species compared to the dinosaurs. One species, Repenomamus robustus, was large enough to eat small dinosaurs; one of them died with a baby dinosaur in its stomach. Many of the mammals were in lineages, such as the Gondwanatheria and the Multituberculata, that are extinct today, but the modern mammal groups apparently evolved during the Cretaceous. Alphadon may have been a primitive marsupial, and Eomaia may have been one of the earliest placental mammals. Purgatorius may have been related to the earliest primates. Extinctions. No major extinction event separated the Jurassic from the Cretaceous periods. Many dinosaur lineages went into decline during the Cretaceous, while new groups of dinosaurs evolved. Some, but not all, dinosaurs would probably have become extinct even if the Cretaceous extinction had not occurred. This extinction event was caused largely by an asteroid that hit Earth 65 million years ago. The large marine and flying reptiles also became extinct at the end of the Cretaceous. The extinction of the dinosaurs allowed mammals to diversify into the forms that dominated the Cenozoic era. See also Cretaceous extinction; flowering plants (angiosperms). Further Reading Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Coiffard, C., et al. “Early Cretaceous angiosperm invasion of western Europe and major environmental changes.” Annals of Botany 100 (2007): 545–553. Falcon-Lang, H. J., and D. J. Cantrill. “Leaf phenology of some mid-Cretaceous polar forests, Alexander Island, Antarctica.” Geological Magazine 138 (2001): 39–52. Field, T. S., and N. C. Arens. “Form, function, and environments of the early angiosperms: Merging extant

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first entry phylogeny and ecophysiology with fossils.” New Phytologist 166 (2005): 383–408. Kaer, Benjamin P., et al. “Unusual gut contents in a Cretaceous ichthyosaur.” Proceedings of the Royal Society of London B (Biology) 270 (2003): S206–208. Lehman, Thomas M., and Elisabeth A. Wheeler. “A fossil dicotyledonous woodland forest from the Upper Cretaceous of Big Bend National Park, Texas.” Palaios 16 (2001): 102–108. Morell, Virginia. “When sea monsters ruled the deep.” National Geographic, December 2005, 58–87. Schweitzer, Mary Higby, et al. “Beta-keratin specific immunological reactivity in feather-like structures of the Cretaceous Alvarezsaurid, Shuvuuia deserti.” Journal of Experimental Zoology B (Mol Dev Evol) 285 (1999): 146–157. Skelton, Peter, et al. The Cretaceous World. New York: Cambridge University Press, 2003. Turner, Alan H., et al. “Feather quill knobs in the dinosaur Velociraptor.” Science 317 (2007): 1,721. ———, et al. “A basal dromaeosaurid and size evolution preceding avian flight.” Science 317 (2007): 1,378–1,381. Wilson, Edward O., and Bert Hölldobler. “The rise of the ants: A phylogenetic and ecological explanation.” Proceedings of the National Academy of Sciences USA 102 (2005): 7,411–7,414. Xu, X., et al. “Basal tyrannosauroids from China and evidence for protofeathers in tyrannosauroids.” Nature 431 (2004): 680–684.

crustaceans  Crustaceans are a major group of

mostly aquatic arthropods. Crayfish, lobsters, crabs, shrimp, barnacles, and many components of microscopic plankton are crustaceans. Most crustaceans have exoskeletons that cover the entire body, although the more than 500 species of hermit crabs have unprotected abdomens and must find shells of dead mollusks in which to live. Typical crustaceans have two pairs of feeding appendages, unlike other arthropods. Crustaceans exhibit an astonishing diversity of ways of making a living. Most are fully aquatic, but some live on land. Some isopods, such as pill bugs, live in the moist soil beneath rocks. Some crabs live on land, though usually on islands not far from the sea. Christmas Island, in the Pacific Ocean, has 14 species of land crab. One of these species, the red crab Gecarcoidea natalis, has a population of more than a hundred million on this island (see figure on page 157). Land crabs breed in the ocean and breathe with gills. The exoskeleton covering the gills is inflated and contains blood vessels that can extract oxygen from air. Some tropical hermit crabs are also terrestrial. One of them, Coenobita clypeatus, lives in trees. Snapping shrimp use their

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crustaceans  157

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carapace. The head has six segments, with appendages that include mouthparts and large and small antennae. The thorax has eight segments, each with a pair of legs, that can be pincers, walking legs, or small legs that manipulate food. The thorax is covered by a shell or carapace. The abdomen has six segments, with small legs, some of which are modified for swimming.

The largest group in the Malacostraca is the decapods, which include crabs, crayfish, lobsters, prawns, and shrimp. Decapods (from Latin for “ten legs”) have five pairs of walking legs on the thorax. They manipulate food with the appendages of the head, which are sometimes modified into large pincers. The appendages of the abdomen are often modified for swimming. The females of most decapods carry the fertilized eggs beneath their abdomens until they hatch. Important groups of decapods are: ●●

Massive populations of red crabs (Gecarcoidea natalis) periodically migrate across Christmas Island in the Indian Ocean.  (Attorney General’s Department, Australian Government)

claws to produce a shock wave that is strong enough to actually kill small prey. Pentastomes look just like parasitic worms that live in vertebrates, with few external features to identify them as crustaceans. Previous to the study of DNA evidence, they were classified in their own phylum. Some crustaceans have complex behavior. Several dozen individuals of a species of Atlantic spiny lobster, Panulirus argus, form long lines and maintain touch contact with their antennae. Migrating in long lines reduces the drag from water currents and gives them protection from predators—not unlike a V of migrating geese. Some species of snapping shrimp form colonies, with a reproductive queen, inside sponges. Evolutionary diversification of crustaceans began very early in the history of multicellular life. By the early Cambrian period, several crustacean lineages had already differentiated. This makes it difficult to reconstruct the evolutionary history of this group of arthropods. The most diverse and well-known group of crustaceans are the Malacostraca. Their bodies have these characteristics. ●●

The cephalothorax consists of the head and thorax and is usually covered by a protective

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True shrimp are primarily marine filter feeders with large populations. They are able to swim backward rapidly. A female shrimp can release up to a million eggs, which hatch into tiny nauplius larvae that live on yolk reserves. They develop through a series of larval phases until they resemble small adults. Many shrimp migrate into estuaries at this stage. The preservation of shrimp populations, on which many marine fish depend, is one reason estuaries must be protected. Prawns differ from true shrimp primarily in having branched gills. Lobsters are mostly solitary marine predators. Their front legs are modified into large pincers. They can live for up to a century, and some have reached 44 pounds (20 kg). Crayfish (or crawdads) are omnivorous freshwater relatives of lobsters. They occasionally live in mud burrows.

Other decapods include the following. In stenopods (from Greek for “narrow feet”), it is the third pair of walking legs that is modified into large pincers. In the blind polychelids (from Greek for “many claws”), most or all of the walking legs have claws. In achelates (from Greek for “no claws”), often called spiny lobsters, none of the legs have claws, and the antennae are very large. Other groups of Malacostraca include the following. ●●

Krill (euphausids) look like shrimp but are usually smaller, and the head and thorax are

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158 cultural diversity  158

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fused together. They are very abundant filter feeders and the basis of many marine food chains. Baleen whales eat large quantities of them. Isopods are flattened vertically and have seven pairs of legs. Most are aquatic, but some have diversified into terrestrial habitats. Pillbugs (genus Armadillidium), also known as woodlice, roly-polies, or crawlyballies, live in moist recesses under rocks and logs, where they scavenge dead plant material. Amphipods look like shrimp but are flattened from side to side. Some of the appendages of the thorax are enlarged into pincers. Mantis shrimp (stomatopods) are not shrimp. They are predators with powerful pincers. Some groups of malacostracans are simple organisms of caves or hot springs.

Other groups of crustaceans, aside from malacostracans, include the following. ●●

●●

●● ●●

The maxillopods are crustaceans with reduced abdomens and include the copepods and the barnacles. Adult barnacles cement themselves to solid surfaces (including the skins of whales) in the ocean and secrete a limestone shell. Their legs have modified into comblike structures with which they sweep in small bits of food. The arrangement of organs within the adult barnacle gives little hint to its arthropod identity, and barnacles were once considered mollusks until the larval form of the barnacle, with recognizable arthropod features, was identified. Many barnacles attach directly to rock and other surfaces, while some, such as gooseneck barnacles, grow a stalk. Some, such as genus Sacculina, are parasites of other crustaceans. Branchiopods are small, shrimplike crustaceans that live as plankton in fresh, brine, salt, and hypersaline conditions. They have flattened abdominal appendages that have gills, and they have hairs that help trap small particles of food. They have two pairs of antennae, the second of which is used for propulsion. Because they breed abundantly, brine shrimp (genus Artemia, also known as sea monkeys) and Daphnia are used as fish food and as experimental organisms. Ostracods are small, flattened, planktonic crustaceans. Remipedia and Cephalocarida are groups of blind, elongated marine crustaceans.

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first entry Many of the 35,000 species of crustaceans are abundant and important parts of aquatic food chains. See also arthropods. Further Reading Bayly, Ian A. E., and Geoffrey A. Boxshall. “An all-conquering ecological journey: From the sea, calanoid copepods mastered brackish, fresh, and athalassic saline waters.” Hydrobiologia 630 (2009): 39–47. Browder, Joan A., and Michael B. Robblee. “Pink shrimp as an indicator for restoration of Everglades ecosystems.” Ecological Indicators 9 (2009) (supplement): S17–S28. Cumberlidge, Neil, et al. “Freshwater crabs and the biodiversity crisis: Importance, threats, status, and conservation challenges.” Biological Conservation 142 (2009): 1,665–1,673. Duffy, J. E. “Eusociality in a coral reef shrimp.” Nature 381 (1996): 512–514. MacDonald, C. D., et al. “Queuing behavior of the Hawaiian spiny lobster Panulirus marginatus.” Bulletin of Marine Science 35 (1984): 111–114. Schram, F. Crustacea. New York: Oxford University Press, 1986. Taylor, Jennifer R. A., and William M. Kier. “Switching skeletons: Hydrostatic support in molting crabs.” Science 301 (2003): 209–210. Versluis, Michel, et al. “How snapping shrimp snap: Through cavitating bubbles.” Science 289 (2000): 2,114–2,117.

cultural diversity  Genetic diversity is essential

for the continued evolution and survival of wild populations of organisms; it is an essential part of biodiversity. In animal populations, mimetic, or cultural, diversity is also very important to survival and continued evolution. This fact has tremendous implications for the preservation of animal biodiversity on this planet. The evolution of animal adaptations has frequently occurred by gene-culture coevolution. Animal populations invent new behavioral patterns (often done by one or a few brilliant individuals within the population) that are an important component of their success. These behavioral patterns are not encoded in the genes. However, they create a situation in which natural selection favors genetic traits that facilitate the behavior patterns. Over time, the behavior may even become genetically encoded. In many cases, however, the traits are useless unless the animals have learned the behavior that makes use of them. The behavioral patterns themselves are transmitted through learning. Passive learning occurs when young animals watch adults handling prey and working out social interactions. In a few cases,

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cultural diversity  159 nonhuman animals actively teach their young. Adult meerkats, for example, partially disable their prey (scorpions) so that the young meerkats can easily kill and eat them, and the adults disable the prey less for older juveniles than they do for younger juveniles (see figure). If the chain of transmission is broken, the cultural component of adaptation can be lost forever. This has occurred several times when wild animal populations have been driven into extinction and conservationists have reintroduced zoo animals into the habitats. Animals that have been fed by zookeepers do not know how to hunt. Sometimes, there are even more basic behavioral lapses suffered by zoo animals reintroduced into the wild. Bears have been extinct in the forests of northern France for centuries, and when zoo bears were released there in the early 21st century, some of them fell off of cliffs and died. The zoo bears had not learned what cliffs were. Bears with mental problems, which would probably have died in the wild, can survive in captivity. It was one of these “psychotic” bears that wreaked havoc in France when it was released. The basic structure of bird songs is encoded in their brains, but young birds learn their specific songs from listening to adults. Occasionally, birds learn the songs of the wrong parental species. The repertoire of bird song is lost when hatchlings raised by humans are the founders of new populations. In zoos, at least a limited amount of cultural transmission occurs from one generation to another. If an extinct or nearly extinct species is produced by cloning, even this limited amount of cultural information is lost. The guar is a nearly extinct Southeast Asian wild cow. Researchers at Advanced Cell Technologies cloned a guar inside the egg and with surrogate mother of the domesticated cow in late 2000. Even though it apparently had no genetic defects, the young cloned guar died shortly after birth from a bacterial infection. Even if it had survived, it would have been helpless if introduced into the wild. Some researchers want to clone mammoths and mastodons inside the eggs and with surrogate mothers of elephants in order to reintroduce them into habitats in which they once lived. Such animals may, in time, invent new cultural adaptations. The genetic rescue of endangered species is better than extinction, but the preservation of wild populations is a far superior process, not least because the lines of cultural transmission are intact. Europeans and white Americans once considered human cultural diversity to be debris that the advance of white civilization would clear away. The eradication of tribal cultures was official policy, even when the lives of the people were spared. The Indian schools of the United States were a notorious

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Many vertebrate species, such as these African meerkats, have complex social behavior, which is an adaptation culturally transmitted from one generation to the next.  (Vivapets)

example, in which children from many tribes were boarded, taught English and the white American lifestyle, and forbidden to speak in their native languages. In the 20th century, European and white American cultures began to realize that native cultures were valuable in their own right, and both they and the tribes tried to rescue the remains of sometimes shattered cultures. Today, for example, there may be no member of the Cherokee tribe who cannot speak English. The Cherokee language is therefore unnecessary for tribal survival. Nevertheless, the tribe puts much effort into maintaining the language, which includes a unique written syllabary invented by the Cherokee scholar Sequoyah in the early 19th century. The tribe not only prints many articles in both English and Cherokee in the tribal newspaper, but has begun immersion schools in which the students must speak Cherokee. The preservation of tribal languages and cultures is not merely an attempt to counteract the unfair practices of the past. Each language represents a uniquely different way of understanding the world and organizing mental concepts. The huge corpus of human knowledge, far exceeding the capacity of any group of people to memorize and transmit, is perhaps the most important human adaptation. Human cultural

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160 cyanobacteria  160 diversity is therefore an essential part of this adaptation. Scholars have used language analysis along with genetic analysis to reconstruct the history of human migrations. Therefore, the preservation of cultural diversity is important to understanding human history as well as to promoting the continued success of the most important human adaptation. Further Reading BBC News. “Endangered animal clone dies.” Available online. URL: http://news.bbc.co.uk/1/hi/sci/tech/ 1113719.stm. Accessed March 21, 2009.

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first entry Campbell, Matthew. “ ‘Psycho’ bear tears apart eco-idyll.” Sunday Times (London), (July 29, 2007). Available online. URL: http://www.timesonline.co.uk/tol/news/ world/europe/article2159387.ece. Accessed May 12, 2011. Thornton, Alex, and Katherine McAuliffe. “Teaching in wild meerkats.” Science 313 (2006): 227–229.

cyanobacteria  See bacteria.

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D darwin,  Charles (1809–1882) British Evolutionary scientist charles Darwin (see figure) was the scientist whose perseverance and wisdom changed the way professional scientists, amateurs, and almost everyone else viewed the world. He explained where all biodiversity comes from. Darwin presented a convincing case that all life forms had evolved from a common ancestor and for a mechanism, natural selection, by which evolution occurs. earlier scholars had proposed evolutionary theories, but, until charles Darwin, no proposals of evolution were credible. Perhaps just as important is the fact that he explained that all the diversity of life sprang from a common ancestor. charles Robert Darwin was born February 12, 1809, in Shrewsbury, england, the same day that abraham lincoln was born in the state of Kentucky. Both men, in different ways, led the human mind to consider new possibilities and freedoms without which future progress would not have been possible. Darwin, like many other aristocratic englishmen, was born into a rich and inbred family. His father, Robert Darwin, was a prominent physician, and his mother, Susannah Wedgwood Darwin, was an heir of the Wedgwood pottery fortune. Robert Darwin and Susannah Wedgwood were, in addition, cousins. Unlike other rich, inbred englishmen, charles Darwin was to put his inherited wealth to better use than perhaps anyone ever has. the Darwin family was respectably but not passionately religious. Robert Darwin was secretly a freethinker but remained associated with the anglican church. Susannah Darwin continued the Wedgwood family tradition of Unitarianism. the family had a history of creative thinking that went beyond the bounds of common opinion. Robert Darwin’s

father, erasmus, also a physician, doubled as a poet and wrote books in which he openly speculated on evolution—even to the extent of suggesting that life began in a warm little pond from nonliving chemicals. charles Darwin grew up, however, with a negative view of evolution. the only major evolutionary theory that had been considered by scientists was that of Jean Baptiste de lamarck, which to the British elite was associated with the chaos of the French Revolution. While young Darwin was not repressed into religious narrowness, he explored the path of evolutionary theory hesitantly and on his own. though not passionate about religious doctrine, the Darwin and Wedgwood families were passionate about the religious argument against slavery. Both families contributed considerable money to the antislavery movement in england and put much personal effort into publicizing the abuses of slavery and insisting that england prohibit slavery in all of its colonies. the Wedgwood fortune came from the production of ceramics. charles Darwin’s uncle, Josiah Wedgwood, produced the famous plaque that depicted a slave in chains, with the words, “am i not a man and a brother?” and distributed thousands of them free of charge. charles Darwin was raised to hate slavery. Meanwhile, there was plenty of opportunity for charles Darwin to develop scientific interests. His family kept a dovecote, and he collected insects and rocks and performed chemical experiments (earning the nickname “Gas” among his friends). Darwin got none of this important training from the schools he attended. He learned adequately in school, but nothing except direct contact with the world of nature inspired him. Being a naturalist, however, was not a career. When it came time for him to go to college, 161

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162 Darwin, Charles 162 he followed his older brother to the University of Edinburgh to study medicine. Darwin stayed in Edinburgh about a year. First, he could not keep his mind on the study of medicine. He spent more time attending lectures in geology and zoology and was more interested in the reproduction of marine invertebrates than in surgery. During his brief stay, he was exposed to some of the radical anticlerical views of fellow students and even of one professor, the zoologist Robert Grant, who openly defended Lamarckian evolution. Edinburgh University, being free from Anglican theology, was a haven for scientific and political debate. While Darwin experienced the bracing atmosphere of free inquiry, he also saw what could happen if one went too far. One student presented a paper at a local scientific society claiming that the human mind consisted only of the brain, without any soul; his remarks were stricken from the record. During his year and a half in Edinburgh working with Grant, Darwin learned how to conduct scientific research, and he presented his first paper there in 1827 on a discovery he had made about the life cycle of the cnidarian Flustra. Second, Darwin could not stand the sight of blood. When he had to witness operations administered without anesthesia, he decided to abandon plans for a medical career. Another experience that Darwin had in Edinburgh was formative of his entire future. He hunted animals, primarily birds, and wanted to learn to preserve them. He learned taxidermy from a freedman named John Edmondstone, who had been a slave in South America. Darwin spent a lot of time talking to him and discovered three things. First, he wanted to travel the world and see some of the amazing diversity of plants and animals that John described. Second, he heard eyewitness accounts (as opposed to the second-hand stories his family used in their tracts) of the brutality experienced by black slaves in South America. Third, he learned that black people were no less intelligent and had the same capacities for emotion and morality as the British whites— which put him in conflict with many leading British intellectuals. After leaving Edinburgh, Darwin chose to attend Cambridge and study theology. He planned to become a country parson. At the time, when the Church of England was securely supported by the government, a country parson needed only to perform his round of duties, then he would have plenty of time for studying birds and flowers and rocks. Some of the best natural history studies, such as the Natural History of Selborne, written by parsonnaturalist Gilbert White, were the work of country ministers. Even at Cambridge, Darwin spent far more time attending lectures in science classes in

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first entry which he was not actually enrolled than in studying theology. He befriended the botany professor John Stevens Henslow and frequently went on field trips with the botany students. He was particularly passionate about collecting beetles. Robert Darwin was openly skeptical about the prospects for success of his son, who, he said, cared “for nothing but shooting, dogs, and rat-catching,” adding, “You will be a disgrace to yourself and all of your family.” At the last minute, before his comprehensive examinations, Darwin studied enough to earn a respectable grade in theology. There was one aspect of his theological studies that Charles was eager to pursue. He was required to read Reverend William Paley’s book Natural Theology, which maintained that the evidence of geology and biology strongly indicated that there was a Creator. At the time, the only alternative to natural theology was some unspecified and mysterious process of self-formation, of which most scientists were understandably skeptical. Little did Darwin, who nearly memorized the book, suspect that he would be the one to present a credible, nonmiraculous mechanism by which nature could design itself. Darwin’s future seemed clear to him: He would get married, assume a parsonage, and settle down to live in the country, where he could collect beetles forever. It would not pay much, but Charles was in line to inherit at least part of a small fortune. Then, at the last minute, an unexpected opportunity arose. The captain of the HMS Beagle, Robert FitzRoy, needed a companion for a voyage around the world. It was a scientific expedition dedicated mainly to surveying the major ports of the world (into which the British assumed they had unlimited access) but also to every other aspect of scientific exploration. The ship already had a naturalist, the ship’s surgeon, but the captain wanted a fellow aristocrat with whom to share meals and conversation. FitzRoy contacted Henslow, who told him the perfect person for the job would be Charles Darwin. It was hardly a job—Darwin had to pay his own way—but it was an opportunity to see the wonders of creation around the world in a way that, as it turned out, Darwin would never have again. FitzRoy interviewed Darwin and offered him the post. This voyage changed Darwin and changed the world. Robert Darwin at first refused to pay for his son’s trip, but Josiah Wedgwood convinced Robert to support Charles. During the 1831–36 voyage of HMS Beagle, Darwin was constantly putting his knowledge of natural history to work. The Beagle went down the east coast of South America to the west coast, across to Australia and the Indian Ocean, around Africa, and back to England. There were long periods in which the ship remained in harbor for surveying

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Darwin, Charles 163 work, during which Darwin was able to go ashore and travel far inland. This was fortunate for him, for he suffered constantly from seasickness. Darwin studied the geology of islands and coastlines; he collected fossils as well as plants and animals. He took careful notes on everything and periodically sent his specimens back to England. He visited tropical rain forests and the heights of the Andes Mountains. The rain forest was, for him, a particularly spiritual experience; one could not look at the beauties of such a forest, he said, without believing that there was more to man than merely the breath of his body. Even so, the voyage had more than spiritual inspiration for him. He read the first volume of the geologist Sir Charles Lyell’s famous and controversial Principles of Geology. While on the voyage, he received the other volumes and read them as well. He was convinced that Lyell was correct about the long ages of Earth history and the gradual changes that had occurred during them—in contrast to an Earth that had been recently created, or at least recently re-created, by a God whose main purpose was humankind. In addition to this, many of the things that Darwin saw made him question some aspects of his belief in creation. He collected fossils and found that animal fossils most nearly resembled the animals that were currently alive in the region. For example, South America is where llamas, capybaras, sloths, and armadillos now live; this is also where the fossils of extinct species of what appeared to be llamas, capybaras, sloths, and armadillos were found. Australia was the place to find most of the marsupials, and most of the marsupial fossils, of the world. It suggested strongly to him that the fossils represented ancestors of the animals now present, and when he saw the animals of the Galápagos Islands, he began to wonder if at least some species had come into existence on the islands where they were now found. Darwin also had experiences with people on this voyage that would influence his later thoughts about evolution and biodiversity. In particular, one of the objectives of the Beagle voyage was to return three Fuegian Native Americans to their tribes as missionaries. Two men and one woman had been captured from a Fuegian tribe and taught Christianity and English life. Now they were going back to enlighten their tribe. Instead, they reconverted to their tribal ways. This made Captain FitzRoy upset but made Darwin think about why the people whom Europeans called primitive had levels of intelligence nearly or completely equal to theirs. He also saw slaves in Brazil (he did not visit the United States) and developed a deep hatred of slavery and of violent and brutal European colonialism. In particular, he was bothered by the way slave owners used Bibli-

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Charles Darwin in old age 

cal passages to justify slavery. Perhaps these experiences laid the groundwork for his later rejection of Christianity. Darwin’s firsthand observations in South America not only filled him with a lifelong hatred of slavery but also had an important, and perhaps the decisive, effect on his views of evolution and biodiversity. He believed passionately that all humans had a common ancestor, that the darker races were not separate creations. He jotted his thoughts in secret notebooks, which scholars have now analyzed. In one passage, he clearly links the idea that all species have a common ancestor to his belief that all humans have a common ancestor. Darwin returned to England as he had left, still believing in some form of creationism, but his mind was prepared for rapid changes of viewpoint. Upon his return, he found that he had become a bit famous among the scientific community because of his correspondence and his specimens. Lyell, instead of just being a hero who wrote a book, became a friend. Darwin spent a couple of years in London cataloging his specimens and writing his travel notes, which became a popular book, The Voyage of HMS Beagle. Darwin married his cousin Emma Wedgwood. Emma was very firmly religious. Even before marriage, Darwin had already begun to entertain doubts about the religious view of the world. In later years, as Darwin developed his evolutionary theories, he

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164 Darwin, Charles 164 had an ever more difficult time reconciling them with Christianity, even though some of his friends (especially the Harvard botanist Asa Gray) managed to retain conventional Christian faith while embracing evolutionary science. By the end of his life, Charles Darwin was an agnostic. Historians have considered that the death of Darwin’s beloved daughter Annie at age 10 may have been the precipitating factor in making him abandon belief in, at least, a providential God. All this time, Darwin was in great pain that his loss of faith was distressing to Emma, which indeed it was. When they wrote notes to each other about it, she remained his loyal partner even though she feared he was losing his soul, and he responded, “You do not know how many times I have wept over this.” Darwin’s religious agnosticism, therefore, was not easy or arrogant but came at the expense of the pain that he caused his dearest friend. Charles and Emma bought a country house in Down, just far enough from London to be able to visit it but not be bothered by it. As it turned out, it would not have mattered how far away from London he lived, because Darwin became ill at this time, remained so for the rest of his life, and hardly ever traveled. He suffered recurring symptoms of headaches, heart flutters, indigestion, boils, muscle spasms, and eczema, on which he kept scientific notes but for which neither he nor any physician had a solution. Several possibilities have been proposed for the cause of Darwin’s illness. Some scholars have suggested that he had contracted Chagas disease, caused by a parasite from a bug bite, while in South America. This is unlikely, because Darwin was developing some of his symptoms shortly before the voyage began. Other scholars have suggested that his illness was genetic in origin and resulted from the inbreeding of the Darwin and Wedgwood families. Emma’s brother Josiah and his wife, who were also first cousins, lost a sickly baby. It has also been suggested that recessive mutations from inbreeding caused the death of Darwin’s daughter Annie. The most commonly accepted explanation is that Darwin was nervous about announcing his controversial theory to the world. Emma was the perfect companion and nurse. Emma’s care and friendship enabled Darwin to continue his research and writing despite his illness and despite the criticisms he received throughout his life. She would play the piano for him, and they would read together in the evenings. The conclusion seems inescapable that Charles Darwin could not have accomplished what he did had it not been for Emma. Darwin’s illness kept him home, and his wealth meant that he did not have to work. He was, accordingly, able to devote full time to the study of science—that is, the few hours of the day in which he

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first entry was not suffering the symptoms of his malady. He read every scientific book and article he could find and corresponded widely with fellow scientists all over the world. The solitude, especially during his strolls on the Sandwalk around his property, allowed him to think. He put the time to good use, not only proposing the modern theory of evolution, but also almost singlehandedly inventing the sciences of ecology, pollination biology, and plant physiology. Until the very end of his life, he noticed things that hurried and shallow people did not: His last book was about the slow but cumulative effects of earthworms on transforming the landscape and creating the soil. It was not long after the Darwins moved to Down House that Charles had to deal with a crisis of thought. By 1837, he had worked out the theory of natural selection. He thought of natural selection, first, because he was very familiar with individual differences within populations, whether of pigeons or of people, and second, because he realized that populations could grow rapidly. He got the latter idea from reading Malthus’s Essay on Populations. Malthus said that because populations grow by doubling but that resources increase, if at all, only in a linear fashion, then people were condemned to an eternal cycle of overpopulation and famine. Though Malthus, a clergyman, used this argument against the concept of Divine Providence, he nevertheless concluded that humankind made progress because of this suffering. Darwin, his Christian faith already slipping, undoubtedly rejected Divine Providence along with Malthus, but he also realized that the whole world of plants and animals was similarly condemned to eternal overpopulation. Out of this crisis came an insight that changed the world. Darwin realized that overpopulation in nature could be a creative force as well as a destructive one, just as Malthus had seen it to be for the human species. The superior individuals in a population would be the ones to survive, and this would cause the population to evolve. One of the consequences of Malthus’s doctrine was the political opinion that any attempts to help the poor through public works and welfare would only cause their populations to grow larger and to increase the total sum of their misery. Throughout Darwin’s adult life, there were riots and political movements in which the poor and their populist leaders threatened the entrenched powers of lords, priests, and the leaders of industry. A new set of Poor Laws in England specifically invoked Malthus as the justification for forcing the poor to leave England, work for lower wages, or be content with poverty. The political theory of the Malthusians was that ruthless competition among companies guaranteed the progress of England and of humankind.

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Darwin, Charles 165 It was exactly the political viewpoint that philosopher Herbert Spencer would later defend, inventing the phrase “survival of the fittest.” Darwin feared that by incorporating Malthus into his theory of natural selection, he might be seen to side with those who oppressed the poor, an association he did not desire. Even today, Darwinian natural selection is often associated with ruthless competition. The novelist Kurt Vonnegut, for example, said that Darwin “taught that those who die are meant to die, that corpses are improvements.” During the 20th century, evolutionary scientists proposed ways in which natural selection could lead to cooperation rather than just to competition. Darwin began to keep a notebook on the subject of natural selection but told almost nobody about it for many years. He had seen what would happen if someone came up with a half-baked theory of evolution and rushed it into print: An anonymous author (now known to be Robert Chambers) wrote such a book in 1844. Darwin did not want his theory to suffer such deserved ridicule. He was afraid to admit that he accepted evolution (called at that time transmutation) partly because it was the reigning doctrine of political revolutionaries. He told his friend the botanist Sir Joseph Hooker that admitting that he believed in transmutation was “like confessing a murder.” Darwin wanted to make sure that he had all the scientific facts in order, to certify every aspect of his theory, before he published it. This was a tall order. Darwin had to demonstrate that populations of plants and animals did have a tremendous amount of variability, that plants and animals did experience overpopulation and other natural stresses, that selection can produce significant changes in populations, and that an evolutionary explanation fit the facts of geology and of the distribution patterns of plants and animals. He gathered information for 21 years, showing that pigeon breeders could use artificial selection to produce astonishing new varieties starting only with the variation present in wild pigeon populations, that plants and animals did suffer the same population stresses that humans do, and that an evolutionary pattern would explain the living and extinct species of barnacles. Darwin spent eight years studying every kind of barnacle in the world, living or extinct. It became quite a burden to him; no man, he said, hated a barnacle quite as much as he did. His son George grew up seeing him study barnacles, and he assumed that is what grownups did. George asked one of his friends, “Where does your father study his barnacles?” Darwin’s evidence piled up, nicely matching his theory of natural selection, but after 21 years, he had hardly begun. He might have worked until he died without completing the “big book” in which he planned to explain everything.

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In 1858, Darwin received a letter and manuscript from Alfred Russel Wallace, a young English naturalist in Indonesia. Wallace had figured out all the same aspects of natural selection that Darwin had, only he was ready to rush into print with it. Fortunately, Darwin had written a brief summary of his theory in 1842 and had shown it to Lyell, Hooker, and Emma. Lyell could therefore vouch that Darwin had thought of natural selection first. Natural selection was presented as a joint theory of Darwin and Wallace in 1858. Some scholars, such as the science historian Loren Eiseley, have said that evolution by means of natural selection was an idea that was in the air already, and Darwin happened to be the first person to write about it. The science historian Peter Bowler has pointed out, however, that Darwin’s version of evolution differed strikingly from all the others, even from that of Wallace, who had not thought of the importance of plant and animal breeding as evidence for the heritable variation within natural populations. For the next year, Darwin worked on what he considered to be only a brief abstract of his ideas, which became a 400-page book, On the Origin of Species by Means of Natural Selection. The editor of the Quarterly Review read an advance copy of the book. He thought it was good but that nobody would be interested in it. He suggested that Darwin write a book about pigeons instead; he pointed out that everybody likes pigeons. However, he was wrong about the popular reception of Darwin’s book. The first printing, 1,250 copies, of The Origin of Species sold out the first day. Perhaps the buyers of Origin of Species were expecting to find something about human evolution in this book, but Darwin stayed away from that subject, saying only that “Light will be thrown on the origin of man and his history,” a statement that remained unchanged in later editions. In the Origin of Species, Darwin argued convincingly that all life had a common evolutionary origin and history and that evolution was caused by natural selection. When Darwin’s friend Thomas Henry Huxley read it, he is reported to have said, “How stupid not to have thought of this before!” It was primarily to the fact of evolution rather than to the mechanism of natural selection that Huxley referred. Natural selection remained a theory seldom embraced until the 20th century. The codiscoverer of natural selection, Alfred Russel Wallace, defended both evolution and natural selection but argued from it (quite differently from Darwin) that the human mind was a product of miraculous creation. Darwinian evolution (soon called Darwinism) survived numerous attacks, for example from the biologist St. George Jackson Mivart. Some of the criticisms, such as those of the engineer Fleeming Jenkin, stemmed

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166 Darwin, Charles 166 not so much from problems with evolution as from the fact that biologists did not as yet understand how genetic traits were inherited. One of his fiercest critics was a man who had once been his friend, the anatomist Richard Owen, who accepted some aspects of transmutation but vehemently rejected Darwin’s nontheistic mechanism of it. After this brief flurry of controversy, within a decade most scientists had accepted Darwin’s proposal of the fact of evolution. (Creationism is primarily a product of the 20th century.) Darwin, being ill, did not defend his views in public. He left this primarily to his “bulldog” friend Huxley. Meanwhile, in America, it was the botanist (and traditional Christian) Asa Gray who publicly defended Darwinian evolution. The world did not have to wait long for Darwin to make very clear statements about human evolution. In 1871, he published a book, The Descent of Man, stating that humans evolved from African apes. Since the size of the human brain and the diversity of human racial characteristics seems to be almost outlandish in proportion to what survival would require and natural selection would produce, Darwin proposed another mechanism of evolution in this same book: sexual selection, by which characteristics evolved in one sex because they were pleasing to the other sex, allowing the individuals that had these characteristics to produce more offspring. In case anyone thought Darwin meant that only the human body had evolved and not the human spirit, they could read another of his books, The Expression of Emotions in Men and Animals. Darwin made yet other very important contributions to the study of biodiversity. Three of them were about pollination. He showed how intricate the process of coevolution could be in his 1862 book about the pollination of orchids. For one flower, the pollinator of which was unknown, Darwin predicted that the pollinator would be a long-tongued moth. Decades after Darwin’s death, this pollinator was discovered, exactly as Darwin had predicted. In an 1876 book, he compared cross-pollination with self-pollination. In 1877, he wrote a book about different forms of flowers on the same plant. He wrote other books about plants, including two books (1875 and 1880) in which he described the ways in which plants move. He also studied and wrote a book about carnivorous plants in 1875. His last book, in 1881, was about the role of earthworms in the formation of soil. All these books were based upon his own greenhouse or field observations and measurements. Although Charles Darwin remains a popular target for antievolutionists and for evolutionists who have their own new theories of evolution, the care-

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first entry fulness of Darwin’s work and breadth of his imagination have assured that his theory has survived far longer than he might have imagined. His personal integrity and humility have also made him one of the most admired scientific figures in history. Darwin not only made the study of evolution, but of biodiversity, possible. As the evolutionary biologist Olivia Judson wrote, Before the “Origin,” similarities and differences between species were mere curiosities; questions as to why a certain plant is succulent like a cactus or deciduous like a maple could be answered only, “Because.” Biology itself was nothing more than a vast exercise in catalog and description. After the “Origin,” all organisms became connected, part of the same, profoundly ancient, family tree. Similarities and differences became comprehensible and explicable. In short, Darwin gave us a framework for asking questions about the natural world, and about ourselves.

Charles Darwin died on April 19, 1882, while Emma was cradling his head in her arms. Darwin’s friends (primarily Huxley) successfully arranged to have him buried in Westminster Abbey, right next to Sir Isaac Newton. See also carnivorous plants; Darwin’s finches; natural selection; pollination; sexual selection; Wallace, Alfred Russel. Further Reading Adler, Jerry. “Charles Darwin: Evolution of a Scientist.” Newsweek, November 28, 2005: 50–58. American Museum of Natural History. “Darwin Digital Library of Evolution.” Available online. URL: http:// darwinlibrary.amnh.org. Accessed August 7, 2011. Armstrong, Patrick. Darwin’s Other Islands. London: Continuum, 2004. Boulter, Michael. Darwin’s Garden: Down House and the Origin of Species. Berkeley, Calif.: Counterpoint, 2009. Bowler, Peter J. “Darwin’s originality.” Science 323 (2009): 223–226. Browne, Janet. Charles Darwin: Voyaging. Princeton, N.J.: Princeton University Press, 1995. ———. Charles Darwin: The Power of Place. New York: Knopf, 2002. Darwin, Charles. Autobiography of Charles Darwin 1809– 1882. Edited by Nora Barlow. New York: Norton, 1993. Desmond, Adrian, and James Moore. Darwin: The Life of a Tormented Evolutionist. New York: Warner, 1991. ——— and ———. Darwin’s Sacred Cause: How a Hatred of Slavery Shaped Darwin’s Views on Human Evolution. Boston: Houghton Mifflin, 2009.

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Darwin’s finches  167 ———, ———, and Janet Browne. Charles Darwin. Oxford: Oxford University Press, 2007. Eiseley, Loren. Darwin’s Century: Evolution and the Men Who Discovered It. New York: Doubleday, 1961. Eldredge, Niles. Darwin: Discovering the Tree of Life. New York: Norton, 2005. Healey, Edna. Emma Darwin: The Inspirational Wife of a Genius. London: Headline, 2001. Judson, Olivia. “The origin of Darwin.” New York Times (February 12, 2009). Available online. URL: http:// www.nytimes.com/2009/02/12/opinion/12judson. html. Accessed May 13, 2011. Keynes, Richard Darwin. Fossils, Finches, and Fuegians: Darwin’s Adventures and Discoveries on the Beagle. New York: Oxford University Press, 2003. Lamoureux, Denis O. “Theological insights from Charles Darwin.” Perspectives on Science and Christian Faith 56 (2004): 2–12. Leff, David. “AboutDarwin.com: Dedicated to the Life and Times of Charles Darwin.” Available online. URL: http:// www.aboutdarwin.com. Accessed August 7, 2011. Loy, James D., and Kent M. Loy. Emma Darwin: A Victorian Life. Gainesville: University Press of Florida, 2010. Moore, James. The Darwin Legend. Grand Rapids, Mich.: Baker Book House, 1994. Quammen, David. The Reluctant Mr. Darwin: An Intimate Portrait of Charles Darwin and the Making of His Theory of Evolution. New York: Norton, 2006. Van Wyhe, John. “The complete works of Charles Darwin online.” Available online. URL: http://darwin-online. org.uk/Freeman_intro.html. Accessed July 7, 2011.

Darwin’s finches  Darwin’s finches are a group of 14 species of finches that inhabit the Galápagos Islands off the coast of Ecuador. The finches and the islands are famous because Charles Darwin visited them in September 1835 during an aroundthe-world trip on HMS Beagle. Because evolution is occurring rapidly in these finches, they represent an almost unique opportunity for studying evolution in action and seeing how new biodiversity develops. They have become perhaps the most famous examples of how biodiversity originates. Because the species are still differentiating, some experts classify the finches into a slightly different set of species than do other experts. As had every previous visitor, Darwin noticed the giant tortoises that are unique to the islands. He also observed that the islands seemed to have similar geography and climate yet were inhabited by slightly different groups of animals. He collected specimens of many of the small birds he found. Because their beaks were all so different from one another, Darwin did not recognize that the birds were all closely related finches. When Darwin returned to London,

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the ornithologist John Gould identified them as different species of finches. Darwin realized that each island might have had its own species of finch, but he had not taken careful notes regarding from which island he had obtained which finch specimen. Fortunately, other visitors to the islands, including Robert FitzRoy, the captain of the Beagle, had kept more careful notes. When Darwin published the account of his voyage on HMS Beagle, he had not yet begun to fully develop an evolutionary theory. A famous passage indicates that he had already begun thinking about evolution: “Seeing this gradation and diversity of structure in one small, intimately related group of birds, one might really fancy that from an original paucity of birds in this archipelago, one species had been taken and modified for different ends.” These finches, then, could be considered the spark that started the fire of evolutionary theory. Between 5 and 10 million years ago, a group of finches from the South American mainland migrated (or perhaps were blown by a storm) to the Galápagos Islands. From this original founding group, the 14 species of finches present today evolved (see table on page 168). Most of the finch species live on more than one of the islands, but none live on all the islands. No island in the Galápagos archipelago has its own unique species of finch. Some species live on or near the ground and eat seeds; others live on or in cactuses and eat seeds, pollen, and nectar; the others live in trees. The tree finches eat fruits, leaves, seeds, and insects, and one of them strips the outer bark and eats the rich inner bark. One group of finches, though it primarily consumes insects, occasionally drinks the blood or eats the eggs of seabirds such as bluefooted boobies. Some finches occasionally perch on iguanas or tortoises and eat the parasites from them. The finches have undergone adaptive radiation in two ways: first, by evolving on different islands, and second, by specializing on different food resources. One of the earliest extensive studies of these finches, which brought them to the attention of the world as an excellent example of evolution in action, was the 1947 study by David Lack. He visited for only four months, not long enough to get extensive data regarding the ongoing processes of evolution in these finch populations. He built an aviary, in which he was able to confirm that the different kinds of finches did not readily interbreed and were, therefore, different species. He showed that evolution had occurred, but his evidence did not show that evolution was still occurring. In order to obtain convincing evidence about natural selection, it is important to closely monitor entire isolated populations of organisms. If this is not done, the researcher cannot determine whether the disappearance of individuals is due to natural

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Darwin’s Finches Ground Finches Small ground finch

Geospiza fuliginosa

Medium ground finch

Geospiza fortis

Large ground finch

Geospiza magnirostris

Cactus finch

Geospiza scandens

Large cactus finch

Geospiza conirostris

Sharp-beaked ground finch

Geospiza difficilis

Tree Finches Small tree finch

Camarhynchus parvulus

Medium tree finch

Camarhynchus pauper

Large tree finch

Camarhynchus psittacula

Woodpecker finch

Cactospiza pallidus

Vegetarian finch

Platyspiza crassirostris

Gray warbler finch

Certhidea fusca

Olive warbler finch

Certhidea olivacea

Cocos finch

Pinaroloxias inornata

selection (the individuals die or fail to reproduce) or due to migration (the individuals leave). This was one of the problems with what had once been considered a classic study of natural selection, the zoologist H. B. D. Kettlewell’s studies on the peppered moths of Britain. Darwin’s finches provided a perhaps unique opportunity to study natural selection and other evolutionary processes, since they are isolated on different islands, to and from which they seldom migrate. A prodigious amount of work is required to keep track of each individual finch, how many offspring it produces, how it lives, and its physical characteristics, even with relatively small populations on small islands. Nevertheless, that is precisely what Peter and Rosemary Grant, evolutionary biologists at Princeton University, and their associates have been doing on some of the islands since the 1970s. Having monitored the lives of more than 20,000 individual finches they have been able to present convincing evidence of natural selection and other evolutionary processes at work. They can recognize the individual finches, and know the genealogies of each, the kinds and sizes of seeds that these individuals eat, and their individual songs as well as the kinds of seeds available on the islands and in what amounts.

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The Grants studied the beak sizes of Geospiza fortis ground finches and the relationship between beak size and the kinds of seeds that these finches ate. The ground finches eat seeds. Some plants (for example grasses) produce small seeds that are relatively easy to crack. These plants grow abundantly during rainy seasons. During dry seasons, large seeds (such as those of the puncture vine) are the most abundant. The large seeds also have very hard coats. Finches with larger beaks can crack larger seeds. The finches with smaller beaks can more easily handle the smaller seeds. A difference of less than a millimeter in beak size can make a tremendous difference in the food resources available to a finch. A finch with a 0.44-inch (11-mm) beak can crack open a puncture vine seed, while an individual with a 0.42-inch (10.5-mm) beak may not be able to do so. The individuals with smaller beaks may starve, or they may eat seeds from the Chamaesyce bush, which produces a sticky, milky sap. The sap gets on the heads of the birds. The birds use their heads to push gravel around as they search for seeds. The birds with sticky heads, when they do this, rub the feathers off the tops of their heads, leaving the skin exposed, which can lead to overheating of the brain, followed by death. As Darwin wrote, “the smallest grain in the balance, in the long run, must tell on which death shall fall, and which shall survive.” The Grants have gathered data about natural selection, character displacement, and incipient speciation among Darwin’s finches. Natural selection in finch populations. In order to show that natural selection is occurring, the Grants had to establish that the beak size differences among the individual Geospiza fortis birds are genetically based. To do this, the Grants switched eggs among nests and found that individual birds had beak sizes similar to those of their biological, not their adoptive, parents. Next, the Grants had to measure changes that occurred in genetically based characteristics, such as beak size. They measured beak sizes of Geospiza fortis during a long drought, when vegetation was sparse and most of the seeds came from the puncture vine. Then, during an El Niño Southern Oscillation event, a tremendous amount of rain fell, and the island was overgrown with plants that produced smaller seeds. Almost immediately, the average sizes of the birds and the sizes of their beaks began to decrease. When the drought returned and the plants that produced small seeds became progressively less abundant, the average body and beak size began to increase in the G. fortis population. This is an example of natural selection in action, first one direction, then the other.

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Darwin’s finches  169 Character displacement between finch species. Natural selection occurs not only in response to weather patterns but also in response to contact between species of finches. On the island of Genovesa, the large cactus finch Geospiza conirostris and the large ground finch G. magnirostris (which has a larger average beak size) live together. During rainy seasons, when there are plenty of seeds, both species exhibit a wide range of beak sizes, and there is overlap between the beak sizes of the largest G. conirostris and the smallest G. magnirostris. The finches in the zone of overlap would compete but do not because there are plenty of seeds for both. During droughts, when seeds become scarce, the two species specialize: Natural selection favors the G. magnirostris with the largest beaks but favors the G. conirostris with the smallest beaks. This is an example of character displacement between two species that minimizes competition between them. Character displacement is expected to occur only when two species are in contact, and this is precisely what we see with these finches. On the island of Española, the large ground finch G. magnirostris is absent. On this island, without competition from the large ground finch, the cactus finch G. conirostris has a much greater range of beak sizes regardless of the weather conditions. Competition between species has not only caused character displacement but may have caused some local extinctions as well. Generally speaking, finches that are very similar to one another in size and the type of food they eat are not found on the same island. The Grants documented in 2006 that natural selection favored larger beaks in the medium ground finch, G. fortis, during a drought in 1977, but during a 2003 drought, after the large ground finch G. magnirostris had invaded the island, natural selection favored smaller beaks. Competition had caused evolution to proceed in the opposite direction. Incipient speciation. The Grants have also observed some possible examples of speciation beginning to occur. During a dry year, they identified two different groups of cactus finch, Geospiza conirostris: One group had shorter beaks than the other group. The differences were only slight: The two groups differed by only 15 percent. This was more than twice as much difference in beak size as there was among individuals within each group. The birds with the longer beaks extracted seeds from cactus fruits, while those with shorter beaks frequently tore open cactus pads and ate the pulp. Moreover, the two groups tended to breed separately; each group had its own type of mating song. This had the elements—genetic variation and reproductive isolation—needed to begin the formation of separate species. When the rains returned, the two groups began to blend back together.

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Computer simulation can retrace the pathway of evolution for the seed-eating finches of the Galápagos. A program designed by the evolutionary biologist Dolph Schluter begins with the ranges of beak sizes within each species, the range of seed sizes available on each island, and the presence or absence of competition and calculates the expected ranges of beak sizes on each of the islands. The result of Schluter’s analysis matches the real pattern of beak sizes very closely. Limits to adaptive radiation. When the finches first arrived on the Galápagos Islands, there were no other similar kinds of birds with which to compete. The islands represented a new world open to them for adaptive radiation. They were able to exploit new ways of making a living without having to compete with other bird species that already possessed superior adaptations. The woodpecker finch (Camarhynchus pallidus), for example, would not have been able to evolve on an island that already had woodpeckers. Some of the cactus finches eat nectar from the flowers of Waltheria ovata, and smaller finches are able to obtain and use nectar more efficiently. (Most birds that consume nectar, such as hummingbirds, are small.) On islands that do not have native bees, some of the finches specialize on nectar, although not exclusively: Nectar constitutes 20 percent of their diet, and they are smaller than the finches that do not eat nectar. On islands that already have populations of the native bee Xylocopa darwini, nectar makes up only 5 percent of the finch diet, and the finches do not differ in size from those that do not eat nectar. Hybridization is rare between species of Galápagos finches, but when it does occur, the Grants often make note of it. In more than one case, hybrids have proven fertile for more than several generations during wet seasons, but under dry seasons, when the successful individuals are the ones that specialize, the hybrids (with intermediate beak sizes) have inferior fitness. It appears that it is the dry seasons in which natural selection keeps the species apart. In the Pacific Ocean, the island of Cocos is the home of one of the same species of finches that is found in the Galápagos, the Cocos Island finch, Pinaroloxias inornata. Unlike the Galápagos Islands, the island of Cocos is not large enough to promote reproductive isolation among populations of finches. Speciation is not occurring in these finches. Rather than specializing on food resources, the Cocos finches have remained generalists, exploiting many different food resources and learning how to do so by watching other finches. See also adaptive radiation; Darwin, Charles; hybridization; natural selection; speciation.

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170 decomposers  170

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Further Reading

Further Reading

Grant, Peter R. Ecology and Evolution of Darwin’s Finches. Princeton, N. J.: Princeton University Press, 1999. Grant, Peter R., and B. Rosemary Grant. “Evolution of character displacement in Darwin’s finches.” Science 313 (2006): 224–226. Summary by Pennisi, Elizabeth. “Competition drives big beaks out of business.” Science 313 (2006): 156. Sato, A., et al. “On the origin of Darwin’s finches.” Molecular Biology and Evolution 18 (2001): 299–311. Weiner, Jonathan. The Beak of the Finch: A Story of Evolution in Our Time. New York: Knopf, 1994.

Haimi, J. “Decomposer animals and bioremediation of soils.” Environmental Pollution 107 (2000): 233–238. Harte, John, and Ann P. Kinzig. “Mutualism and competition between plants and decomposers: Implications for nutrient allocation in ecosystems.” American Naturalist 141 (1993): 829–846. Lodge, D. Jean. “Factors related to diversity of decomposer fungi in tropical forests.” Biodiversity and Conservation 6 (1997): 681–688. Setälä, H., et al. “Functional diversity of decomposer organisms in relation to primary production.” Applied Soil Ecology 9 (1998): 25–31. Shahid, Naeem, et al. “Producer-decomposer co-dependency influences biodiversity effects.” Nature 403 (2000): 762–764. Wardle, David A., et al. “Plant removals in perennial grassland: Vegetation dynamics, decomposers, soil biodiversity, and ecosystem properties.” Ecological Monographs 69 (1999): 535–568.

decomposers  Decomposers are organisms

that consume dead organisms. Because many of them release carbon dioxide into the air and nutrients into the soil, they have an essential role in the biogeochemical cycles. Most decomposers live on or in the soil. However, when an animal dies, its formerly commensalistic intestinal bacteria become decomposers. Dead animals are frequently consumed by scavengers such as vultures, and the decomposers consume the leftovers and wastes of the scavengers. Every kingdom of organisms has decomposers. Most bacteria (and perhaps some archaea) are decomposers, as are most fungi and many protists. Some plants are decomposers. The coral-root orchid (Corallorhiza) has no chlorophyll. It obtains all of its organic compounds from decomposing wood and forest litter. The most famous decomposer animal is the earthworm, which consumes soil and digests the organic matter within it. Many small arthropods that live in the soil, such as collembolans, are also decomposers. Some beetles are decomposers also. Burying beetles, such as the rare Nicrophorus americanus, bury small mammals and lay their eggs in the carcasses. Scarab beetles (family Scarabaeidae) bury feces and lay their eggs in it. Maggots of thousands of species of flies consume carrion. Decomposition occurs in stages. Decomposers and scavengers transform corpses into complex organic molecules, such as the humus that makes soil dark brown. Other decomposers transform these organic molecules into simple inorganic molecules, such as carbon dioxide, ammonia, and phosphate. Many bacteria transform one kind of inorganic molecule into another. For example, some bacteria change ammonia to nitrite, others change the nitrite to nitrate, and some release nitrogen gas into the atmosphere (denitrification). See also biogeochemical cycles; carbon cycle; nitrogen cycle.

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deep oceans, biodiversity in  The deep oceans, or open oceans, occur away from the continental shelves. Because ocean waters are constantly moving, the life of the deep oceans does not have as much of a geographical pattern as does life on the land. Deep ocean habitats can be roughly divided into pelagic and benthic zones.

Surface Pelagic Waters The pelagic zone is the water of the open oceans above the sea floor. Most of the biologically important nutrients in the oceans come from the continents. Therefore, the water of the pelagic zone of the open oceans is relatively poor in nutrients such as nitrogen and iron. Most of the photosynthetic organisms are single-celled protists and cyanobacteria. Because of the low nutrients, these organisms are not abundant in any one location, which is why the oceans are blue and not green. However, because open oceans cover about 70 percent of Earth’s surface, there is a lot of photosynthetic productivity in the pelagic zone. A complex food web depends on these protists and cyanobacteria. Billions of small arthropods, such as krill, eat the photosynthetic and herbivorous protists. Organisms such as the protists and the krill that are small enough that they float without swimming are called plankton. One of the reasons that ocean waters have low nutrient levels is that the photosynthetic plankton organisms absorb them quickly. Small fish and invertebrates such as shrimp eat the plankton, larger fish eat the smaller fish and shrimp, and top predators such as sharks and porpoises eat the larger fish.

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deep oceans, biodiversity in  171 The largest animals in the open oceans are whales, which strain plankton from the water with their baleen plates. Since water can hold more organisms than air, terrestrial ecosystems contain no analog of the large marine filter feeders. For 100 million years during the Cretaceous period, large pachyormid fishes fulfilled this role in the oceans. After their extinction, rays (family Mobulidae) and sharks (families Cetorhinidae and Rhinocodontidae) acted as large filter feeders. Predatory whales evolved early in the Paleogene period, but filter-feeding whales (Mysticeti) did not evolve until 25 million years ago. Atmospheric temperatures and sunlight cause tropical pelagic waters to be warmer than temperate and polar waters. However, the following two processes cause the open ocean to have less latitudinal difference in temperature than does the land. ●●

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Ocean currents spread warmth among the open oceans. For example, currents carry the very warm surface waters near Southeast Asia toward South America, bringing rain during El Niño periods of the El Niño Southern Oscillation (ENSO). The Gulf Stream carries warm Caribbean waters toward Europe and is largely responsible for warm European temperatures. England is much warmer than Labrador, which is at the same latitude, largely because of the Gulf Stream. Before about 3 million years ago, a large ocean current passed through what is now the Isthmus of Panama, carrying even more warm waters into the North Atlantic and much of it into an Arctic Ocean that was more open than it is today. As a result, prior to the formation of the isthmus, the Arctic Ocean was much warmer than it is today. About 30 million years ago, deciduous forests grew to the northern extremes of the continents because of the warmer climate created by this ocean current. Water retains more heat than land. This is why Antarctic waters, though very cold, are not as cold as the Antarctic continent. The Antarctic Ocean, rich in nutrients, produces enough krill and fish that penguins and other birds that live on the shores of the Antarctic continent can survive on them, and whales visit these waters.

Currents also move nutrients among the open oceans. The most productive open oceans are not always tropical but are frequently those in which currents bring nutrients up from the ocean depths. This is what happens along the west coast of South

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America during the La Niña periods of the ENSO. The Gulf Stream and other currents largely bypass the Sargasso Sea, leaving it nutrient poor. However, the Sargasso Sea is filled with Sargassum seaweeds upon which a complex food chain depends. The large organisms of the surface pelagic waters are reasonably well known. The microscopic life, like microscopic life everywhere, remains largely mysterious. The biotechnologist J. Craig Venter sailed through the Sargasso Sea and analyzed the DNA in water samples. The DNA was sufficiently diverse that it must have come from thousands of unknown microbes.

Deep Pelagic Waters In contrast to the shallow waters, the deep waters remain mysterious. Water pressure increases by about one atmosphere for each 30 feet (about 10 m) of depth. This does not present as much of a problem for the animals that live there all the time as it does for animals, such as whales and humans, who dive. Light is also unable to penetrate very far beneath the surface waters. Moreover, some of the deepest waters may contain very little dissolved oxygen. Many species of giant cephalopods (squid and octopus) live in deep pelagic waters. Some cephalopods, such as Vampyroteuthis infernalis, live in waters partway toward the bottom of the sea, while others, such as Architeuthis dux, live nearly at the bottom. Deep pelagic waters are also the home to predatory angler fishes, which use bioluminescent lures to attract prey in the dark waters. These waters remain largely unexplored except by remotely controlled probes because of the difficulty of dealing with the tremendous pressures of the deep waters.

Benthic Waters Benthic waters occur at the bottom of the sea. Most benthic habitats depend on dead organisms that fall from the surface waters. Widely scattered animals, including echinoderms and angler fishes, live there. The deepest benthic waters occur in the Marianas Trench near Southeast Asia; the maximum depth is 35,827 feet (ca. 12,000 m) at the Challenger Deep. Two types of unusual benthic habitats have been discovered that are not entirely dependent on food items settling down from above. These are the cold seeps and the hydrothermal vents. Cold seeps. Hydrogen sulfide, methane, and hydrocarbons seep out of some locations on the ocean floor. Some bacteria and archaea can metabolize these molecules. Larger animals can either eat these microbes, or the microbes may live symbiotically within their tissues. These animals include tubeworms and clams. The metabolic reactions are

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172 deep oceans, biodiversity in  172 very slow, and the animals may have very long life spans. For example, the tubeworm Lamellibrachia luymesi can probably live as long as 250 years. Locations of cold seeps include the Gulf of Mexico, Monterey Canyon off the coast of California, the Sea of Japan, the Pacific Ocean off the coast of Costa Rica, the Atlantic Ocean off Africa, the ocean floor near Alaska, and under an Antarctic ice sheet. The deepest cold seep so far discovered occurs at 24,035 feet (7,326 m) in the Sea of Japan. Hydrothermal vents. At some locations on the seafloor, volcanic activity heats seawater and fills it with hydrogen sulfide gas to make it very acidic. Superheated water (sometimes more than 800°F or [450°C] and which, because of the tremendous depths, does not boil) emerges from the seafloor. When the hot water comes into contact with the very cold water of the ocean depths, minerals precipitate out of the water. If the minerals contain a lot of sulfur, they form dark-colored cones known as “black smokers.” If the minerals contain a lot of silicon or calcium, they form “white smokers.” The hottest water is actually a supercritical fluid that is neither gas nor liquid. Hydrothermal vents resemble cold seeps, only they are hotter and metabolism occurs more rapidly. Bacteria and archaea can live in the hottest water and metabolize hydrogen sulfide to form the basis of a food chain. Most of the animals live in cooler water nearby. Small arthropods graze directly on the microbes, while larger animals have symbiotic microbes in their tissues. The most common animals are gigantic tubeworms, especially the species Tevnia jerichonana and Riftia pachyptila. Annelid worms, snails, clams, shrimp, and crabs are also common. In one location, the most common animals are eels. Hydrothermal vents are wellsprings of biodiversity. Most of the animal species are closely related to animals that live in shallower waters. Some have evolved unique adaptations. Pompeii worms (Alvinella pompejana) can withstand very hot water, and the scaly-footed gastropod Crysomallon squamiferum has scales of iron on its foot.

Deep Ocean Conservation Two of the major threats to the open oceans are pollution and overfishing. Pollution. A huge amount of garbage, much of it toxic, is dumped into the oceans. Most sewage contamination affects only the waters of the continental shelves, and most metallic garbage sinks to the bottom of the ocean. Plastic, however, floats. Pieces of plastic, some large but most of them small, accumulate in gyres of slow water surrounded by ocean currents, where they form “garbage patches.” The Pacific Trash Vortex is located between about 135°

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first entry and 155° west longitude and 35° to 42° north latitude. Its most highly concentrated portion is about the size of Texas. Fishes, sea turtles, and birds often mistake the plastic for prey items; many dead animals have been found with hundreds of pieces of plastic in their digestive systems. The plastic can also transport toxic molecules. Overfishing. Modern fish harvest technology provides the ability to scoop up hundreds of thousands of fishes at a time. Techniques include purseseine nets, drift nets, trawl bags, and very long lines with hooks on them. Aerial surveillance also allows many fishing vessels to converge upon schools of fish. Ocean invertebrate populations such as those of shrimp are also overfished. Overfishing has had two profound effects on ocean animal populations: ●●

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The populations of some fish have precipitously declined. An example is the Atlantic cod (Gadus morhua). Starting in the 1980s, catches of cod increased over previous levels by a factor of about four. In 1992, cod populations plummeted. Other fishes whose populations have plummeted are the bluefin tuna (Thunnus thynnus) and the orange roughy (Hoplostethus atlanticus). Animals other than fish can get caught in the nets. This “by-catch” can exceed the total weight of the target fish or shrimp. For each pound of shrimp that is caught on the open oceans, there are two pounds of by-catch. Thousands of dolphins and sea turtles have perished in this manner.

Overfishing has other effects as well. Millions of people in Africa depend on ocean fish for their protein. Fish populations near Africa have declined, largely due to overfishing by European vessels. The result is that many Africans compensate for this protein by eating “bushmeat,” the flesh of rain forest animals that are already endangered, including chimpanzees and gorillas. Therefore, sustainable fishing is important not only to maintain ocean fish populations but for global food security. Many consumers now insist on eating only fish that are harvested in a sustainable fashion. More information about which fishes are environmentally responsible can be found at the Monterey Bay Aquarium and Blue Ocean Institute Web sites. One alternative to open ocean fishing is aquaculture, in which fish and shrimp are raised in enclosures. These enclosures may be on land, in shallow water, or in the open ocean (where the practice is called mariculture). Aquaculture can be sustainable but usually is not. The fish may be fed meat that comes from open ocean fish; in these cases, aquacul-

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deep oceans, biodiversity in  173 ture results in even more destruction of open ocean populations. Crowded aquaculture populations produce concentrated pollution and may experience disease outbreaks. In response, aquaculture managers may use antibiotics. The pollution (including antibiotics), as well as diseased fishes, may escape into the wild. Fishes from aquaculture may not only spread diseases to wild populations but interbreed with them. Aquaculture fishes grow faster and breed when they are younger, and they may confer the genes for these life history patterns to the wild fish populations. The good news is that fish populations can often recover once the pressures on them are relieved. Some international agreements have restricted fish harvests, but these mostly affect fishing on the continental shelves, within territorial waters. Consumers are beginning to show a preference for fish that have been harvested sustainably. However, fishing on the open oceans remains largely uncontrolled. See also continental shelves, biodiversity in; coral reefs; pollution. Further Reading Blue Ocean Institute. “Guide to Ocean Friendly Seafood.” Available online. URL: http://www.blueocean.org/seafood. Accessed August 8, 2011. Cherel, Y., et al. “Stable isotopes document the trophic structure of a deep-sea cephalopod assemblage including giant octopod and giant squid.” Biology Letters 5 (2009): 364–367. Cowles, David L., and James J. Childress. “Aerobic metabolism of the anglerfish Melanocetus johnsoni, a deep-pelagic marine sit-and-wait predator.” Deep Sea Research 42 (1995): 1,631–1,638. Dekas, Anne E., et al. “Deep-sea archaea fix and share nitrogen in methane-consuming microbial consortia.” Science 326 (2009): 422–426. Summarized by Fulweiler, Robinson W., “Fantastic fixers.” Science 326 (2009): 377–378. Department of Biology, Pennsylvania State University. “Life Without Light.” Available online. URL: http://homes. bio.psu.edu/cold_seeps. Accessed July 9, 2010. deRoos, A. M., et al. “Evolutionary regime shifts in age and size at maturation of exploited fish stocks.” Proceedings of the Royal Society of London B (Biological Sciences) 273 (2006): 1,873–1,880. Doney, Scott C. “The growing human footprint on coastal and open-ocean biogeochemistry.” Science 328 (2010): 1,512–1,516. Earle, Sylvia. The World Is Blue: How Our Fate and the Oceans’ Are One. Washington, D.C.: National Geographic, 2009. Friedman, Matt, et al. “100-million-year dynasty of giant planktivorous bony fishes in the Mesozoic seas.” Science 327 (2010): 990–993.

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Halpern, Benjamin S., et al. “A global map of human impact on marine ecosystems.” Science 319 (2008): 948–952. Hilborn, R. “Salmon-farming impacts on wild salmon.” Proceedings of the National Academy of Sciences USA 103 (2006): 15,277. ———, et al. “Biocomplexity and fisheries sustainability.” Proceedings of the National Academy of Sciences USA 103 (2006): 6,564–6,568. Kaiser, Jocelyn. “The dirt on ocean garbage patches.” Science 328 (2010): 1,506. Levin, Lisa A., et al. “Environmental influences on regional deep-sea species diversity.” Annual Review of Ecology and Systematics 32 (2001): 51–93. Levinton, Jeffrey S. Marine Biology: Function, Biodiversity, Ecology. New York: Oxford University Press, 2008. Longhurst, Alan. Mismanagement of Marine Fisheries. New York: Oxford University Press, 2010. Marx, Felix G., and Mark D. Uhen. “Climate, critters, and cetaceans: Cenozoic drivers of the evolution of modern whales.” Science 327 (2010): 993–996. McLeod, Karen, and Heather Leslie, eds. Ecosystem-Based Management for the Oceans. Washington, D.C.: Island Press, 2009. Monterey Bay Aquarium. “Seafood watch.” Available online. URL: http://www.montereybayaquarium.org/ cr/seafoodwatch.aspx. Accessed August 8, 2011. Pauly, D., et al. “Towards sustainability in world fisheries.” Nature 418 (2002): 689–695. Pelagic Shark Research Foundation. “Pelagic Shark Research Foundation.” Available online. URL: http:// www.pelagic.org. Accessed May 13, 2011. Pennisi, Elizabeth. “In the deep blue sea: A survey of corals and their kin shows the ocean’s evolutionary potential.” Science 327 (2010): 519. Rios, L. M., Charles Moore, and P. R. Jones. “Persistent organic pollutants carried by synthetic polymers in the ocean environment.” Marine Pollution Bulletin 54 (2007): 1,230–1,237. Roberts, C. M., and J. P. Hawkins. “Extinction risk in the sea.” Trends in Ecology and Evolution 14 (1999): 241–246. Smith, Martin D., et al. “Sustainability and global seafood.” Science 327 (2010): 784–786. Sogin, M. L., et al. “Microbial diversity in the deep sea and the underexplored ‘rare biosphere.’ ” Proceedings of the National Academy of Sciences USA 103 (2006): 12,115–12,120. Stachowicz, John J., et al. “Understanding the effects of marine biodiversity on communities and ecosystems.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 739–766. Venter, J. Craig, et al. “Environmental genome shotgun sequencing of the Sargasso Sea.” Science 304 (2004): 66–74.

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174174 deserts, cool 

deserts, cool  Cool deserts are dry shrublands,

usually with grasses. They are found poleward from the warm deserts. They receive moderate amounts of snow in the cold winters but very little rain in the warm summers. Unlike warm deserts, which often result from subtropical dry air at just less than 30° north and south latitudes, cool deserts occur between 30° and 40° north and south latitudes. The main cause of cool desert conditions is rain shadows, in which mountains block moisture from the oceans. Some deserts are so far from oceans that rain and snow do not reach them, even though there is no pronounced rain shadow effect. In some cases, cool deserts are found near oceans with cold water from which little evaporation occurs. Examples include the following. ●●

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The Great Basin Desert of North America, which covers much of Nevada, Utah, and the northern parts of Arizona and New Mexico, is dry because the Pacific mountain ranges (Sierra Nevada, White Mountains, Cascades) block moisture from the Pacific Ocean and the Rocky Mountains block moisture from the Gulf of Mexico. The Owens Valley Desert of California is dry because it is in the immediate rain shadow of the Sierra Nevada. It is cool not merely because of its latitude but also because its average elevation is about 5,000 feet (about 1,500 m) above sea level. The Patagonian Desert in southern Argentina is dry because the Andes block moisture from the Pacific Ocean, and there is little evaporation from the cold currents of the Atlantic Ocean. The Central Asian deserts (Turkestan Desert, Taklamakan Desert, Gobi Desert) are far from any ocean and surrounded by mountains.

As in some warm deserts, the shrubs of cool deserts have deep and expansive root systems. Because of the cold winters, most cool desert shrubs are deciduous, unlike most of those in warm deserts. Their leaves are small to allow heat to be conducted into the air without much water loss. Some, such as sagebrush, produce slightly larger leaves in the spring, after snowmelt, than in the dry summer. Many cool desert shrubs are remarkably tolerant of salty soils. Because deserts have come into existence somewhat recently in Earth history, the cool deserts of the world are largely isolated from one another and have different dominant shrubs (see table). Cool deserts intergrade into shortgrass prairies (North America) steppes (Central Asia), and warm deserts.

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first entry

Examples of Cool Desert Shrubs Great Basin

Sagebrush (Artemisia tridentata)

Owens Valley

Greasewood (Sarcobatus vermiculatus) Shadscale (Atriplex confertifolia)

Patagonia

Acantholippia deserticola Benthamiella patagonica

Central Asian deserts

Camel’s thorn (Alhagi maurorum) Saxaul (Haloxylon ammodendron)

Because cool deserts also have grasses, they can support some of the same large animals as the adjacent shortgrass prairies. In North America, pronghorns (Antilocapra americana) move between shortgrass prairie and sagebrush desert. Gazelles (Procapra gutturosa) and wild donkeys known as onagers (Equus hemionus) of the Mongolian steppe also live at the edges of the Gobi Desert. In South America, camel-like guanacos (Lama guanicoe) and large flightless birds called rheas (Rhea americana) live both in grasslands and in parts of the Patagonian Desert. Central Asian cool deserts are home to the Bactrian camel (Camelus bactrianus), the twohumped relative of the single-humped dromedary camel that lives in the warm Middle East and Sahara. Both species of camel can tolerate thirst for long periods and drink tremendous amounts of water at oases. The presence of grasses in the sagebrush desert is the reason it is often called sagebrush steppe. Wildfires maintain grasslands by destroying woody plants. In the tallgrass prairies, the woody plants are the trees of the temperate deciduous forest. In the shortgrass prairies, it is often the cool desert shrubs that are burned. Both overgrazing and fire suppression can cause grasses to become rare and cool desert shrubs to dominate, and both of these processes are symptomatic of human activity in cool desert regions. Severe overgrazing can destroy the shrubs as well. Cool deserts withstand fires better than do dry coniferous forests, however, and fire suppression has encouraged the spread of junipers into the Great Basin sagebrush desert. See also communities, ecological; deserts, warm; disturbances, ecological; grasslands and savannas; temperate deciduous forests. Further Reading Anderson, Jay E., and Karl E. Holte. “Vegetation development over 25 years without grazing on sagebrushdominated rangelands in southeastern Idaho.” Journal of Range Management 34 (1981): 25–29.

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deserts, warm  175 Biondini, Mario E., et al. “Secondary successional patterns in a sagebrush (Artemisia tridentata) community as they relate to soil disturbance and soil biological activity.” Plant Ecology 60 (1985): 25–36. Miller, Richard F., and Jeffrey A. Rose. “Fire history and western juniper encroachment into sagebrush steppe.” Journal of Range Management 52 (1999): 550–559. Raedeke, Kenneth J., and Javier A. Simonetti. “Food habits of Lama guanicoe in the Atacama Desert of northern Chile.” Journal of Mammalogy 69 (1988): 198–201. Romo, J. T., and M. R. Haferkamp. “Water relations of Artemisia tridentata ssp. wyomingensis and Sarcobatus vermiculatus in the steppe of southeastern Oregon.” American Midland Naturalist 121 (1989): 155–164. Saltz, David, and Daniel I. Rubenstein. “Population dynamics of a reintroduced Asiatic wild ass (Equus hemionus) herd.” Ecological Applications 5 (1995): 327–335.

deserts, polar  Polar deserts are regions with either bare rock or thick layers of ice, found in the coldest land surfaces on Earth. They are called polar deserts because little snow falls, and the bare rocks and small pockets of soil retain little water. They are colder and drier than arctic tundra. Examples include the McMurdo dry valleys of Antarctica, which have been ice-free for thousands of years; the coast of Antarctica; the northern edges of Eurasia and North America; and Arctic islands such as Greenland, Ellesmere Island, Franz Josef Land, and Svalbard, all of which have land surface within 10° of latitude of the North Pole. Some tundra plants can tolerate dry conditions and live in polar desert regions adjacent to the tundra. Examples are Saxifraga oppositifolia and the dwarf azaelea Loiseleuria procumbens around the Arctic Ocean. The only native flowering plants of Antarctica are the pearlwort Colobanthus quitensis and the hairgrass Deschampsia antarctica, which live in sheltered rock recesses near the ocean. As global warming continues, some of the tundra plants that now live in polar deserts may be able to expand their ranges and form tundra vegetation. This will not happen rapidly enough to compensate for the loss of the species-rich arctic tundra, which may be rapidly replaced by boreal forests. See also boreal and subalpine forests; greenhouse effect and biodiversity; tundra. Further Reading Bay, Christian. “Floristical and ecological characterization of the polar desert zone of Greenland.” Journal of Vegetation Science 8 (1997): 685–696.

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Gold, Warren G., and Lawrence C. Bliss. “Water limitations and plant community development in a polar desert.” Ecology 76 (1995): 1,558–1,568.

deserts, warm  Deserts are regions with little

rainfall. Some deserts have had very little rainfall throughout recorded history. For example, most of the Atacama Desert of Peru has had no noticeable amount of rainfall since observations began in 1571. Furthermore, deserts receive only a little snow, and most of their rainfall comes in powerful storms. All desert plants are therefore adapted to long periods of dryness. Warm deserts also have mild winters and hot summers. Cool deserts (treated in a separate entry) may have cold winters. Warm deserts are found in southwestern North America, on the west coast of South America, in North Africa and the Middle East, near the west coast of southern Africa, and in Australia. The three major regions of warm desert in North America are as follows. ●●

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In the Mojave Desert of California, creosote and bursage bushes are regularly spaced, almost like a plantation or a decorated carpet, because the area between them is filled with roots that soak up the little rain that falls. The only major species of succulent plant in the Mojave Desert is the tree-sized yucca known as Joshua tree. In the Colorado (or Sonoran) Desert of Arizona and northern Mexico, many species of cactus predominate as well as acacia trees, under which the cactus seedlings germinate. In the Chihuahuan Desert of New Mexico, Texas, and northern Mexico, creosote and mesquite bushes dominate. Because of its proximity to the Gulf of Mexico, the Chihuahuan Desert receives more rain than the other deserts, allowing grasses to grow between the bushes.

The major South American deserts are in Peru, especially the Atacama Desert. The major African deserts are the Sahara, which covers most of North Africa, and the Kalahari Desert, near the western coast of southern Africa, particularly in Namibia and Botswana. Desert covers much of the Middle East, including the entire Arabian Peninsula, and some other Eurasian areas, such as the Thar Desert of India and Pakistan. The Great Outback of Australia is a desert.

Causes of Desert Conditions Warm deserts have mild winters, with some rainfall, and hot summers, with occasional thunderstorms.

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176 deserts, warm  176 The following are three main reasons that warm deserts are dry. ●●

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Hadley cells. Hadley cells are pockets or bands of air circulation, named after the British meteorologist who discovered them. The warmest places on Earth are along the equator, where moist air rises above tropical rain forests. Much of the moisture condenses above the equator and produces abundant tropical rainfall. The air circulates poleward, then descends to the surface of Earth again at about 30° N and 30° S latitude. The air becomes even drier as it descends and becomes warmer. The return of the air toward the equator, producing trade winds, completes the cycle of each Hadley cell. The result is a band of warm deserts in the subtropical zone, roughly 30° N and 30° S. The northern continents have the greatest land mass and the largest warm deserts, all of them between roughly the 20th and 30th parallels of north latitude. The deserts of the southern hemisphere are also between roughly the 20th and 30th parallels of south latitude. Rain shadows. Mountains force moist oceanic winds upward, where they become cooler and their moisture condenses as rain or snow on the windward side. The wind, now much drier, descends the leeward side of the mountains and becomes warmer and drier. Nearly every warm desert is slightly drier than the Hadley cells would make it. The southwestern desert in North America is surrounded by low mountains, not enough themselves to cause desert conditions. The Atacama Desert is between the Andes and the Chilean Coast Range, which block moisture from both east and west. Ocean currents. Coastal regions near cold ocean currents often have little rainfall. This is yet another reason that the Atacama Desert receives almost no rainfall.

The extreme conditions of Death Valley in California are due not only to Hadley cells and rain shadows but to its low elevation, which allows hot air to accumulate. Its lowest point, Badwater, is 282 feet (86 m) below sea level. Plants that live near the bottom, such as the shrub Tidestromia oblongifolia, have photosynthetic reactions that function best at high temperatures (see figure). As the name would suggest, saline water has accumulated at the bottom of Death Valley, where Salicornia pickleweeds are almost the only plants. Death Valley was a lake

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first entry when glaciers were melting at the end of the most recent ice age. Warm deserts have the highest average temperatures on Earth. The highest temperature ever recorded was 136°F (58°C) in the Sahara of Libya in 1922. However, temperatures can drop rapidly at night. In the Sahara, a high temperature of 126°F (52°C) was followed by a nighttime low temperature of 26°F (-5°C). Both of these temperature records were made possible by the dry conditions. Water gains and releases heat more slowly than dry soil, causing humid environments to have cooler days and warmer nights.

Desert Plant Adaptations to Drought Plants are small and few in deserts compared to other ecological communities, though more abundant than casual observers often recognize. Plants have numerous adaptations to make efficient use of the scarce moisture that warm deserts receive. Their

A severe rain shadow keeps most of the rain and snow out of Death Valley, California. Conditions at the bottom of Death Valley (282 feet [86 m], below sea level) are very hot, dry, and salty. Few plants can survive there, but Tidestromia oblongifolia thrives under conditions that would kill most complex plants.  (Stanley A. Rice)

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deserts, warm  177 adaptations are either avoidance (maintaining moist conditions inside their tissues) or tolerance (growing despite dry internal conditions), and include the following. Reduced leaf area. Desert shrubs generally have small leaves. Succulents may have no leaves at all (as in desert cacti) or leaves only during the rainy season (as in desert spurges). Small leaves allow more of the heat load to diffuse into the air, thereby requiring less transpiration of water vapor to cool them. Succulent stems store the heat in the water inside their tissues. Storage. Many warm desert plants are succulents and store water in their tissues, which are usually protected by spines and thorns from thirsty animals. Examples include the cacti of the North and South American deserts and the spurges of the African deserts (see table on page 178 and 179). They often have wide, shallow root systems that quickly absorb rain. Their succulence also allows them to absorb carbon dioxide from the air during the cool nights and store it in the form of acid; they can then produce food by photosynthesis during the hot daytime without opening their pores. Deep roots. Many warm desert shrubs have deep roots that reach the water table. While these roots may have essentially unlimited water, they cannot provide much of it to the aboveground part of the shrub, because such roots, expensive to grow, are not numerous, and they must transport the water a long distance upward. Some mesquites have been found to have roots that are more than 100 feet (30 m) deep. Many shrubs, despite limited access to groundwater, produce leaves and bloom in the spring. The ocotillo bush produces leaves and bright red flowers in the spring, while it looks like dead sticks the rest of the year. Some shrubs grow more quickly than others. Near the bottom of Death Valley, the shrubs exploit soil water sources that do not last for many years. Tidestromia oblongifolia shrubs live only a few years; they produce seeds and die when the water runs out. In contrast, Atriplex hymenelytra shrubs grow slowly when water is available and stop growing when it is not. Ephemeral plants. Many desert wildflowers germinate during the winter rainy season, then bloom in the spring when the rains have ended. The warm desert spring may produce a carpet of wildflowers, such as Mexican poppies in the American southwest. The entire plant of Mimulus bigelovii may be only about two inches (a few cm) in height, almost a third of which consists of flowers (see figure). Another example is the paper daisy (Leucochrysum fitzgibbonii) of Australia. By summer, the wildflowers have produced seeds and begun to die. Ephemeral plants grow very quickly during the brief wet season. Some desert

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This ephemeral wildflower (the monkeyflower Mimulus bigelovii) grows only a few centimeters tall and completes its entire life cycle within the few weeks of wet weather in the desert spring.  (Stanley A. Rice)

plants, such as the desert nardoo fern of Australia (Marsilea drummondii), grow only when temporary ponds are wet; only its spores survive the dry season. Condensation of fog. Some coastal deserts, such as in South America and Africa, receive little, if any, rainfall but frequently receive fog and mist from the oceans. The fog droplets collect on the stems and leaves of the plants already present and drip into the soil. Some desert plants grow well in moist microhabitats, such as the following. ●●

●●

Some warm desert plants may create moist microhabitats for other plants. Phacelia campanularia is a southwest American desert wildflower that often grows beneath the creosote shrubs of the Mojave Desert. Many cactus seedlings will not survive past germination unless they are in the moist shade cast by shrubs such as acacias. The cactus seedlings eventually grow up through the “nurse shrub” (see figure on page 180). Dry creek beds (called arroyos in southwestern North America and wadi in the Middle East) are also a relatively moist microhabitat. After the rainy season, arroyos are the

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178 deserts, warm  178

first entry

Examples of Plants in Different Deserts Common Name

Scientific Name

Plant Family

NORTH AMERICA Colorado Desert Succulents Beavertail cactus

Opuntia basilaris

Cactaceae (cactus)

Organ pipe cactus

Stenocereus thurberi

Cactaceae (cactus)

Saguaro cactus

Carnegiea gigantea

Cactaceae (cactus)

Brittlebush

Encelia farinosa

Asteraceae (composite)

Catclaw

Acacia greggii

Fabaceae (legume)

Ocotillo

Fouquieria splendens

Fouquieriaceae

Chuparosa

Beloperone californica

Acanthaceae (acanthus)

Elephant tree

Bursera microphylla

Burseraceae (torchwood)

Jojoba

Simmondsia chinensis

Rutaceae (citrus)

Mexican poppy

Eschscholzia mexicana

Papaveraceae (poppy)

Purplemat

Nama demissum

Hydrophyllaceae (waterleaf)

Scarlet globemallow

Sphaeralcea ambigua

Malvaceae (mallow)

Upland shrubs

Arroyo shrubs

Ephemerals

Mojave Desert Succulents Joshua tree

Yucca brevifolia

Agavaceae (agave)

Bursage

Ambrosia dumosa

Asteraceae (composite)

Creosote bush

Larrea tridentata

Zygophyllaceae

Desert senna

Senna covesii

Fabaceae (legume)

Phacelia campanularia

Hydrophyllaceae (waterleaf)

Shrubs

Ephemerals Desert phacelia

Chihuahuan Desert Succulents Silver cholla cactus

Cylindropuntia echinocarpa

Cactaceae (cactus)

Prosopis glandulosa

Fabaceae (legume)

Shrubs Mesquite

SOUTH AMERICA Peruvian Desert Succulents Cardon grande

Echinopsis atacamensis

Cactaceae (cactus)

Cinerea cactus

Copiapoa cinerea

Cactaceae (cactus)

Lechero

Euphorbia lactiflua

Euphorbiaceae (spurge)

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deserts, warm  179 Peruvian Desert (continued) Shrubs Coronilla de fraile

Encelia canescens

Asteraceae (composite)

Mesquite

Prosopis pallida

Fabaceae (legume)

Cryptantha parviflora

Boraginaceae (borage)

Ephemerals Cryptantha

AFRICA Sahara Shrubs Acacia

Acacia seyal

Fabaceae (legume)

Desert date

Balanites aegyptiaca

Zygophyllaceae

Tamarisk

Tamarix gallica

Tamaricaceae (tamarisk)

Kalahari Desert Succulents African milk tree

Euphorbia trigona

Euphorbiaceae (spurge)

Carrion flower

Stapelia gigantea

Asclepiadaceae (milkweed)

Hoodia

Hoodia gordonii

Apocynaceae (milkweed)

Pachypodium

Pachypodium succulentum

Apocynaceae (milkweed)

Welwitschia

Welwitschia mirabilis

gymnosperm

Acacia mellifera

Fabaceae (legume)

Shrubs Black thorn

●●

last places to dry. They fill rapidly with water during brief summer thunderstorms. Some desert shrubs have shallower roots than many but survive in arroyos. These shrubs are often members of predominantly tropical plant families and have survived in desert arroyos from the time, several million years ago, when tropical seasonal forests covered what is now the Colorado Desert. Examples include members of the acanthus, citrus, and torchwood families in the arroyos of the Colorado Desert (see table). Springs produce desert pools and oases. In the Anza-Borrego Desert of California, part of the Colorado Desert, a grove of fan palms (Washingtonia filifera) grows around a spring. Sahara oases have trees such as tamarisks (genus Tamarix) and the date palm (Phoenix dactylifera). It is difficult to know which tree and shrub species are native to Sahara oases, since they have been the centers of human habitation for thousands of years. Most oasis date palms are cultivated, as are figs, olives, and apricots.

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●●

In the Middle East, the leaves of the desert rhubarb (Rheum palaestinum) are about three feet (1 m) wide, which contrasts sharply with the small leaves of most desert plants. The leaves collect water from rains and funnel it to the roots. In this way, the water is concentrated in the plants’ root zones. The leaves transpire almost 16 times as much water vapor as evaporates from bare soil.

Warm deserts also have poor soil. Fertile soil contains a lot of humus from the decomposition of leaf and stem litter. Deserts produce far less litter than do other ecological communities, and decomposers require moisture.

Desert Plant Biogeography Major desert areas are separated from each other by wetter environments. Furthermore, modern deserts have come into existence only in the past few million years. Therefore, major desert areas have very different sets of dominant plant species. Cacti (family Cactaceae) are the major succulents of North and South

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180 deserts, warm  180

first entry sand dunes. An example is the Australian sandhill cane Zygochloa paradoxa, which stores water in its underground stems. Perhaps the strangest desert plant is Welwitschia mirabilis, which grows in the southern African desert. It is the only species within its gymnosperm evolutionary lineage. It is the only gymnosperm that has (independently) evolved the kind of photosynthesis that is common in flowering plant succulents. The stem remains underground. Long leaves keep growing as their tips are destroyed by desert conditions. During occasional periods of moisture, reproductive structures emerge from between the two leaves. Warm deserts intergrade into adjacent ecological communities. The Chihuahuan Desert contains grasses; no clear line separates it from arid grasslands. The Mojave Desert intergrades with cool deserts to the north. The deserts of southwest Africa intergrade into the shrublands of South Africa.

Desert Animal Adaptations Desert animals have adaptations that allow them to avoid or tolerate heat and drought. Avoidance. All desert animals avoid drought to the extent that is possible. Some desert animals are active only during moist seasons or in areas of permanent moisture. Examples include the following. Seedlings of many cactus species, such as the cholla, organ pipe (Stenocereus thurberi), and saguaro (Carnegeia gigantea), grow in the shade of shrubs such as acacias and continue to grow after the acacias have died.  (Organ Pipe Cactus National Monument; Stanley A. Rice)

American deserts, while spurges and milkweeds dominate the succulent flora of Africa (see table on pages 178 and 179). These plants look enough like cacti that many horticulturalists call them cacti. Some desert shrubs are found nearly worldwide, for example, the acacia and mesquite genera. The fluctuation between wet and dry conditions is ecologically similar to a disturbance, in which a flush of resources follows a long period without them. This explains the overlap between weed and desert plant families. Caltrop (Tribulus terrestris and T. cistoides, also known as puncture vine and devil’s thorn) is a desert plant from South Africa. In other parts of the world, such as the warmer regions of North America, it is a weed. It was naturalized in recent centuries on the Galápagos Islands. It is in the family Zygophyllaceae, which is also known as desert shrubs in North America, Africa, and the Middle East. The composite family (Asteraceae) is also famous for its weeds. Many grasses are also weeds, but a few grasses live in (and stabilize) desert

xviii+598_Biodiversity_F.indd 180

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●●

●●

The Death Valley desert pupfish (Cyprinodon salinus) lives in the saline conditions at the bottom of Death Valley. A spring maintains the moisture all year. Because desert springs are isolated, different species of pupfish have evolved in desert pools in other areas of the American Southwest. It avoids drought but must physiologically tolerate hot water and salt. The Australian shield shrimp Triops australiensis lives and breeds in desert saline pools. Adult desert frogs emerge from underground during the wet season, mate, and lay eggs. The tadpoles mature, and the adult frogs dig tunnels in the moist soil. Once underground, the Australian water-holding frog (Cyclorana platycephalus) sheds a layer of skin that forms a membrane that traps much of the moisture as the soil dries out. It can remain underground for several years if rains fail to come. It thus avoids drought by becoming dormant during the dry season.

Tolerance. Other desert animals tolerate drought. Their major way of doing this is to be active primarily at night. Most of them also remain in wet microhabitats whenever possible. This is where most

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deserts, warm  181 prey (such as lizards and rodents) and most predators (such as snakes and roadrunners) live. Many desert insects, such as ants and termites, live underground. Scorpions, abundant in deserts worldwide, hunt at night. Other examples include the following.

Among the most amazing desert animal adaptations are those of dromedary camels (Camelus dromedarius) of the Sahara and Middle East deserts. They include the following: ●●

●●

●●

●●

The Australian whistling spider (Selenocosmia stirlingi) spends the day at the end of a three-foot-long (1 m-long) burrow and at night waits behind the silk door of the burrow to ambush arthropods that come near. Australian sand grasshoppers (Urnisa guttulosa) bury themselves in sand, with only their eyes and antennae exposed, during the day and emerge to eat plant tissues at night (only during the wet season). Pit viper snakes (Crotalinae) have special sensory organs that detect infrared light, which all warm objects emit. This allows them to “see the heat” of mammalian prey species.

Some desert mammals have adaptations that allow them to dissipate body heat without the loss of water. The ears of American jackrabbits (such as Lepus californicus) have large exposed areas that allow body heat to radiate into the air. All desert animals have ways to avoid water loss. Snakes and lizards are abundant and diverse in the deserts of the world. They all have scales that prevent evaporation, and they excrete a slurry of uric acid rather than watery urine. Many desert animals also have ingenious ways of obtaining water, as in the following examples. ●●

●●

●●

Some desert animals get all their water from their food. The Ayrean grasswren (Amytornis goyderi), a desert bird of Australia, gets all its water from the seeds and arthropods that it eats; it also excretes less water than most other birds. In many cases, desert animals that eat seeds gather them just before dawn, when there is the greatest chance that moisture will have condensed on them from the air. Kangaroo rats (genus Dipodomys) of the American Southwest and the Australian spinifex hopping-mouse (Notomys alexis) not only get all their water from the food that they eat, but rely heavily on metabolic water. This is water that the mitochondria in their cells produce in the process of releasing energy from the metabolism of sugar. Some beetles that live in the deserts of southern Africa stand on sand dunes when fog moves in from the ocean. They drink the water that condenses on their bodies.

xviii+598_Biodiversity_F.indd 181

●●

●●

●● ●●

●●

Dromedary camels store most of their body fat in a single hump rather than distributed throughout the body under the skin. This reduces the insulation of the skin and helps body heat dissipate into the air. Camel humps do not store water. Like other desert mammals, camels make use of metabolic water, of which the metabolism of their fat produces a great deal. Camel blood cells are oval-shaped, which helps to prevent them from sticking together when the blood thickens due to dehydration. Their bodies can withstand up to 25 percent fluid loss from sweating, in contrast to most mammals, in which heart failure begins at 15 percent fluid loss. The cells are remarkably resilient to changes in blood salinity, which occurs when camels drink a large amount of water (up to 40 gallons [150 L] at a time) after a long thirst. Camels can tolerate a body temperature up to 106°F (41°C). Camels have thick coats of hair. This interferes with the loss of body heat but also shields camels’ bodies from the intense heat of the desert. Their long legs keep their bodies far from the hot desert soil. Camels lose very little water through urine (which can be as thick as syrup) or feces.

Deserts have low biodiversity compared to most other ecological communities, but plants and animals have evolved numerous adaptations independently in deserts around the world to avoid or tolerate dry conditions. Few deserts are threatened with human development, which requires water. Solar power plants have been constructed in some desert areas, particularly the Mojave Desert in California, and many more are planned. There are few endemic species in the Mojave Desert, and it would require the development of many solar power plants before this desert were harmed. Desert oases may have endemic species and require habitat protection. Some deserts, such as the Sonoran Desert, are particularly rich in species and require particular attention, especially since much of the Sonoran Desert is near Tucson and Phoenix. Conservation is particularly important for bats and other pollinators of the Sonoran Desert cacti. Although most pharmaceuticals come from rain forest plants, a few come from desert plants. An extract of the African succulent

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182 deuterostomes  182 Hoodia gordonii has been used for centuries by local tribes to reduce the symptoms of hunger and is now marketed as a natural supplement for weight loss. Increasing drought in connection with global warming may cause some desert areas, whose plants and animals are already on the brink of survival, to lose many of their species. See also biogeography; communities, ecological; convergence; deserts, cool; disturbances, ecological; grasslands and savannas; shrublands. Further Reading Atchley, Michael C., et al. “Arroyo water storage and soil nutrients and their effects on gas-exchange of shrub species in the northern Chihuahuan Desert.” Journal of Arid Environments 43 (1999): 21–33. Brown, James H., and C. Robert Feldmeth. “Evolution in constant and fluctuating environments: Thermal tolerances of desert pupfish (Cyprinodon).” Evolution 25 (1971): 390–398. Gulmon, Sally L., and Harold A. Mooney. “Spatial and temporal relationships between two desert shrubs, Atriplex hymenelytra and Tidestromia oblongifolia in Death Valley, California.” Journal of Ecology 65 (1977): 831–838. Holzapfel, Claus, and Bruce E. Mahall. “Bidirectional facilitation and interference between shrubs and annuals in the Mojave Desert.” Ecology 80 (1999): 1,747–1,761. Kaufman, Donald W., and Glennis A. Kaufman. “Effect of moonlight on activity and microhabitat use by Ord’s kangaroo rat (Dipodomys ordii).” Journal of Mammalogy 63 (1982): 309–312. Mahall, Bruce E., and Ragan M. Callaway. “Root communication mechanisms and intracommunity distributions of two Mojave Desert shrubs.” Ecology 73 (1992): 2,145–2,151. McAuliffe, Joseph R. “Sahuaro-nurse tree associations in the Sonoran Desert: Competitive effects of sahuaros.” Oecologia 64 (1984): 319–321. Nagy, K. A. “Seasonal water, energy and food use by freeliving, arid-habitat mammals.” Australian Journal of Zoology 42 (1994): 55–63. Pockman, William T., and John S. Sperry. “Vulnerability to xylem cavitation and the distribution of Sonoran Desert vegetation.” American Journal of Botany 87 (2000): 1,287–1,299. Polis, Gary A., and Sharon J. McCormick. “Intraguild predation and competition among desert scorpions.” Ecology 68 (1987): 332–343. Reichman, O. J., and David Oberstein. “Selection of seed distribution types by Dipodomys merriami and Perognathus amplus.” Ecology 58 (1977): 636–643. Rundel, Philip W., James Ehleringer, Harold A. Mooney, and Sally L. Gulmon. “Patterns of drought response in

xviii+598_Biodiversity_F.indd 182

first entry leaf-succulent shrubs of the coastal Atacama Desert in northern Chile.” Oecologia 46 (1980): 196–200. Tucker, Compton J., and Sharon E. Nicholson. “Variations in the size of the Sahara Desert from 1980 to 1997.” Ambio 28 (1999): 587–591. Vasek, Frank C. “Creosote bush: Long-lived clones in the Mojave Desert.” American Journal of Botany 67 (1980): 246–255. Ward, David. The Biology of Deserts. Oxford: Oxford University Press, 2009. Winter, Klaus, and Michael J. Schramm. “Analysis of stomatal and nonstomatal components in the environmental control of CO2 exchange in leaves of Welwitschia mirabilis.” Plant Physiology 82 (1986): 173–178.

deuterostomes  See animals. Devonian period, biodiversity in  The

Devonian period (410 to 360 million years ago) was the fourth period of the Paleozoic era. The first significant advances of life onto land had occurred during the preceding Silurian period. During the Devonian period, plants filled the wet areas of Earth, making large areas of Earth’s surface green for the first time. Climate. The climate in the equatorial regions was warm and wet. Portions of the southern continent, over the South Pole, were cold. Atmospheric oxygen levels were lower and carbon dioxide levels higher than at present (see table on page 183). Continents. During the Devonian, there were three major continental areas. What is now North America and Europe formed a single landmass near the equator, much of it covered by shallow oceans. A portion of what is now Siberia lay to the north. Gondwanaland, a continent composed of what is now South America, Africa, Antarctica, India, and Australia, formed a large mass in the Southern Hemisphere. Marine life. Marine life, especially fishes, diversified during the Devonian (see figure on page 184). ●●

●●

Invertebrates. The invertebrate groups that dominated the Silurian period continued to proliferate during the Devonian. Brachiopods continued to be more common than superficially similar bivalves. Among the cephalopod mollusks, a new group appeared—the ammonites, with coiled shells. Trilobites were much less diverse than in previous periods but remained common. Vertebrates. Many kinds of fishes evolved during the Devonian period. So great was their diversity that the Devonian period has

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Devonian period, biodiversity in  183 been called the age of fishes, even though there were also many species of plants and animals on land. Armored jawless fishes evolved into some large forms such as the five-foot (1.5-m) Psammolepis, then declined toward extinction, mainly due to competition with fishes that had jaws and that could therefore forage more efficiently. One lineage of jawless fishes without armor survived as the ancestors of modern lampreys and hagfishes. The jawed fishes included the heavily armored placoderms (“plateskins”), a group now extinct. Some, such as Dunkleosteus, were 33 feet (10 m) in length. The placoderms were the dominant group of fishes in the sea at this time. Although fossilized shark scales have been found in Silurian deposits, the first full shark fossils date from the Devonian period, at which time shark species proliferated. The most abundant group of fishes today, the rayfinned fishes, began to proliferate during the Devonian period.

Multicellular Biodiversity   in the Devonian Period Conditions Atmospheric oxygen

75 percent of modern level

Atmospheric carbon dioxide

6.3 times modern level

Global temperature

11°F (6°C) higher than today

Sea level

260 feet (80 m) higher than today

Approximate number of families* Continental

70

Marine

450

Total

520

Examples of marine animals Angustidontis sp.

crustacean arthropod

Cladoselache sp.

shark

Dipleura dekayi

trilobite

Dunkleosteus sp.

armored jawed fish

Hydroblastus hendyi

echinoderm

Lepidocoleus hohensteini

annelid

Cheirolepis sp.

ray-finned fish

Orthonychia protei

gastropod mollusk

Psammolepis sp.

armored jawless fish

Sporadoceras orbiculare

ammonite mollusk

Continental life. At the beginning of the Devonian period, there were only small plants (about 3 feet [1 m] in height) and a few arthropods in terrestrial wetlands. By the end of the Devonian period, the first trees and terrestrial vertebrates had evolved. ●●

Examples of continental animals Acanthostega gunneri

fishlike amphibian

Attercopus fimbriungus

spider relative

Dipnorhynchus sp.

lungfish

Eusthenopteron foordi

amphibianlike fish

Ichthyostega stensoi

fishlike amphibian

Orsadesmus rubecollus

millipede

Tiktaalik roseae

fishlike amphibian

Examples of land plants Archaeopteris obtusa

seed-bearing tree

Gillespiea randolphensis

fernlike plant

Protolepidodendron sp.

tree clubmoss

Psilophyton sp.

trimerophyte plant

Rhacophyton sp.

fern

Zosterophyllum rhenanum

zosterophyllophyte plant

*Based on Benton

xviii+598_Biodiversity_F.indd 183

●●

Plants. Early Devonian Rhynia was not much bigger than the late Silurian Cooksonia. These plants had xylem cells, which carry water from the ground up to the tips of the stems. Xylem allowed the evolutionary descendants of these plants to grow to the size of trees. By the end of the Devonian, some trees were about 30 feet (10 m) tall. Their descendants became much larger trees during the subsequent Carboniferous period. Silurian plants evolved into Devonian clubmosses, horsetails, and ferns, which reproduced by spores rather than by seeds. Silurian plants had only simple branching stems, but during the Devonian, the first leaves evolved. Some of the branches were united by layers of green tissue, which became the veins and blades of the leaves. Before the end of the Devonian, progymnosperms such as Archaeopteris had primitive forms of seeds. Vertebrates. The lobe-finned fishes, which had fingerlike bony reinforcements in their fins, evolved in continental freshwater during the Devonian period. One group of lobe-finned fishes was the lungfishes. A few

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184 dicots 184

first entry

Boyce, c. Kevin, et al. “chemical evidence for cell wall lignification and the evolution of tracheids in early Devonian plants.” International Journal of Plant Sciences 164 (2003): 691–703. clack, Jennifer a. “Devonian climate change, breathing, and the origin of the tetrapod stem group.” Integrative and Comparative Biology 47 (2007): 510–523. Murphy, Dennis c. “Devonian times.” available online. URl: http:// www.devoniantimes.org/index.html. Placoderms were large armored fishes that lived in the oceans during the accessed September 17, 2009. Devonian period. Rode, alycia l., and Bruse S. lieberman. “integrating evolution and biogeography: a case involving Devonian crustaceans.” lungfishes still live in tropical rivers today. Journal of Paleontology 79 (2005): 267. their lungs allow them to survive long periRolfe, W. D. ian, and Jerzy Dzik. “Angustidontus, a late ods in mud when ponds become seasonally Devonian pelagic predatory crustacean.” Transactions dry. From one of the lineages of lobe-fi nned of the Royal Society of Edinburgh (Earth Sciences) 97 fishes, the fi rst tetrapod amphibians evolved (2006): 75–96. during the Devonian. the crucial fi rst steps, Roth-nebelsick, anita, and Wilfried Konrad. “assimilafrom lobe-fi nned fishes to amphibianlike tion and transpiration capabilities of rhyniophytic fishes (such as Eusthenopteron) to fishplants from the lower Devonian and their implicalike amphibians (such as Ichthyostega) to tions for paleoatmospheric cO2 concentration.” Palamphibians occurred during this geological aeogeography, Palaeoclimatology, and Palaeoecology period. the recently discovered Tiktaalik 202 (2003): 123–176. roseae was almost exactly in the middle of

the fish-to-amphibian transition. living among the small plants in the early Devonian mud were the fi rst land animals, relatives of modern arthropods such as scorpions, mites, and spiders. Shortly thereafter, the ancestors of insects, centipedes, and millipedes were living among the small plants of early Devonian wetlands. Extinctions. One of the mass extinction events in earth history occurred at the end of the Devonian, at which time an estimated 22 percent of families, representing 83 percent of species, became extinct. the causes of this extinction event are unclear. See also amphibians; fishes; mass extinctions.

dicots  Dicots are the most abundant flowering plants. there are at least 170,000 species of dicots, ranging from tiny herbaceous plants to trees. along with the conifers, the flowering plants have transformed the landscape of earth into a living surface of green. in addition, flowering plants have undergone coevolution with animals that pollinate their flowers and disperse their seeds. as a result, the flowering plants, especially the dicots, have filled the world with an astounding diversity of form, color, and scent. Flowering plants have flowers and fruits. Flowers may contain:

Further reading algeo, t. J., et al. “effects of the Middle to late Devonian spread of vascular land plants on weathering regimes, marine biota, and global climate.” in Plants Invade the Land: Evolutionary and Environmental Approaches, edited by Patricia G. Gensel and D. edwards, 213– 236. new york: columbia University Press, 2001. Benton, Michael. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Bond, David, et al. “extent and duration of marine anoxia during the Frasnian-Famennian (late Devonian) mass extinction in Poland, Germany, austria, and France.” Geological Magazine 141 (2004): 173–193.

xviii+598_Biodiversity_F.indd 184

● ● ● ●

Sepals: leafl ike protective structures Petals: often colorful structures that attract pollinators Stamens: male structures that produce pollen Pistils: female structures that produce seeds

the term dicot refers to the embryo of the plant. When it emerges from the seed, the embryo has two cotyledons, or embryonic leaves. Most dicots also have veins that form cores in the middle of the roots, rings in the young stems, and networks in the

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dicots  185 leaves, in contrast to the arrangement of veins in the monocots, the embryos of which have only one cotyledon. Taxonomists (scientists who study evolutionary relationships among organisms) have traditionally divided the flowering plants into two groups: the monocots and the dicots. Recent evolutionary research, however, has shown that the dicots actually represent several distinct lineages. This makes them a paraphyletic cladistic group. All of these dicot lineages except one are considered to be “primitive dicots” and are discussed in the entry on flowering plants. The remaining dicot lineage, which contains the vast majority of dicots, is called the eudicots, and is the subject of the remainder of this entry.

Primitive and Core Eudicots There are several relatively primitive lineages within the eudicots. Here are three of the important families of primitive eudicots that are important in North America and characteristics by which to recognize them. The poppies (Papaveraceae) are herbaceous plants with milky sap. This sap helps protect them from animals and often contains potent chemicals such as morphine. Poppy flowers have numerous stamens (the male parts), all separate from one another. The buttercups (Ranunculaceae) are also herbaceous plants whose flowers have numerous separate stamens. Relatives of buttercups include larkspurs and columbines, the petals of which have long spurs. Only specialized pollinators can obtain nectar from inside these spurs. The sycamores (Platanaceae) are large, fastgrowing trees found mostly near water. Their large leaves and striking white bark make them easily recognizable. The fruits form fluffy parachutes and are condensed into spheres that hang from the branches during winter. In spring, the wind blows the seeds with their fruit parachutes away. Platanaceae is no longer considered a well-defined family. Most other eudicots are part of an advanced lineage called the core eudicots. Taxonomists have identified several major lineages within the core eudicots. Two of these lineages are the rosids and the asterids.

ests. They produce tiny male flowers on dangling stalks known as catkins. The female flowers produce a single large nut surrounded by tiny leaflike bracts (see figure). In oaks, the nut is an acorn, and the bracts form a cap. The leaves of oaks and beeches consist of a single blade. North American oaks (genus Quercus) consist of two groups. The red and black oaks have leaves with spines, while white oaks have leaves with smooth lobes. Eastern and western North America have entirely separate species of oaks. In eastern North America, all the oaks are deciduous except the live oak, Quercus virginiana, which is evergreen. In western North America, most of the oaks are evergreen. Oaks dominate several kinds of temperate deciduous forests. For example, white oaks (Quercus alba) grow in moist upland forests, post oaks (Quercus stellata) grow in dry forests, and water oaks (Quercus nigra) grow near water. Europe and Asia have a set of oak species entirely different from those of North America. There are few species of beech, and one major species of beech (Fagus grandifolia) dominates North

Rosids In most rosids, the components of the flowers are separate, just as in the primitive dicots. Here are some families of rosids that are important in North America and characteristics by which to recognize them. The oaks and beeches (Fagaceae) are major forest trees. They grow slowly and dominate old for-

xviii+598_Biodiversity_F.indd 185

Water oaks (Quercus nigra) produce separate male and female flowers, but the flowers are on the same plant. The male flowers hang in catkins (green arrow), while the female flowers are acorns (red arrow), here shown at the pollen-receptive stage.  (Stanley A. Rice)

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186 dicots  186 American beech ­forests; in contrast, North America has 90 species of oaks. The American chestnut (Castanea americana) used to dominate large areas of the deciduous forest of eastern North America, but they have (except for resprouted saplings) been destroyed by an accidentally introduced fungus. The walnuts and hickories (Juglandaceae) are also important forest trees, although they are usually minor components mixed into old forests dominated by oaks or beeches. Walnuts (genus Juglans) and hickories (genus Carya) also produce catkins of male flowers. The female flowers produce a single large nut surrounded by a single husk (walnuts) or a husk divided into four parts (hickories). The large leaves consist of several to many small leaflets. The birches and alders (Betulaceae) are small trees that often grow near water. They produce catkins of male flowers and tight clusters of female flowers that sometimes look like cones. The leaves consist of a single blade. By vigorously resprouting, alders (genus Alnus) can recover quickly from flood damage. Alders have bacteria in their roots that manufacture nitrogen fertilizer. Therefore, although they are far less abundant than oaks (there are only eight species of alders in North America), they play an important ecological role. Birches seldom dominate whole forests except in the far north. The seaside alder, Alnus maritima, is an interesting example of a disjunct species, found in only a few locations very distant from one another. The rose family (Rosaceae) has flowers with five petals and many stamens that grow from the edge of a central disc. Although horticultural varieties of roses (genus Rosa) may have many petals, wild roses have only five. The flowers are open, easily accessible by many kinds of pollinators. While the flowers in this family look very much alike, there is great diversity in their growth patterns (small wildflowers to large trees) and fruits, including most of the commercially valuable fruits. In peaches, plums, and cherries (Prunus), a single seed develops inside the fruit. In blackberries (Rubus), many small berries cluster together. In apples (Malus) and pears (Pyrus), the stem at the base of the flower grows up and surrounds the seeds. In strawberries (Fragaria), the stem at the base of the flower grows up and pushes the seeds outward. The strawberry is not actually a fruit; the fruits are the black “seeds” on the outside of the expanded stem. Although commercially valuable, the rose family plays a minor role in natural landscapes compared to oaks: short-lived black cherry trees (Prunus serotina), a few shrubs, and many species of wildflowers. The mulberry family (Moraceae) includes mulberries and figs. Male trees produce catkins of male flowers. Female trees produce clusters of tiny fruits.

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first entry In mulberries (genus Morus), the tiny fruits are on the outside of the cluster. In figs (Ficus), the tiny fruits are on the inside of the cluster; a fig is an inside-out mulberry. Mulberries and figs are very common in tropical rain forests. The North American bois d’arc (Maclura pomifera) produces a fruit that was eaten by mammals that are now extinct. Mulberries, like poppies, produce a defensive milky sap. The leaves consist of a single blade. The legume family (Fabaceae) produces beanlike fruits in which the seeds line up in single file inside a capsule. In most species, the flowers have a boatlike structure, with a banner that resembles a sail and a keel that encloses the stamens and pistil. In some legumes, such as mimosas, the numerous, long, and colorful stamens are the most noticeable feature of the flowers. The leaves often consist of three to several dozen small leaflets. Legumes range in size from small herbaceous plants to large trees. Like alders, legumes have bacteria in their roots that manufacture nitrogen fertilizer. The bacteria are different from those in alders; fertilizer production in alder and legume roots is therefore an example of evolutionary convergence. North American forests have a few leguminous trees, such as the black locust (Robinia pseudoacacia) and honey locust (Gleditsia triacanthos), and grasslands have many leguminous wildflowers, such as the poisonous locoweeds (genus Astragalus). However, most legumes grow in tropical rain forests and tropical seasonal forests. Leguminous acacias are very important components of tropical savannas. Many acacias have evolved close cooperation with ants. The willow family (Salicaceae) consists of willow, cottonwood, poplar, and aspen trees. Male trees produce catkins of male flowers, and female trees produce catkins of female flowers (see figures on page 187). The leaves consist of a single blade. These trees usually grow fast in areas that have been recently disturbed, for example, by flooding. Because of its fast growth, the black poplar (Populus trichocarpa) was one of the first plant species for which biotechnologists decoded the entire genome. Members of the mustard family (Brassicaceae) are often called “crucifers” because their flowers have four petals in the shape of a cross. Almost all of them are wildflowers, often weedy components of recently disturbed fields. Many important vegetables, such as radishes, are in the mustard family; cabbage, cauliflower, broccoli, and brussels sprouts were all bred from a single species of wild plant, Brassica oleracea. A species that lives in Europe and Asia, Arabidopsis thaliana, goes through its entire life cycle in a few weeks and has therefore been of great interest to genetic researchers; it was one of the first plant species for which biotechnologists decoded the entire genome.

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Cottonwoods (Populus deltoides) grow as separate male and female plants. Male cottonwood trees produce catkins of male flowers that release pollen (left), while female cottonwood trees produce catkins of female flowers that produce seeds (right).  (Stanley A. Rice)

The sumac family (Anacardiaceae) consists of bushes such as the North American sumac, tropical trees such as cashew and mango, and vines such as poison ivy, poison oak, and poison sumac (genus Toxicodendron). Poison ivy is not actually poisonous to animal metabolism. The urushiol in its leaves provokes a strong allergic reaction in most people—but not in everyone, and not in mammals that eat its leaves (such as deer) and its berries (such as squirrels). Poison ivy and poison oak are easily recognizable because their leaves consist of three leaflets. The maple family (Sapindaceae, formerly Aceraceae) includes maple trees and soapberry trees. Sugar maples (Acer saccharum) are major components of the temperate deciduous forest, while silver maples (Acer saccharinum) grow vigorously in floodplains. Maple trees and shrubs may be recognized by the fruits, in which a seed is enclosed in a single wing. This allows the fruit to whirl like a helicopter blade in the wind. Sugar maples are famous because their sap can be boiled into syrup and for their brilliant autumn colors in eastern North America.

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The grape family (Vitaceae) consists of vines, including several species of wild grape (genus Vitis) and the Virginia creeper (Parthenocissus quinquefolia). The leaves consist of a single blade, and clusters of small flowers emerge from the opposite side of the stem from the leaf. Domesticated grapes (Vitis vinifera) come from Europe, but rootstocks of wild American grapes from Texas and Oklahoma (Vitis rotundifolia) were resistant to fungi that killed European grapes in the late 19th century. Grafting European grapes onto American rootstocks helped to save the French wine industry. The spurge family (Euphorbiaceae) consists of herbs and shrubs that contain poisonous milky sap. Male flowers cluster around a female flower; in the genus Euphorbia, this cluster is reduced into a structure that looks like a single flower. In North America, most spurges are weedy herbaceous plants or small shrubs in dry areas. In African deserts, spurges have evolved a resemblance to the cacti of American deserts, another example of evolutionary convergence. The most poisonous plant chemical known, ricin, is produced by the castor bean

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bush Ricinus communis. In tropical forests, some are trees, such as the Brazilian rubber tree (Hevea brasiliensis), in which the milky sap can be dried to form rubber. Manioc (Manihot esculentum) is a small tree whose starchy roots are the tropical counterpart of potatoes; in some varieties, people must leach out the poisons before consuming the starch.

Asterids In many asterids, parts of the flowers (particularly the petals) have fused together over evolutionary time, in some cases forming tubular structures that can be pollinated only by specialized animals. Here are some families of asterids that are important in North America and characteristics by which to recognize them. The nightshade family (Solanaceae) consists of mostly herbaceous plants noted for their poisonous leaves, stems, and fruits. Some members of this family, however, are important foods, such as potatoes (Solanum tuberosum) and tomatoes (Lycopersicon esculentum). The mint family (Lamiaceae), most of which are herbaceous, is recognizable because its tubular flowers have a landing platform for pollinators, and its stems are square in cross-section. Many spices come from the leaves of these plants, including mint, oregano, basil, thyme, and sage. Some species are poisonous. In tropical forests, some mints are trees, such as teak (Tectona grandis), which is famous for wood used in shipbuilding. The carrot family (Apiaceae), also herbaceous, is easily recognizable because its flowers are in umbrella-shaped clusters. Carrots and celery are members of this family. Many spices come from the fruits of these plants, including cumin, coriander, dill, fennel, anise, and caraway. The seeds of celery and the leaves of coriander (known as cilantro) are also popular flavors. Some species are poisonous. The milkweed family (Apocynaceae) consists mostly of herbaceous plants with defensive milky sap. The clustered flowers are easily recognizable because the five coronas, which look like an extra set of petals, form beaks that enclose each of the five stamens. The composite family (Asteraceae) consists of almost 23,000 species of plants, most of them herbaceous weeds that grow rapidly in recently disturbed areas or in grasslands. Composites have flowers that form highly complex reproductive structures. These structures are called composite because each of them consists of several or many small flowers surrounded by small leaflike bracts. Examples are the wild balsamroot (see figure) and the sunflower. A sunflower appears to be a flower that consists of yellow petals radiating outward from a central disc of small struc-

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Composite dicots (family Asteraceae) have numerous small flowers (florets) compressed into a single flowerlike structure called a head. Disk florets (red arrow) are tubular and erect; they produce both pollen and seeds. Unopened disk florets are in the center of the head. Each structure that looks like a petal is actually a ray floret (green arrow) that radiates from the center of the head. This species is Balsamorhiza sagittata from the Black Hills of South Dakota.  (Stanley A. Rice)

tures. Each of these “petals,” however, is a separate ray flower. Each ray flower consists of five petals fused into a single petal surrounding a pistil. The central disc contains several to many disc flowers, each one of which consists of five petals fused into a single petal surrounding stamens and a pistil. A sunflower, therefore, is dozens of flowers united into a single structure. Most species of composites have both ray and disc flowers. Some, such as dandelions, consist only of raylike flowers and have no central disc. Some, such as thistles, consist only of disc flowers and have no rays.

Other Core Eudicots Lineages of core eudicots other than rosids and asterids also contain important plants. One of these is the cactus family (Cactaceae), whose flowers (usually large) have numerous petals and stamens (see

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dicots  189 figure). Primitive cactus trees in Central and South America have spines and succulent leaves. Leafless cacti, in the deserts of North and South America have green, succulent stems but no leaves. From simple ancestors that lived near the beginning of the Cretaceous period, the flowering plants have diversified into hundreds of thousands of species, produced many specialized reproductive structures, and adapted to every habitat on Earth, including coastal Antarctica. Of the two flowering plant species that live in Antarctica, one is a monocot and one is a dicot. Most flowering plants are dicots. No other group of multicellular organisms, except insects, have evolved such tremendous diversity. Explorers continue to discover new species of dicots, usually, but not always, in tropical forests. Many species are driven to extinction, often before they have been studied by scientists, when humans destroy their habitats. This is a tremendous loss to the ecological communities of which they are the basis, to scientific research, and to the human economy. See also Essay: “Ghosts of Biodiversity Past;” adaptive radiation; biodiversity, resources for agriculture; biodiversity, resources

Cactus flowers (such as this Opuntia basilaris from the Anza Borrego Desert of California) have numerous petals and numerous stamens.  (Stanley A. Rice)

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for medicine; cladistics; coevolution; Cretaceous period, biodiversity in; flowering plants (angiosperms); monocots; pollination. Further Reading Abrams, Marc D. “Adaptations and responses to drought in Quercus species of North America.” Tree Physiology 7 (1990): 227–238. Anderson, Edward F. The Cactus Family. Portland, Ore.: Timber Press, 2001. California Oak Mortality Task Force. “California Oak Mortality Task Force.” Available online. URL: http:// www.suddenoakdeath.org. Accessed May 13, 2011. Callaway, Ragan M. “Effect of shrubs on recruitment of Quercus douglasii and Quercus lobata in California.” Ecology 73 (1992): 2,118–2,128. ———, Nalini M. Nadkarni, and Bruce E. Mahall. “Facilitation and interference of Quercus douglasii on understory productivity in central California.” Ecology 72 (1991): 1,484–1,499. Carney, Shanna E., et al. “Invasive Argentine ants (Linepithema humile) do not replace native ants as seed dispersers of Dendromecon rigida (Papaveraceae) in California, USA.” Oecologia 135 (2003): 576–582. DeBeaulieu, Antoine LeHardy. An Illustrated Guide to Maples. Portland, Ore.: Timber Press, 2003. Ertter, Barbara. “Floristic surprises in North America north of Mexico.” Annals of the Missouri Botanical Garden 87 (2000): 81–109. Available online. URL: http:// ucjeps.berkeley.edu/floristic_surprises.html. Accessed March 23, 2005. Keator, Glenn. The Life of an Oak: An Intimate Portrait. Berkeley, Calif.: Heyday Books, 1998. Logan, William Bryant. Oak: The Frame of Civilization. New York: Norton, 1996. Miller, Howard A., and Samuel Lamb. Oaks of North America. Happy Camp, Calif.: Naturegraph Publishers, 1984. Mohan, Jacqueline E., et al. “Biomass and toxicity responses of poison ivy (Toxicodendron radicans) to elevated atmospheric CO2.” Proceedings of the National Academy of Sciences USA 103 (2006): 9,086–9,089. National Research Council (U.S.). Tropical Legumes: Resources for the Future. Washington, D.C.: National Research Council, 2002. Panizzi, L., et al. “Composition and antimicrobial properties of essential oils of four Mediterranean Lamiaceae.” Journal of Ethnopharmacology 39 (1993): 167–170. Petrides, George A. A Field Guide to Trees and Shrubs. Boston: Houghton Mifflin, 1972. Rizzo, D. M., et al. “Phytophthora ramorum as the cause of extensive mortality of Quercus spp. and Lithocarpus densiflorus in California.” Plant Disease 86 (2002): 205–214. Russell, Charles E., and Peter Felker. “The prickly-pears (Opuntia spp., Cactaceae): A source of human and

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190 dinosaurs  190 animal food in semiarid regions.” Economic Botany 41 (1987): 433–445. Russell, Tony, and Catherine Cutler. The World Encyclopedia of Trees. London: Anness Publishing, 2003. Strauss-Debenedetti, Sylvia, and Fakhri A. Bazzaz. “Plasticity and acclimation to light in tropical Moraceae of different sucessional positions.” Oecologia 87 (1991): 377–387. Tudge, Colin. The Secret Life of Trees: How They Live and Why They Matter. New York: Penguin, 2006. Wanvestraut, Robert H., et al. “Competition for water in a pecan (Carya illinoensis K. Koch)-cotton (Gossypium hirsutum L.) alley cropping system in the southern United States.” Agroforestry Systems 60 (2004): 167–179.

dinosaurs  The term dinosaur usually refers to reptiles, many of them large, that dominated Earth during the Mesozoic era. They are probably the most famous examples of extinct biodiversity. The earliest dinosaurs lived during the Triassic period. Dinosaurs diversified into numerous forms during the Jurassic and Cretaceous periods, perhaps because one of the mass extinctions, which occurred at the end of the Triassic period, removed competition from other vertebrate groups. The dinosaurs themselves became extinct at the end of the Cretaceous period. Modern phylogeny classifies organisms based on evolutionary divergence. Since birds and mammals diverged from the group of vertebrates usually called reptiles, there is no such thing as reptiles unless one includes birds and mammals in the group. Dinosaurs had many characteristics of skin, teeth, and bones that would remind observers of the reptiles with which they are familiar. In fact, since birds evolved from dinosaurs, the cladistic approach would indicate that the dinosaurs still exist: They are birds. Therefore, the dinosaurs that most people think of are more properly called nonavian dinosaurs. Although dinosaurs are truly ancient, the therapsid (mammal-like) reptile lineage had diverged before the dinosaur lineage, and true mammals already existed by the time the first dinosaurs roamed Earth. The first dinosaurs to be studied were large, which is why Sir Richard Owen gave them the name dinosaurs (Greek for “terrible lizards”) in 1842. The first famous dinosaur discoveries came from the northern plains of the United States. In the late 19th century, almost 150 new dinosaur species were revealed by the excavations and reconstructions of the American paleontologists Edward Drinker Cope and Othniel Charles Marsh. They began as collaborators but ended up in a three-decade-long intense rivalry. Marsh did not perform much field work. One account claims that Marsh visited a spot where

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first entry dinosaur bones were lying about like logs but did not recognize them. Marsh was, however, rich enough to buy fossils and to hire field workers. His uncle, George Peabody, endowed a museum at Yale University specifically so that Marsh could study dinosaurs. Cope, who was also wealthy, spent much productive time in the field. He worked in Montana at the same time that General Custer’s army was being annihilated nearby. When suspicious Native Americans checked out his camp, he entertained them by taking out his false teeth until they went away. A schoolteacher who found some dinosaur bones genially informed both Marsh and Cope about them. Cope sent the schoolteacher money and told him to ask Marsh to send all the specimens back to him. The rivalry grew intense enough that the excavators of the Marsh and Cope camps threw rocks at one another. Cope lost his money, but not his ego, in financial speculation and died poor. He willed his body to a museum, hoping to have his skeleton used as the “type specimen” to represent the human species. When the skeleton was prepared, it was found to have syphilitic lesions and was unsuitable as a type specimen. Most of what scientists know about dinosaurs comes from the study of fossilized bones, in the tradition of Cope and Marsh. Recently, this has included the microscopic study of the spaces left by blood vessels in the bones. Other kinds of fossil evidence have also allowed many insights into the lives of dinosaurs, such as the following. ●●

●●

●●

Gastroliths. These are “stomach stones” that helped grind coarse plant material in the stomachs of some dinosaurs that ate branches and leaves. Many modern birds swallow stones that help them grind their food. Eggs. Fossilized eggs with embryos inside reveal some of the processes of dinosaur development. In addition, the discovery of caches of eggs reveals that dinosaurs cared for nests of eggs in a manner similar to that of most modern birds. Soft material. In 2005, the paleontologist Mary Higby Schweitzer discovered soft tissue, including what may be blood vessels and cells, in a dinosaur bone. Some of this soft tissue was collagen, the protein that makes up cartilage. Analysis of this collagen revealed a close relationship with birds rather than with reptiles or mammals.

Since the time of Owen, Marsh, and Cope, dinosaurs have entered the popular imagination as emblematic both of huge size and of evolutionary failure. In both ways, the image is unfair. First, many

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dinosaurs 191 dinosaurs were small or medium sized. Many of the smaller dinosaurs were sleek and rapid, and some had feathers. Second, there were many kinds of dinosaurs all over the world; they were, for more than 100 million years, an astounding evolutionary success. Some dinosaurs were extremely large. Sauroposeidon proteles, which lived 110 million years ago in what is now Oklahoma, had a body 100 feet (30 m) in length, with a neck more than 30 feet (10 m) long. the size estimate of the neck of this dinosaur is based on the fact that most vertebrates have the same number of neck vertebrae, and the longest vertebrae found for this dinosaur were about five feet (152.4 cm) long. the sauropod Supersaurus weighed nearly 110 tons (100 metric tons), the largest animals to ever live on land (see figure). they were also the largest four-legged animals that could possibly have lived; if they had grown to 154 tons (140 metric tons), the size of the legs necessary to support the weight would have become so great that the legs would not have been able to move. Sauropods were herbivorous dinosaurs whose large size and long necks allowed them to eat leaves even in the tallest trees. instead of having large teeth to grind the branches and leaves, they had small sharp teeth that could tear leaves and branches to be swallowed whole. Grinding occurred in the stomach with the aid of gastroliths. if dinosaurs such as Apatosaurus (formerly Brontosaurus) held their heads and necks upright, they would have needed seven times the blood pressure of a human, and the huge heart would have required the energy equivalent to about half the food intake of the dinosaur. Some

paleontologists say that huge, long-necked dinosaurs did not raise their heads. Perhaps they lifted their heads just long enough to eat. in contrast, the carnivorous dinosaurs, even the famous Tyrannosaurus rex, were much smaller (about five tons [4.6 metric tons]) because meat was much less available than vegetation (see figure on page 192). the huge sauropod dinosaurs were probably also stupid. the huge, long-necked dinosaurs had small brains (and small teeth) because the force of leverage that would have been necessary to raise a large head at the end of a long neck would have been too great. large dinosaurs were also stupid because a single, large brain in the head would have been too far away from the tail to allow quick control over muscle movement. the large dinosaurs had a brain but also had a secondary ganglion of nerves near the base of the tail, which aided in control of posterior muscles. among the oldest known dinosaur fossils are Herrerasaurus and Eoraptor, from the late triassic period about 230 million years ago. Because these fossils already had dinosaur specializations, the ancestral dinosaur must have lived even earlier. these earliest dinosaurs were about the size of a human and had narrow heads, long pointed snouts, mouths that extended from ear to ear, many small sharp teeth, and large eyes. Unlike nearly all other reptiles, these early dinosaurs walked on their two hind legs, which allowed their “hands” to evolve the ability to grasp prey. From animals similar to Herrerasaurus, two lineages of reptiles evolved: the bird-hipped dinosaurs (ornithischians) and the lizard-hipped dinosaurs (saurischians), which evolved

Grazing dinosaurs, such as Supersaurus, were the largest land animals to ever live—each leg was the size of a human.

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Predatory dinosaurs, such as Tyrannosaurus rex, were much smaller than the grazing dinosaurs but were the largest terrestrial predators to ever live.

into numerous forms during the ensuing Jurassic and cretaceous periods. Ornithischians had a pelvis that reminded early paleontologists of birds. their teeth and jaws allowed for the tearing and grinding of plant materials, and the enlarged ribs and pelvis allowed for the digestion of large quantities of plant material. Despite their name, the ornithischians were not the ancestors of birds; they all met extinction at the end of the cretaceous period. as time went on, ornithischians diverged into different lineages, all of which became much larger than their Herrerasaurus ancestors. they included the following. ●





Pachycephalosaurs, or “thick-headed” dinosaurs, had skulls with thick domes that may have served as battering rams during fights. Recent research has failed to fi nd evidence of tiny fractures that would have resulted from such confl icts. Ceratopsians, or horned dinosaurs, reverted to walking on all fours. By the late Paleozoic, some were quite large and had large horns, such as Triceratops. Thyreophores, or “shield-bearing” dinosaurs, evolved into large animals with armored plates and, in the stegosaurs, a paired row of large plates along the back.

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Ornithopods also evolved into large forms but remained primarily bipedal.

Saurischian dinosaurs had long necks and “hands” with long index fi ngers, a basic pattern now found in many birds. they diverged into the sauropods and the theropods. ● ●

Sauropods became very large. an example is the Supersaurus mentioned above. Theropods had long, flexible necks, sharp teeth and claws, and “hands” with three curved claws that were good at grasping. their bones were thin, light, and hollow, like those of modern birds. their collarbones were fused into a wishbone, or furcula, a feature found only in birds today. these features made the later development of fl ight possible.

From large theropod ancestors, coelourosaurians evolved. Some of them, such as Tyrannosaurus, were quite large, with big heads but very small arms. Others were much smaller, with larger brains and eyes like modern birds, resembling an ostrich in body form, even to the point of having a toothless beak. all but one of these birdlike lineages became extinct. the lineage that survived to eventu-

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dinosaurs 193 ally become birds was the maniraptorans, which were dinosaurs with feathers. the maniraptoran dinosaurs apparently had hollow bones, a wishbone, and feathers before they had the ability to fly. evolutionary biologists conclude from this that the original function of feathers was not for fl ight but to hold in body heat. this may have been the fi rst step in warm-bloodedness, which is important in providing the energy needed for fl ight. Specimens of one of them, Oviraptor, have been found brooding eggs in the fashion of modern birds, another indication of warm-bloodedness. Archaeopteryx was a feathered dinosaur (a bird) that retained many dinoOne evolutionary branch saur characteristics, such as teeth, claws on its wings, and vertebrae in its of maniraptorans not only had tail. It had feathers similar to those of modern birds. feathers but could fly. the earliest known of these was Archaeopteryx, from 150 million years ago, during the landscape may have been one reason that dinosaurs Jurassic period (see figure). although skeletally simwere in decline during the late cretaceous. Massive ilar to other maniraptorans, Archaeopteryx resemvolcanic eruptions changed the climate and further bled modern birds in having long arms that formed hastened the decline of dinosaurs. it was appara wing with fl ight feathers, reduced teeth, and a ently an asteroid that hit earth 65 million years ago large brain. Because maniraptorans were runners, that sent all remaining dinosaurs, except birds, into evolutionary biologists believe that fl ight originated extinction. Until almost the last moment, there were from rapid running “from the ground up” rather at least 100 species of dinosaurs. Fossil evidence sugthan from gliding “from the trees down.” the evogests that some dinosaurs survived the cretaceous lutionary lineage of Archaeopteryx became extinct, extinction, but not many and not for long. but related lineages continued to evolve more birdSee also cretaceous period, biodiversity like characteristics, such as a larger breastbone in; Jurassic period, biodiversity in; triassic that allowed massive fl ight muscles to anchor. By period, biodiversity in. the early cretaceous period, before the extinction of nonavian dinosaurs, there were fi nch-sized Further reading dinosaur birds capable of a modern type of fl ight. achenbach, Joel. “Dinosaurs: cracking the mystery of how Other lineages adapted to an aquatic existence and they lived.” National Geographic, March 2003, 2–33. resembled modern waterfowl, some of them even asara, John M., et al. “Protein sequences from mastodon losing the ability to fly. all but one lineage, the and Tyrannosaurus rex revealed by mass spectrosbirds, became extinct by the end of the cretaceous copy.” Science 316 (2007): 280–285. period. Bakker, Robert t. The Dinosaur Heresies. new york: WilDinosaurs diversified into many forms, from liam Morrow, 1986. huge consumers of branches and leaves to small, ———. “the bite of the Bronto.” Earth 3 (1994): 26–33. sleek predators, mainly during the Jurassic and cre———. “Dinosaur mid-life crisis: the Jurassic-cretaceous taceous periods. When flowering plants evolved at transition in Wyoming and colorado.” in: lucas, S.G., the beginning of the cretaceous, some dinosaurs et al., eds. Lower and Middle Cretaceous Terrestrial evolved the ability to consume their leaves, but there Ecosystems: New Mexico Museum of Natural History was apparently no coevolution between nonavian and Science Bulletin 14 (1998): 67–77. dinosaurs and flowering plants for pollination of carpenter, K., K. F. Hirsch, and J. R. Horner, eds., Dinosaur flowers or dispersal of fruits. insects (and some birds) Eggs and Babies. cambridge: cambridge University evolved many pollinating forms, and mammals were Press, 2007. particularly good dispersers of fruits and seeds. the carrano, Matthew t., and Patrick M. O’connor. “Bird’sincreasing dominance of flowering plants in the eye view.” Natural History, May 2005, 42–47.

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194 disjunct species  194 Clark, James M., and Xing Xu. “Evolutionary transitions among dinosaurs: Examples from the Jurassic of China.” Evolution Education and Outreach 2 (2009): 236–247. Currie, Philip E., and Kevin Padian. Encyclopedia of Dinosaurs. New York: Academic Press, 1997. Erickson, Gregory M., et al. “Tyrannosaur life tables: An example of nonavian dinosaur population biology.” Science 313 (2006): 213–214. Fiorillo, Anthony R. “The dinosaurs of arctic Alaska.” Scientific American, December 2004, 84–91. Fipper, Steve. Tyrannosaurus Sue: The Extraordinary Saga of the Largest, Most Fought Over T. Rex Ever Found. New York: Freeman, 2000. Foster, J. Jurassic West: The Dinosaurs of the Morrison Formation and Their World. Bloomington, Ind.: Indiana University Press, 2007. Horner, John R., Kevin Padian, and Armand de Ricqlès. “How dinosaurs grew so large—and so small.” Scientific American (July 2005): 56–63. Irmis, Randall B., et al. “A late Triassic dinosauromorph assemblage from New Mexico and the rise of dinosaurs.” Science 317 (2007): 358–361. Levin, Eric. “Dinosaur family values.” Discover, June 2003, 34–41. Norell, Mark. Unearthing the Dragon: The Great Feathered Dinosaur Discovery. New York: Pi Press, 2005. Organ, Chris L., et al. “Molecular phylogenetics of mastodon and Tyrannosaurus rex.” Science 320 (2008): 499. Parker, Steve. Dinosaurus: The Complete Guide to Dinosaurs. Richmond Hill, Ont.: Firefly Books, 2003. Prum, R., and A. H. Brush. “The evolutionary origin and diversification of feathers.” Quarterly Review of Biology 77 (2002): 261–295. Sampson, Scott D. Dinosaur Odyssey. Berkeley: University of California Press, 2009. Sander, P. Martin, and Nicole Klein. “Developmental plasticity in the life history of a prosauropod dinosaur.” Science 310 (2005): 1,800–1,802. Schweitzer, Mary Higby, et al. “Beta-keratin specific immunological reactivity in feather-like structures of the Cretaceous alvarezsaurid, Shuvuuia deserti.” Journal of Experimental Zoology B (Mol Dev Evol) 285 (1999):146–157 ———, et al. “Gender-specific reproductive tissue in ratites and Tyrannosaurus rex.” Science 308 (2005): 1,456–1,460. ———, et al. “Analyses of soft tissue from Tyrannosaurus rex suggest the presence of protein.” Science 316 (2007): 277–280. Stevens, Kent A., and J. Michael Parrish. “Neck posture and feeding habits of two Jurassic sauropod dinosaurs.” Science 284 (1999): 798–800. Stokstad, Erik. “Did horny young dinosaurs cause illusion of separate species?” Science 318 (2007): 1,236.

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first entry Turner, Alan H., et al. “A basal dromaeosaurid and size evolution preceding avian flight.” Science 317 (2007): 1,378–1,381. ———, et al. “Feather quill knobs in the dinosaur Velociraptor.” Science 317 (2007): 1,721. Weishampel, David B., Peter Dodson, and Halszka Osmólska. The Dinosauria, 2nd ed. Berkeley: University of California Press, 2004. Xu, X., et al. “Basal tyrannosauroids from China and evidence for protofeathers in tyrannosauroids.” Nature 431 (2004): 680–684. Yeoman, Barry. “Schweitzer’s dangerous discovery.” Discover, April 2006, 36–41, 77.

disjunct species  Disjunct species contain or consist of populations (disjunct populations) that are isolated from one another. Because of the distances that separate the populations of disjunct species, gene flow rarely occurs between them. Gene flow occurs when pollen or seeds (of plants) or animals travel from one population or part of a population to another. If the populations of a disjunct species are genetically different, the populations can often be described as subspecies. If enough time passes, it is practically inevitable that the disjunct populations will evolve into separate species unless they become extinct. Two ways are generally recognized in which populations within a species could have become disjunct. The first is that the populations are relictual, that is, they are relicts of a large ancestral population (see figure on page 195). Populations of the species that were formerly present between the disjunct populations have disappeared, leaving the relictual populations isolated from one another. If the two relictual populations diverge, they are considered the product of vicariance. The other way that disjunct populations can form is that a few organisms dispersed (as seeds or as a small flock) from the main population and settled in a distant location, forming a new population, an explanation called dispersal. How can scientists determine which explanation, the relictual versus the dispersal, is correct? The best evidence is if fossil or other evidence of the formerly intervening populations can actually be discovered. In some cases, evidence for populations of that particular species cannot be found, but if it is found for other species with similar disjunct distributions, then it can be inferred for the species in question as well. For example, there are many species of wildflowers in the alpine tundra of the high elevations of the Sierra Nevada, Cascade, Olympic, Rocky, and Sangre de Cristo Mountains of western North America that are very similar, in some cases nearly identical, to those of the arctic tundra of northern Alaska and Canada. Hundreds

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disjunct species  195

Fan palms (Washingtonia filifera) have been planted widely throughout the western United States. However, they are native only to palm oases in the deserts of the southwestern United States, where their survival is in jeopardy. The wild populations of palms, such as this one in the Anza-Borrego Desert of California, are relicts of larger populations that grew before the formation of deserts in the Southwest.  (Stanley A. Rice)

or thousands of miles separate the disjunct arctic and alpine populations. These distributions were, in fact, somewhat difficult to explain before Louis Agassiz and Charles Darwin. Agassiz explained the ice ages: At various times, much of North America was, in fact, in the arctic tundra zone. As the glaciers retreated, some tundra plants migrated north, where they are now found as arctic tundra; others migrated up the mountains, where they are now stranded as alpine tundra. Darwin explained the subsequent vicariance of these populations by evolution occurring separately in each. This is also the explanation of how disjunct populations of tundra species, such as the sedge Eriophorum vaginatum and boreal species such as the larch tree, came to be stranded in the bogs of northern states in the United States, such as Michigan. The next best evidence comes from genetic comparisons. If the disjunct populations can be shown to have several distinct mutations within their DNA, mutations not shared with one another, then they may be relictual. If one of the populations has DNA that is a subset of another population, then the first population dispersed from the second. The only problem with this approach is that even if one population dispersed from another, the new population can evolve its own distinct mutations, which would

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make it appear as relictual. Therefore, genetic studies are most useful to detect recently dispersed disjunct populations. Numerous examples of disjunct populations have been found. One example is the seaside alder, Alnus maritima. Many alders are large bushes that grow in swamps or next to streams and rivers with rocky beds. The hazel alder, Alnus serrulata, grows in this kind of streamside habitat throughout much of the eastern United States, but unlike the hazel alder, the seaside alder is a disjunct species and consists entirely of three small disjunct populations. One population lives on the Delmarva Peninsula, east of Chesapeake Bay. Another lives almost entirely within Johnston County in central Oklahoma. The third lives in a single swamp in Bartow County in northwest Georgia. Why is the seaside alder so rare, despite its apparent similarity to the hazel alder, which grows throughout eastern North America? First, consider the vicariance hypothesis. Alders reproduce in two ways. Their seeds, produced in autumn, grow best in sunny locations with moist mineral soil. Along many rivers, locations that have moist mineral soil are often shaded and not good for the growth of alder seedlings. In a second reproductive mode, once a bush is established, it can keep resprouting from the same roots even if floods wash many of its branches away or if it is subsequently shaded by the growth of larger trees. The botanists Stanley Rice and J. Phil Gibson have demonstrated that both species of alders prefer sunny over shady conditions, but the hazel alders are found in shade more frequently than seaside alders. In the past (perhaps after the most recent ice age), both species of alders may have established themselves abundantly in the new landscape of sunny, moist, mineral soil. Subsequent regrowth of forests shaded the alder habitats, and the hazel alders have tolerated these shaded conditions at least a little better than the seaside alders. Hazel alders have therefore persisted throughout eastern North America, whereas the seaside alders have persisted in only three places. The seaside alder survived in these three places by chance, not because the three places were the most suitable habitats. The climatic conditions in Oklahoma, Georgia, and Delaware are quite different, and without doubt there are many places between these three locations that are better for seaside alder growth but in which the seaside alder by chance became extinct. Researchers have found that separate mutations have occurred in the three populations. These three populations are now classified as three distinct subspecies. There is no direct evidence that earlier populations of the seaside alder lived in places between Oklahoma,

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196 disjunct species  196 Georgia, and Delaware. Fossilized leaves that are identical to modern seaside alder leaves have been found in northwestern North America, which suggests that this species once grew across the entire continent. The species of alder that are most closely related to the seaside alder, in fact, grow in eastern Asia. This is the vicariance hypothesis for the disjunct distribution of the seaside alder. Now consider the dispersal hypothesis. The seaside alder might have originated in one location, perhaps Delmarva, and subsequently dispersed to the other locations. How could this have happened? Something, or someone, might have carried the seeds from Delmarva to the other locations. Neither wind nor watershed patterns seem to suggest how this could have occurred. Native Americans use alder bark as a medicine and may have carried seeds or cuttings with them. The Georgia population is within the former Cherokee Nation territory, and the Cherokees are known to have moved south from the Iroquoian lands of what is now the northeastern United States. Subsequently, the Cherokee were relocated by the United States government to Oklahoma in 1835. Could Cherokee have carried the seeds or small plants with them from the Northeast to Georgia to Oklahoma, connecting all three of the existing populations? This explanation is unlikely to be true, because the three populations (subspecies) are different enough that they must have been separated for a long time, much longer than the Cherokee migrations of ca. 1000 and 1835 c.e. In the case of the seaside alder and in many other cases as well, the disjunct populations are threatened with extinction. Not only do small populations have a greater risk of extinction, disjunct populations are frequently not in the habitats most suitable for them. Oklahoma seaside alders have been planted and are surviving well in distant locations, while they are barely surviving in Oklahoma, where they can withstand the summer heat only if the soil is continually wet. This is because the climatic changes that isolated the disjunct populations in the first place are now threatening them with extinction. The Georgia and Delmarva populations are similarly threatened. In other cases, a species may have a large, central population and several disjunct populations at some distance away from the central population, as in the following examples: ●●

●●

The least tern (Sternula antillarum) is a shorebird that is abundant in many areas, but the interior subspecies of the least tern (which migrated up the Mississippi and Arkansas Rivers into Oklahoma) is rare. The white spruce (Picea glauca) is abundant in the subalpine forests of the mountains

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first entry

●●

●● ●●

●●

●●

of central North America and the boreal forests of Canada. The limber pine (Pinus flexilis) is fairly common in the Rocky Mountains and Sierra Nevada. In the Black Hills of South Dakota, relictual populations of both the white spruce and the limber pine survive. They became stranded in the Black Hills after the most recent ice age and have declined in abundance since then. The spruce remains abundant in the Black Hills because it grows well in cool, moist, shaded areas of the northern hills, although global warming could rapidly create conditions in which they can no longer survive. In contrast, the limber pine has nearly become extinct in the Black Hills because it requires cool, dry, sunny conditions, which are now rare in the Black Hills. The few remaining limber pines are being crowded and shaded out by the extremely abundant ponderosa pines. The bishop pine (Pinus muricata) grows near the northern coast of California. There is a small population of bishop pines about 200 miles from the main population in the Purísima Hills near the central California coast. It persists on a rare kind of soil composed almost entirely of dead diatoms that accumulated in shallow oceans millions of years ago. A genus of heather shrub, Erica, is abundant in Europe but also in South Africa. Olive trees are also disjunct. The familiar olive tree (Olea europaea) grows around the Mediterranean Sea, O. paniculata grows in the forests of Queensland in Australia, and the black ironwood O. laurifolia grows in South Africa. The crowberry family Empetraceae has disjunct genera. Corema album grows in the Azores, Spain, and Portugal, while C. conradii grows in the northeastern United States and adjacent areas in Canada. Species of the genus Empetrum live in cool temperate regions of the Northern and Southern Hemispheres, but not in between. Many freshwater fishes have disjunct populations because their habitats are separated from one another by large expanses of dry land.

In some cases, humans are strongly implicated in disjunct distributions of other species. The pygmy shrew (Sorex minutus) has an Irish population disjunct from the mainland European population. Genetic analysis shows that the Irish shrews are all

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disturbances, ecological  197 descended from a recent founding event. They may have been stowaways in a human vessel. Disjunct populations are frequently the failed dead ends of evolution. They can also be wellsprings of new biodiversity. Because they are disjunct, these populations are reproductively isolated from the larger population, which allows them to evolve in a different direction. If they have dispersed from a large, central population, they may also by chance be genetically different from the original population. Evolution can occur more rapidly in small populations. If the disjunct population evolves rapidly, it can produce a new species that will appear on the scene in what amounts to a geological instant. Much of the work of saving biodiversity is in saving small disjunct populations of rare species in the face of rapid climate change. See also biogeography; bogs, life in; extinction; founder effect and genetic drift; ice ages; population genetics; speciation; tundra. Further Reading Bernardi, G., and J. Lape. “Tempo and mode of speciation in the Baja California disjunct fish species Anisotremus davidsonii.” Molecular Ecology 14 (2005): 4,085–4,096. Coleman, Max, et al. “Repeat intercontinental dispersal and Pleistocene speciation in disjunct Mediterranean and desert Senecio (Asteraceae).” American Journal of Botany 90 (2003): 1,446–1,454. Fok, Koon Wah, et al. “Inferring the phylogeny of disjunct populations of the azure-winged magpie Cyanopica cyanus from mitochondrial control region sequences.” Proceedings of the Royal Society of London B (Biology) 269 (2002): 1,671–1,679. Gibson, J. Phil, Stanley A. Rice, and Clare M. Stucke. “Comparison of population genetic diversity between a rare, narrowly distributed species and a common, widespread species of Alnus (Betulaceae).” American Journal of Botany 95 (2008): 588–596. Habel, Jan Christian, and Thorsten Assmann. Relict Species: Phylogeography and Conservation Biology. Berlin: Springer, 2010. Koenemann, Stefan, et al. “A new, disjunct species of Speleonectes (Remipedia, Crustacea) from the Canary Islands.” Marine Biodiversity 39 (2009): 215–225. Masheretti, S., et al. “How did pygmy shrews colonize Ireland? Clues from a phylogenetic analysis of mitochondrial cytochrome b sequences.” Proceedings of the Royal Society of London B (Biology) 270 (2003): 1,593–1,599. Penman, T. D., et al. “Bioclimatic analysis of disjunct populations of the giant burrowing frog, Heleioporus australiacus.” Journal of Biogeography 32 (2005): 397–405.

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Schrader, James A., William R. Graves, Stanley A. Rice, and J. Phil Gibson. “Differences in shade tolerance help explain varying success in two sympatric Alnus species.” International Journal of Plant Sciences 167 (2006): 979–989. Terry, Astrid, et al. “Restricted gene flow and incipient speciation in disjunct Pacific Ocean and Sea of Cortez populations of a reef fish species, Girella nigricans.” Evolution 54 (2000): 652–659. Wisheu, Irene C., et al. “Disjunct Atlantic coastal plain species in Nova Scotia: Distribution, habitat and conservation priorities.” Biological Conservation 68 (1994): 217–224.

disturbances, ecological  Ecological disturbances are any events that damage or remove the dominant vegetation in an ecological community. They can be as small as a gopher mound in a grassland or a tree falling in a forest or as large as a fire or hurricane that damages an extensive area. They usually occur individually, but during the ice ages glaciers caused many thousands of disturbances simultaneously. The term disturbance carries negative connotations, and for the individual plants in the dominant vegetation a disturbance is indeed negative. However, a disturbance can also be considered an abrupt release of resources: Suddenly, light shines down on the forest floor, or nutrients from ashes are released into the soil. This was experimentally demonstrated in the 1960s, when some forests on the Hubbard Brook watershed in New Hampshire were clearcut. A flush of nutrients came out in the water that drained from the clear-cut slopes. To the organisms that can use this flush of resources, a disturbance is positive. Many of these organisms have rapid life cycles and population growth rates that allow them to capitalize on the briefly available resources. After plants begin to grow in the disturbed area and animals return, the resources are again locked up within the tissues of organisms. As forests grew back on the Hubbard Brook watershed, the flush of nutrients at the bottom of the slope decreased. Within decades, forests had grown back, and the runoff of nutrients was no greater than that of adjacent intact slopes. Many species of organisms depend on periodic disturbances and cannot survive in ecological communities that do not experience them. It is even questionable whether ecological communities could persist without at least small-scale disturbances, since there are no communities that do not experience them. It is clear that disturbances enhance biodiversity, and the management of disturbances is an important part of the work of people who maintain the healthy function of ecosystems. In the old days

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198 disturbances, ecological  198 of Smokey the Bear, foresters put out every fire they could; now they spend as much time conducting “controlled burns” as they do fighting wildfires. Disturbances can be placed roughly in two categories: those that remove the soil, and those that leave the soil largely intact. When a disturbance, such as a volcanic eruption or a landslide, removes the soil, the plants that move into the disturbed area must build the soil up before the ecosystem can recover. If a disturbance, such as a storm or a fire, leaves the soil in place, many plants can move right in and begin to grow. In fact, many seeds that are already in the soil can simply sprout. The plants that grow after a disturbance do not all grow at the same time or the same rate. Some plants grow faster and dominate the habitat sooner, while others grow more slowly and dominate the habitat later. The result is a series of stages, known as ecological succession, by which the habitat recovers. Even the smallest disturbances can release resources from the dominant plant species and make

first entry them available for other plant species. The grasses of the shortgrass prairie of the western plains of North America (itself dependent on fire; see below) form a thick sod of underground stems and fibrous roots that few seedlings can penetrate. Even fires do not disturb this sod, but bison and prairie dogs disrupt the sod. Bison scratch their parasites by rolling around in the grass, tearing it up and creating “buffalo wallows.” New seedlings of grass and other plants grow in these roughly circular wallows, called greenups because they produce new leaf area earlier in the spring than do the established grasses. Prairie dogs dig burrows and produce piles of newly turned earth (see figure). The prairie around each burrow may consist almost solely of the grama grasses Bouteloua curtipendula and B. gracilis, while wildflowers such as scarlet globemallow (Sphaeralcea coccinea) can grow only on these mounds. Eroded areas of the shortgrass prairie may be the only place to find wildflowers such as the evening primrose Oenothera caespitosa (see figure on page 199). Fires and other disturbances can, therefore, greatly enhance biodiversity. Animals may also benefit from disturbances. Generations of children have learned from the Walt Disney movie Bambi that hunters and fires are evil. Conservationists have called this the Bambi syndrome. The postfire regrowth, however, can produce a bounty of rich food for grazing and browsing mammals that would find little to eat in the middle of an old forest. Fires and other disturbances can also enhance animal biodiversity. The extent to which disturbances enhance the diversity of fungi and microbes has not been extensively investigated.

Ecological Communities that Depend upon Disturbance

Prairie dogs and bison create disturbed areas in grasslands, such as in the badlands of South Dakota. Prairie dogs dig burrows and produce mounds, while bison graze, trample, and roll in the dirt. The disturbed areas may have higher levels of soil nutrients.  (Stanley A. Rice)

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It is probable that nearly every terrestrial benefits from occasional disturbances such as fires, which clear away dead wood, release nutrients, and allow sunlight to reach the ground. Some ecological communities, however, would not even exist without recurring disturbances (usually fire) to which their species have adapted but which other species cannot tolerate. The disturbances prevent ecological succession and maintain a fire-tolerant set of species. Examples include the following. Grasslands. The grasslands (also known as prairies and steppes) of the world could not exist without periodic fires. An ocean of grassland, the tallgrass prairie, once covered major portions of Minnesota, Iowa, Illinois, the eastern portions of North and South Dakota, Nebraska, and Kansas and extended down into Oklahoma and Texas. The tallgrass prairie received enough rainfall that many species of

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disturbances, ecological  199

In grasslands, most wildflowers grow in eroded or otherwise disturbed areas, where the thick grass sod has been broken. This is Oenothera caespitosa in the badlands of South Dakota.  (Stanley A. Rice)

forest trees, such as oaks, could have easily grown there. Tree seeds continually germinated near the edges of the tallgrass prairie, but frequent fires killed many of the germinating saplings. The saplings that survived, such as those of bur oak (Quercus macrocarpa), grew into small shrubs rather than tall trees. The fires did not harm the grasses, which are perennials and have underground buds and whose leaves grow from the bases. After a fire, the grasses would simply resprout. This growth form allowed grasses to flourish not only after fires but in response to grazing animals. The nongrass wildflowers, called forbs, were also perennials and could sprout after fires. Shortgrass (semiarid) prairies, such as the western prairies of Colorado, Wyoming, and the western Dakotas, do not have enough moisture for trees to grow. They do, however, have enough moisture to support cool desert shrubs such as sagebrush, yet sagebrush does not dominate these grasslands, largely because of fire. Fire kills sagebrush and other shrubs but not the grasses. The steppes of central Asia experience a similar cycle of renewal by fire. Fire actually benefits the grasses and forbs of the prairies. The plants die back to the ground each

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winter, then sprout in the spring. After a few years, dead stems and leaves have built up a thick layer that not only shades the ground but also ties up the nutrients. Fire transforms dead litter, with trapped minerals, into fertilizing ash. The sun penetrates to the soil surface, now dark with ash, and warms it more quickly in the spring. Grasses and forbs grow profusely after a fire if it occurs during early spring or late fall. Fires are unlikely to occur at other times, when the grassland has wet green foliage. Prairies, especially those with tall grass, have deep, rich soil. Nearly all the North American tallgrass prairies have been converted to prime agricultural land. Very few of these grasslands now remain, most of them along railroad tracks or cemeteries that were established before agriculture. Preserving these prairies is therefore very important. Because it keeps the trees and shrubs out, fire is a necessary management tool for maintaining prairies. Fall and spring are the best times for controlled burns, as the prairies are not filled with green blades of grass, but these are also the times when the wind can be strongest and fires can get out of control. Chaparral. Found mostly in California, chaparral habitats consist of fire-adapted shrubs. After fire, the shrubs resprout either from their roots or from seeds. If several decades pass without fire, the chaparral shrubs have more dead than living stems, and the litter layer beneath them is deep and crisp in the hot, dry summers. One can even smell volatile combustible chemicals produced by the shrubs themselves. Fire is inevitable. After the fire, not only do the shrubs grow back, but many wildflowers as well, whose seeds have lain dormant in the soil since the previous chaparral fire. Many other shrublands, such as the matorral of Chile and the fynbos of South Africa, also depend on a fire cycle. Serotinous pine forests. There are certain pine forests in coastal California mountains that rely on a fire cycle. They are called closed-cone pines because their cones do not open as soon as they become mature. The seeds usually remain sealed inside until a fire bakes them open. Their cones are serotinous, that is, hardened. Then, after the fire, the seeds fall on the ground and germinate into a thick regrowth of pine seedlings. One example is the forest of bishop pines (Pinus muricata) in the Purísima Hills near Lompoc, California. A fire destroyed the forest in 1995. Before the end of the summer, the ground beneath standing black trunks was covered with almost nothing but pine seedlings (see figure on page 200). Beneficial fungi help the pines grow rapidly in soil that was fertilized by the ashes. By 2002, some of the new pine trees were already producing cones. Often, these forests have no other dominant tree species (see table on page 201). Older cones on some

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200 disturbances, ecological  200

first entry woods, box elders, and willows, whose seedlings begin their growth in sunny, wet conditions. These conditions are created by floods that wash away the overstory of trees in part of the floodplain and open up a sunny space in which the seedlings can grow. These seedlings do not grow well in shade and therefore do not establish well in places that have not flooded.

Disturbances and Conservation

Some pines, such as these bishop pines (Pinus muricata) in the Purísima Hills of coastal California, open their cones only after a fire has destroyed the adult trees. A thick growth of pine seedlings springs up after the fire.  (Stanley A. Rice)

individuals of these species eventually open and drop their seeds even if a fire does not occur. Many pine forests may not absolutely require a fire cycle for reproduction, but the fires strongly enhance regeneration. Young lodgepole pines (Pinus contorta) in California and in the Rocky Mountains often have cones that open without fire, whereas older trees often have cones that will not open unless they are burned. The populations of pitch pines (P. rigida) of the pine barrens in New Jersey also consist of a mixture of closed-cone and open-cone trees. The cones of ponderosa pines (P. ponderosa) in western North America do not need fire to open, nor do their seeds need to grow on burned soil. However, fires clear out openings in which pine seedlings can grow much more readily than in the shade of trees in an undisturbed forest. Floodplain and streamside habitats. Fire is the most common, but by no means the only, type of disturbance that determines the species composition of wild habitats. Riparian (riverside) forests consist of tree species, such as sycamores, cotton-

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To most people, disturbances (particularly fire) are nothing more than disasters that need to be stopped. When wildfires, fanned by hot, dry Santa Ana winds, make the bushes of the California chaparral explode into flame in a rapidly advancing front, firefighters work around the clock to stop this natural disaster. Humans want to make the natural world “behave itself.” They do not want the fire to burn the houses of people who insist on living in the chaparral in defiance of the natural fire cycle. In such circumstances, total suppression of fires is expected. It is, however, impossible. When fires do not burn in western forests or chaparral, dead timber builds up. When there are no small fires, the risk of large fires increases. When fires begin as a result of lightning or arson, they are much larger and more damaging than they would otherwise have been. Forest managers often clear some areas as an artificial substitute for fires. They also use controlled burns, small fires deliberately set, to reduce the danger of larger fires. Rarely, these fires get out of control. The widespread practice of fire suppression during the 20th century has dramatically altered the North American landscape. Almost all the tallgrass prairies have been destroyed by agriculture and the growth of cities and suburbs. However, even if this had not occurred, fire suppression would have diminished the prairie and allowed forests to spread. The area of the shortgrass prairie is diminishing, and ponderosa pine woodland and sagebrush are spreading. In large areas of the central United States, eastern red cedar (Juniperus virginiana), formerly controlled by natural fires, is spreading. Although it is a native species, it has assumed the role of an invasive. In the Arbuckle Mountains of central Oklahoma, native forests of post oaks (Quercus stellata) were cut down, and the land was used for pasture. Fire suppression has subsequently allowed Ashe junipers (Juniperus ashei) to cover these mountains. Both species of junipers cast deep shade that prevents the successful regeneration of the oak forests. (Besides all this, the Ashe juniper is a major source of allergenic pollen.) Woodlands of oaks, which can partially tolerate fires, have been replaced by forests of trees that thrive in the

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disturbances, ecological  201 Examples of Pine Species that Depend on a Fire Cycle for Persistence Scientific Name

Common Name

Location

Pinus coulteri

Digger pine

Coastal California

Pinus muricata

Bishop pine

Coastal California

Pinus pungens

Table Mountain pine

Eastern North America

Pinus radiata

Monterey pine

Coastal California

Pinus torreyi

Torrey pine

Coastal California

Pinus banksiana

Jack pine

Eastern North America

Pinus contorta

Lodgepole pine

California, Rockies

Pinus rigida

Pitch pine

Eastern North America

Usually require fire for seed release

Partial seed release without fire

absence of fire, such as maples, throughout the eastern deciduous forests. Native American tribes frequently set fires to forests and grasslands, thus encouraging the regeneration of prairie and woodland edge plant species, which they, and the animals they hunted, preferred. Fires cleared away much forest undergrowth. The decimation of Native populations, first by European diseases and then by American conquest, effectively ended both the natural and the Native American fire cycles. American explorers assumed that the thick undergrowth of the forests was natural, rather than an artifact of the collapse of the Native human inhabitants. Fire suppression has not only altered the species composition but the internal climatic conditions of American forests. A continuous shaded canopy retains moisture more readily than an open woodland of separate trees. Moreover, the trees that grow in the conditions of greater moisture (mesic conditions) produce leaves that decompose more readily. Fires, which formerly burned the dry, well-aerated leaf litter, cannot readily spread through leaf litter that is dense and thick. This process, which has been called mesophication, has contributed to the replacement of oaks by maples. It has also caused an understory of mesic oaks, such as Quercus shumardi, to grow up beneath and begin to replace the overstory of fire-tolerant oaks, such as the post oak Quercus stellata, in many locations. It is not possible to find an “original” natural habitat anywhere. All the natural habitats of Earth have shifted their locations during just the past

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few thousand years. Sometimes this has been from human activity; sometimes it has been from fires or other natural disturbances. The most important set of disturbances has been the advance and retreat of glaciers during and after the most recent ice age. When Henry Wadsworth Longfellow wrote “This is the forest primeval” in his epic poem Evangeline, he was describing an Acadian forest that had not been there when glaciers covered the land a few thousand years earlier. The entire surface of Earth is covered with plants that are always shifting locations in response to changes in climate, to disasters, and, more recently, to human disturbances. Disturbance appears to play an important role in maintaining even the tropical rain forests. These rain forests experienced drought during the ice ages that brought cold conditions to the northern latitudes. Natural habitats of plants and animals are not fragile crystals that can be easily shattered by one human error or stroke of natural bad luck. They form a web of ecological interactions and consist of a great diversity of species that actually make them strong, not fragile, and able to adjust to fluctuating and sometimes disastrous circumstances. To preserve natural habitats, it is necessary to safeguard their processes. We cannot preserve them, timeless and immobile like a painting. Protected areas must be allowed to undergo natural changes, including disturbances. It is also necessary to protect the species of plants and animals that grow in disturbed areas and allow recovery from these disturbances. See also deserts, cool; grasslands and savannas; invasive species; shrublands; succession, ecological.

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202 DNA studies of biodiversity  202 Further Reading Barbour, Michael G., et al. “Fire.” Chapter 16 in Terrestrial Plant Ecology. Menlo Park, Calif.: Addison Wesley Benjamin Cummings, 1999. Botkin, Daniel B. Discordant Harmonies: A New Ecology for the Twenty-first Century. New York: Oxford University Press, 1990. Cartmill, M. “The Bambi syndrome.” Natural History (June 1993): 6–12. Grogan, P., et al. “Below-ground ectomycorrhizal community structure in a recently burned bishop pine forest.” Journal of Ecology 88 (2000): 1,051–1,062. Heckenberger, Michael J., et al. “Pre-Columbian urbanism, anthropogenic landscapes, and the future of the Amazon.” Science 321 (2008): 1,214–1,217. Summarized by Mann, Charles C. “Ancient earthmovers of the Amazon.” Science 321 (2008): 1,148–1,152. Keeley, Jon E. “Demographic structure of California chaparral in the long-term absence of fire.” Journal of Vegetation Science 3 (1992): 79–90. ———, and C. D. Fotheringam. “Smoke-induced seed germination in Californian chaparral.” Science 276 (1997): 1,248–1,250. Likens, Gene E., et al. “Effects of forest cutting and herbicide treatment on nutrient budgets in the Hubbard Brook watershed-ecosystem.” Ecological Monographs 40 (1970): 23–47. Nowacki, Gregory J., and Marc D. Abrams. “The demise of fire and the ‘mesophication’ of forests in the eastern United States.” BioScience 58 (2008): 123–138. Rice, Stanley A. “Plants heal the landscape.” Ch. 9 in Green Planet: How Plants Keep the Earth Alive. Piscataway, N.J.: Rutgers University Press, 2009. Thomas, Peter, and Rob McAlpine. Fire in the Forest. New York: Oxford University Press, 2010. West, Neil E. “Intermountain deserts, shrub steppes, and woodlands.” Chapter 7 in Barbour, Michael G., and William Dwight Billings, eds. North American Terrestrial Vegetation. New York: Cambridge University Press, 1988. Wheelwright, Jeff. “Fire in the sky: Why America’s ecological treasures sometimes just need to burn.” Discover (June 2006): 50–57. Willis, K. J., and H. J. B. Birks. “What is natural? The need for a long-term perspective in biodiversity conservation.” Science 314 (2006): 1,261–1,265.

DNA studies of biodiversity  DNA is the

molecule, found in every cell, that encodes an organism’s genetic information (genes). Most cells have noncoding DNA in addition to genes. Mutations in the DNA accumulate over time and alter the sequence of bases in the DNA. Usually, more mutations accumulate in noncoding DNA than in genes because natural selection may eliminate organisms

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first entry that have deleterious mutations in their genes. The result of the accumulation of mutations is that each species has a recognizable set of base sequences. In theory, the species of any organism could be determined by identifying these base sequences. It is much easier to identify a species of multicellular organisms by its physical characteristics than by its genes, because genetic identification involves extraction and analysis of DNA, which takes longer and is expensive. However, if genetic identification of individual organisms could be made quick and inexpensive, it would solve several problems in field work on biodiversity, such as the following. ●●

●●

●●

It often takes a well-trained expert to distinguish among closely related species. To identify all the species in a habitat, the expertise of several scientists is needed, since each specializes on a certain set of organisms. The number of habitats that can be studied is thus limited by the number of available experts. Some organisms cannot readily be identified by physical characteristics—most notably, bacteria. Organisms often cannot be identified unless they are at a certain stage of their life cycle. Many plant species are difficult to identify when they are not flowering, and fungi are often indistinguishable unless they are undergoing sexual reproduction.

New techniques offer the promise of rapid genetic identification of organisms. It is not necessary to analyze the base sequence of all, or even of very many, genes in order to identify a species. For animals, there is enough variation in the cytochrome oxidase I gene (coxI) to allow identification in most cases. For fungi, an internal transcribed spacer (ITS), which is part of the noncoding DNA, can be used. For plants, two genes are used: Neither the large subunit of the ribulose bisphosphate carboxylase gene (rbcL) nor the megakaryocyte-associated tyrosine kinase gene (matK) may be sufficient by themselves to identify a plant species, but when used together, they may work very well. Furthermore, quick and inexpensive ways of identifying the genetic variants of these genes are available and could conceivably be packaged for field use. A researcher would need only to know how to use the kit; the information could be compared with an online database from the field. Currently, the equipment is expensive, but once it is in place, the newest equipment can identify a specimen for as little as $2. This approach, while imperfect, is quite reliable. In a 2006 study, it had a 98 percent success rate of distinguishing among 521 species of tropical butter-

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DNA studies of biodiversity  203 flies and moths. The two plant genes allow the species of a plant to be identified correctly 72 percent of the time; if the comparison is limited to plant species that are known to occur locally, identification is correct nearly 100 percent of the time for seed plants. For seedless plants, identification is a bit less accurate. The rbcL and matK genes are found in chloroplasts, while the coxI gene is found in mitochondria, both of which are inherited only from the female parent (seeds and eggs). As a result, hybrid organisms may not be recognized. Still, these sources of error are much less than what normally happens with mistaken identifications based on appearance. There will probably always be a necessity for voucher specimens (a specimen as an example of the species the researcher has claimed to identify) and the supervision of experts, but the experts do not need to do all the work. There is already a huge backlog of unsorted and unidentified field specimens awaiting identification in herbaria and museums around the world; one biologist estimated that, with experts working alone, it would take 50,000 years to identify all of them. In some cases, genetic techniques have allowed new species to be identified. Organisms that had been assumed to be a single species may be several species, indistinguishable even by experts. This is especially the case with certain insects, in which the insects that have Wolbachia bacteria in their cells cannot interbreed with those that do not, resulting in a speciation event. On the other hand, these techniques may identify genetic variation within species as species-level differences, thus inflating the number of species that are identified. Sometimes, scientists gather DNA specimens from entire ecological communities and then analyze it to determine the number of species the sample represents. This approach, known as metagenomics, has been especially useful in sampling microbial communities in the soil and in the oceans. It has also been used to estimate the diversity of multicellular organisms. In 2009, some scientists drove a vehicle for several hundred miles in the eastern United States and collected DNA from the bumper of the vehicle as an estimate of species diversity along the route. Besides finding bacteria, the researchers also collected insect DNA in this manner. Only 8 percent of the DNA fragments matched those of known sequences, suggesting that even in well-studied regions there are many unknown species. The genetic approach has been called the “barcode of life,” since the computerized sequence of bases looks like a barcode of colored bars, each color representing the base A, C, T, or G. The Consortium for the Barcode of Life (CBOL) is a scientific organization that is advancing the development and appli-

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cation of these techniques. The name “barcode of life” is also meant to reflect the same kind of ease of species identification as supermarket barcodes allow for item identification, pricing, and inventory. If the experts do not have to do all of the work, more habitats can be sampled more frequently, allowing not only more comprehensive biodiversity studies but the monitoring of changes in biodiversity over time. One researcher, the botanist Vincent Savolainen, raised the possibility that genetic barcoding may be “Star Trek’s tricorder coming to reality.” This is, at present, an excessive expectation, but barcoding may prove revolutionary in studies of biodiversity. See also natural selection. Further Reading Chase, Mark W., and Michael F. Fay. “Barcoding of plants and fungi.” Science 325 (2009): 682–683. ———, et al. “Land plants and DNA barcodes: Short-term and long-term goals.” Philosophical Transactions of the Royal Society of London Biology 360 (2005): 1,889–1,895. Consortium for the Barcode of Life, Smithsonian Institution. “What is CBOL?” Available online. URL: http:// www.barcoding.si.edu. Accessed August 24, 2009. Hajibabaei, Mehrdad, et al. “DNA barbodes distinguish species of tropical Lepidoptera.” Proceedings of the National Academy of Sciences USA 103 (2006): 968–971. Hebert, Paul D. N., et al. “Ten species in one: DNA barcoding reveals cryptic species in the neotropical skipper butterfly Astraptes fulgerator.” Proceedings of the National Academy of Sciences USA 101 (2004): 14,812–14,817. Jones, Matthew B., et al. “The new bioinformatics: Integrating ecological data from the gene to the biosphere.” Annual Review of Ecology, Evolution, and Systematics 37 (2006): 519–544. Kress, W. John, et al. “Use of DNA barcodes to identify flowering plants.” Proceedings of the National Academy of Sciences USA 102 (2005): 8,369–8,374. Lahaye, Renaud, et al. “DNA barcoding the floras of biodiversity hot spots.” Proceedings of the National Academy of Sciences USA 105 (2008): 2,923–2,928. Ratnasingham, Sujeevan, and Paul D. N. Hebert. “Barcoding of Life Data System.” Available online. URL: http:// www.barcodinglife.org. Accessed August 10, 2011. Savolainen, Vincent, et al. “Towards writing the encyclopaedia of life: An introduction to DNA barcoding.” Philosophical Transcactions of the Royal Society of London Biology 360 (2005): 1,805–1,811. Smith, M. Alex, et al. “DNA barcodes affirm that 16 species of apparently generalist tropical parasitoid flies (Diptera, Tachinidae) are not all generalists.” Proceedings of the National Academy of Sciences USA 104 (2007): 4,967–4,972.

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204 DNA studies of biodiversity  204 Song, Hojun, et al. “Many species in one: DNA barcoding overestimates the number of species when nuclear mitochondrial pseudogenes are coamplified.” Proceedings of the National Academy of Sciences USA 105 (2008): 13,486–13,491. Spooner, David M. “DNA barcoding will frequently fail in complicated groups: An example in wild

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first entry potatoes.” American Journal of Botany 96 (2009): 1,177–1,189. Venter, J. Craig, et al. “Environmental genome shotgun sequencing of the Sargasso Sea.” Science 304 (2004): 66–74.

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E ecology  ecology is the study of the relationships

ate. Some of the infrared photons are absorbed by greenhouse gases such as carbon dioxide, methane, and water vapor, with the result that high concentrations of these gases can cause the atmosphere to become warmer. this is the source of the greenhouse effect and is the reason that the earth was much warmer in the past than it is today. Methane reacts with oxygen in the atmosphere, producing carbon dioxide. Plants remove carbon dioxide from the air. in this way, photosynthesis prevents an excessive greenhouse effect from occurring. in fact, excessive photosynthesis may have been a contributing factor to worldwide glaciations that occurred during Precambrian time. B. Chemical energy in organisms. all organisms need chemical energy to build the complex molecules that make up their bodies and to run their metabolic reactions, which they use for the uptake of molecules, for growth, for movement, and for reproduction. Plants absorb photons of sunlight and transfer them to the potential energy of chemical bonds in sugar molecules. From these sugar molecules, plants make all of their other molecules. animals obtain chemical energy by eating plants or by eating other animals that have eaten plants. When plants and animals die, decomposers obtain chemical energy from them. the result is the food chain or food web. the evolution of every organism has been strongly influenced by its place in the food web. Since only 10 percent of the food energy is transferred from one step in the food chain to the next, the total weight of photosynthetic organisms is usually 10 times as great as the total weight of herbivorous animals, which is 10 times as great as the total weight of carnivorous animals. Since 100 calories of sugar in plants can support only 1 calorie of

between organisms and their living and nonliving environments. ecology can be divided broadly into two areas: the relationship between an organism and its nonliving environment (autecology, from Greek auto-, meaning self) and the relationship between an organism and other organisms (synecology, from Greek syn-, meaning with).

auTEColoGy i. Energy balance of the Earth and organisms. every organism must maintain the proper balance of heat and chemical energy. an organism must remain within a relatively narrow range of temperature if it is to survive and must obtain energy for its metabolism. a. Energy balance of the Earth. the surface of the earth obtains almost all of its energy in the form of photons from the Sun. the clouds, ice, and light-colored rocks of the earth reflect some of the sunlight, called albedo, back into outer space. albedo does not increase the temperature of the earth. the darker rocks, water, and organisms of the earth absorb sunshine. the sunshine increases the temperature of the earth and all its surface components, which results from increased movement (kinetic energy) of its molecules. the earth cannot conduct kinetic energy into outer space. the only way in which the earth can cool off is to radiate low-energy infrared photons into outer space. the Sun shines visible photons on one side of the earth; invisible photons radiate outwards in all directions from the earth. Over time, the input and output of photons to and from the earth is in balance. the average temperature of the earth can temporarily fluctu205

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206 ecology  206 carnivore, carnivores are often rare and have evolved adaptations that allow them to search for and pursue prey over a wide area. C. Energy balance of organisms.  Organisms obtain some of their warmth from sunshine and the warm air around them and the rest from their food. Organisms must also get rid of energy, thus maintaining an energy balance. The energy that originally entered the organisms as photons or as food can be lost in three ways. First, organisms can radiate infrared photons. Warm-blooded animals radiate more infrared energy than do cold-blooded animals, plants, and their surroundings. Second, organisms can conduct kinetic energy into the air or water around them. Third, plants and animals on dry land can evaporate water. A great deal of energy is required to evaporate water, therefore evaporation (transpiration from plants, perspiration from animals) is a very efficient cooling mechanism. The evolution of each species has been influenced by the necessity of maintaining energy balance. For example, bushes in deserts have evolved small leaves that allow them to disperse more of their heat load in the form of kinetic energy rather than the evaporation of water, which is rare in their habitats. At the same time, these bushes have often evolved deep roots, which maximize the amount of water they can obtain. Plants and animals from separate evolutionary lineages have often evolved similar adaptations to these climatic conditions. Animals need to increase their energy loss in hot environments and restrict it in cold environments. Warm-blooded animals have evolved thick layers of hair or fat to insulate them in cold environments. Hibernation is an evolutionary adaptation that allows animals to avoid excessive energy loss during winter. The temperature and rainfall patterns of different parts of the Earth are influenced by the movements of the Earth, as well as the arrangement of the continents. Before the Pleistocene epoch, oceanic currents carried warm water into North Polar regions, making them much warmer than they are today. The movement of continents subsequently closed off some of this circulation, causing the North Polar region to become permanently cold, and beginning a cycle of ice ages. II. Obtaining matter.  Organisms not only need energy but also need matter. Photosynthesis removes carbon dioxide gas from the air or water and makes sugar from it. Animals and decomposers obtain matter from the food chain at the same time and from the same sources where they obtain energy. All organisms, including plants, release carbon dioxide gas back into the air or water. Organisms also need nitrogen and minerals such as phosphorus, potassium, and calcium. Plants obtain them mostly

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first entry from the soil by absorbing inorganic chemicals with their roots. Plants store some of these minerals and use others in the construction of their large organic molecules. Animals and decomposers obtain minerals from their food. One corollary to the eternal cycling of matter is that nothing ever goes away. Molecules may change form, as when exposure to oxygen causes an organic toxin to break down into harmless components. Some toxins are persistent, such as the slowly degrading pesticide DDT or the immortal element mercury. Humans often think that they can “throw things away” and forget about them, but one of the major slogans of ecology is “There is no such place as away.” This way of thinking was very evident during the 2010 Gulf oil spill. BP, with the guidance and permission of the federal government, used tons of dispersant chemicals (themselves of undetermined toxicity) to break the oil globules into invisibly small particles. They correctly assumed that people would not be concerned about petroleum toxins that they could not see. Just as the laws of nature dictate that one cannot get something for nothing, they also dictate that one cannot get nothing from something.

Synecology I. Interactions within populations. A population is all of the individuals of a species that interact. Populations can grow exponentially because of the reproduction of the individuals that make it up. Species have evolved different reproductive systems that allow individuals to produce offspring successfully and disperse them into new locations. Populations also contain genetic variability, which is essential for natural selection. The fitness of an individual organism is its reproductive success relative to the other members of the population. Individuals compete with one another not only for resources such as food and territory but also for opportunities to mate, resulting in sexual selection. Different populations in a species can become new species. Practically every aspect of evolution is influenced by the synecology of populations. II. Interactions between species. Evolution has produced millions of species, each having complex interactions with many others. Species, just like individuals within species, can compete with one another. Plant species have evolved different ways of protecting themselves from herbivores, including thousands of kinds of toxic chemicals, and herbivores have evolved ways of getting around the plant defenses. Prey animals have evolved many ways of protecting themselves from predators, and predators have evolved many ways of finding and eating the prey. Many animals obtain their food by pollinat-

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ecosystems  207 ing the plants that have made use of those animals to transport their pollen. Many species have evolved very close relationships, called symbioses, in which the other species is the most important environmental factor. Often, one species benefits but the other does not (parasitism), while in others one species benefits while the other is unaffected (commensalism). In many cases, symbioses have evolved toward the mutual benefit of both species (mutualism). Symbioses result from coevolution. In some cases, one species has evolved such a dependence on another that its individuality has been lost and the two have fused into one (symbiogenesis). III. Ecological communities. The total of all the interspecific interactions in a location is the ecological community. This is the context within which all evolutionary change occurs. Evolution has produced a great diversity of species within each community (biodiversity). Biodiversity results from a balance between speciation and extinction. The movements of continents not only influence the climate, as explained above, but also separate species and bring species together, allowing new interactions to occur and new biodiversity to evolve. When new islands emerge from the ocean, new species quickly evolve. Disturbances such as fire and storm occur within ecological communities, which are disastrous to some individuals but create openings that can be colonized by others. Species diversity has been much enhanced by the evolution of species that specialize in disturbed areas. Individuals within species grow first and rapidly in disturbed areas but are usually later replaced by individuals in species that grow more slowly, a process known as ecological succession. Many human activities create disturbances. The disturbances created by humans, however, may be occurring more rapidly than ecological communities or the evolutionary process can handle, with the result that human activity may now be causing the sixth of the Earth’s great mass extinctions. Because all the species in ecological communities interact, forming a complex network of effects, it is very difficult to predict the effects of a single ecological event. One cannot assume that pesticides will simply kill pests and leave everything else in the ecological community unaltered. The pesticides may have unintended victims, such as predators, with the paradoxical result that the pest populations may actually increase (a process known as resurgence). The toxins may concentrate in the food chain, a process known as biomagnification. This is the reason for the other major slogan of ecology, “You can’t do just one thing.” IV. Ecosystems. An ecosystem incorporates the ecological community with the flow of energy and cycling of matter into a single system. Ecosys-

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tem ecology ties together autecology and synecology by considering both organisms and the nonliving environment as components of an interacting system. At every level, from the energy balance of an individual organism to the interactions of all the species in the world, ecology is the exterior context within which all interior functions of organisms must occur and is the setting within which biodiversity develops. See also biogeochemical cycles; biogeography; biomagnification; carbon cycle; coevolution; communities, ecological; disturbances, ecological; ecosystems; greenhouse effect; herbivory; hydrological cycle; mass extinctions; mutualism; nitrogen cycle; parasitism; pollination; population genetics; predation; speciation; succession, ecological; symbiogenesis. Further Reading Barbour, Michael G. and William Dwight Billings, eds. North American Terrestrial Vegetation. New York: Cambridge University Press, 1988. Bazzaz, Fakhri A. Plants in Changing Environments: Linking Physiological, Population, and Community Ecology. New York: Cambridge University Press, 1996. Begon, Michael, Colin R. Townsend, and John L. Harper. Ecology: From Individuals to Ecosystems, 4th ed. Oxford, U.K.: Blackwell, 2006. Hagen, Joel B. An Entangled Bank: The Origins of Ecosystem Ecology. New Brunswick, N. J.: Rutgers University Press, 1992. Harper, John L. “A Darwinian approach to plant ecology.” Journal of Ecology 55 (1967): 247–270. Mayhew, Peter J. Discovering Evolutionary Ecology: Bringing Together Ecology and Evolution. Oxford, U.K.: Oxford University Press, 2006.

ecosystems  Ecosystems are the systems by

which energy flows from the Sun, through the Earth, and into outer space and by which matter cycles on the Earth. Ecosystems can be defined on a large scale (e.g., the entire Earth) or on smaller scales (e.g., the tallgrass prairie ecosystem of North America or the Cedar Lake Bog ecosystem of Minnesota). Within ecosystems, the amount of energy and of each kind of atom or molecule (matter) within each ecosystem compartment and the transfer of energy and matter from one compartment to another are quantified. A compartment may be organisms with a certain ecological function (e.g., producers) or a certain stage of energy flow or cycling of matter (e.g., leaf litter). The concept of ecosystems incorporates ecological communities, which are the living organisms within ecosystems.

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208 ecosystems 208

first entry

flow of ENErGy Sunlight energy is absorbed by all objects, such as oceans and rocks. White, reflective materials, such as ice and snow, absorb very little sunlight. the resulting heat provides energy for the patterns of climate and weather. all of these things could happen on a dead earth and did happen before there was life on earth. the presence of organisms, however, has caused energy to move in a manner strikingly different from the ways in which they would have moved if earth had remained a dead planet. Sunlight energy, trapped by photosynthesis into sugar molecules, passes through several trophic levels, from plant to plant-eater to meat-eater. (“trophic” comes from the Greek word for “eating.”) Green plants and photosynthetic microorganisms that make up the fi rst trophic level are called producers because they alone can capture sunlight energy and store it in molecules. Some of the energy contained within the plants’ molecules flows to the second trophic level, the herbivores, when the herbivores eat the plants. Some of this energy is stored in the molecules that make up the bodies of the herbivores. Some of this energy flows to the third trophic level, the carnivores, when the carnivores eat the herbivores. Some of this energy is stored in the molecules that make up the bodies of the carnivores. Many animals, such as humans, are omnivores, which often eat a roughly equal mixture of plant and animal foods, if available. Herbivores and carnivores are called consumers because they can only consume, not produce, energy from sunlight. consumers that eat just one kind of food are called specialists, while those that eat several or many kinds are called generalists. When an organism dies, the potential energy stored within its

molecules is consumed by scavenger animals and by decomposers such as bacteria and fungi. Species of animals can fulfi ll more than one role; for instance, predatory carnivores sometimes scavenge. Because the links among producers, herbivores, carnivores, and decomposers are complex, the resulting set of interactions is called a food web. less than 10 percent of the energy stored in the body of a plant or an animal is typically stored in the body of the animal that eats it. this was fi rst demonstrated in a food web in cedar lake Bog, Minnesota, studied by ecologist Ray lindeman in 1942 in one of the earliest pieces of food web research. By obtaining samples of plants and animals from the bog, lindeman made estimates of the total number of kilocalories of energy within the molecules of the producers and consumers and what happened to this energy as it flowed through the food web. the following numbers refer to the potential energy within a typical square meter of the bog (a little more than a square yard), during a year (see figure): ●



the growth of green plants (level 1 of the figure) produced more than 1,100 kcal of potential energy each year by photosynthesis. Of this amount, the plants used more than 200 kcal for their own cellular respiration. Herbivorous animals consumed some of the energy stored in the cells of the plants. Since respiration and herbivory removed about 400 of the original 1,100 kcal of energy from the plants, the plants stored about 700 kcal of energy. the herbivores (level 2 of the figure) did not digest all of the food that they ate during

In most ecosystems, such as Cedar Lake Bog, organisms at each level of the food chain collectively contain about one-tenth the energy of the organisms at the level just below them.  (modeled after Raymond Lindeman)

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ecosystems  209

●●

the year. They excreted part of it, and their digestive systems absorbed the remainder. The herbivores used some of the energy for their own cellular respiration. Carnivores such as fishes consumed some of the herbivores and the energy contained within them. Since respiration and predation removed some of the original energy that was consumed by the herbivores, the herbivores stored about 70 kcal of potential energy. The carnivores (level 3 of the figure) did not digest all of the food that they ate. They excreted part of it, and their digestive systems absorbed the remainder. The carnivores used some of the energy for their own cellular respiration. The remaining 13 kcal were stored in the molecules of the carnivores.

The result has been described as an energy pyramid because the energy stored within the molecules of the organisms of one trophic level is usually less than 10 percent as much as the energy stored within the molecules of the organisms in the trophic level on which it feeds. It has also been described as the ten percent law for this reason. In the bog studied by Lindeman, the energy in the molecules of the herbivores is exactly 10 percent of the potential energy in the molecules of the producers, and the energy in the molecules of the carnivores is almost 20 percent of the energy in the molecules of the herbivores. In most food chains, a trophic level stores far less than 10 percent of the energy that is stored in the trophic level below it. The organic molecules produced by plants in an ecosystem are collectively called primary productivity. The ecosystems with the greatest primary productivity are those with the greatest temperature and moisture; the ecosystems with the least primary productivity are cold or dry (see figure on page 210). In general, marine ecosystems have less primary productivity than do terrestrial ecosystems, largely because of the lack of nutrients in the waters of the deep oceans (see table). In general, aquatic and terrestrial ecosystems differ markedly in the flow of energy from one trophic level to another. The primary producers in aquatic systems are primarily phytoplankton, which are a very energy-rich food source. Land plants, unlike phytoplankton, produce a lot of tissue such as wood that allows them to grow large. This tissue is not very nutritious to herbivores. This tissue also takes longer to decompose than do the bodies of phytoplankton organisms. Moreover, some phytoplankton store energy in the form of oil, which allows them to float but which is also very nutritious to herbivores. Therefore aquatic systems have a greater biomass of

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Average Primary Productivity of Some Ecosystems on Earth,   in Kilograms Dry Weight Per   Square Meter Per Year Tropical forests

2,000

Swamp and marsh

2,000

Reefs and estuaries

1,800

Temperate forests

1,250

Savanna

900

Boreal forests

800

Dry woods and shrublands

700

Cultivated land

650

Temperate grasslands

600

Continental shelves

360

Lakes and streams

250

Tundra

140

Open oceans

125

Deserts

40

Total continental

773

Total marine

152

World

333

*To convert to pounds per square foot per year, multiply by 0.2. Note: From Whittaker

herbivores and a lower mass of detritus and decomposers. The rich source of primary production often allows aquatic food chains to have many more levels than terrestrial food chains. A typical aquatic food chain might be phytoplankton to small zooplankton to small arthropods to large arthropods to small fish to large fish to predatory bird, while a typical terrestrial food chain might be grass to rodent to predator. The ten percent law explains how humans can use farmland more efficiently by eating plants than by eating meat from grain-fed animals. The United States is the world’s leading producer of agricultural crops. More than half of the grain raised in the United States and nearly 40 percent of the grain raised in the world are used as livestock feed rather than as human food. David Pimentel, an ecologist at Cornell University, estimated in 1997 that the food produced in the United States could feed 800 million people if it were used to feed people directly, rather than to feed livestock. A strictly vegetarian diet could support about 10 times as many people as could a

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210 ecosystems 210

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This map shows the global pattern of gross primary production (GPP, the total amount of photosynthesis) in grams of carbon per square meter per year. Tropical rain forests have the highest plant productivity.  (Adapted  from Beer, et al.)

strictly carnivorous diet. therefore a larger number of people can receive adequate nutrition if all people ate relatively less meat. americans (who eat more than 90 pounds [40 kg] of beef per capita each year) consume a disproportionate share of scarce food resources. if americans ate less meat, a great deal of food energy might become available to the poor people of the world. it is not necessary to avoid meat totally in order to bring these benefits about. For each 100 kcal of food energy in the livestock feed, the animal uses between 30 and 60 kcal for its own metabolism; between 20 and 30 kcal of the energy is in the animal’s waste; the remainder contributes to the growth of the animal. the efficiency by which feed is converted into livestock growth is higher than the efficiency of herbivores in the wild because the livestock feed has already been processed: the stems and roots of the crop plants have been removed. also, the animals do not need to expend much energy to locate and consume their food, since it is usually provided for them in a trough. consider, also, that humans do not consume very much of the animal’s body, eating primarily the muscles (meat). therefore, in reality, the efficiency of energy in the agricultural food chain from farm to beef on the plate is very low. the efficiency of energy use is even lower when we consider that sunlight energy is not the only

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energy used in producing meat: We also use a huge amount of fossil fuel to plant, fertilize, spray, harvest, and process the grains and to maintain and process the livestock. Raising beef cattle requires 54 kcal of fossil fuel energy for each calorie of protein that reaches the consumer; eggs require 26, pork requires 17, and turkey requires 13. the most energy-efficient meat production is chicken, in which only 4 kcal of fossil fuel energy are needed for each kilocalorie of protein that reaches the consumer. these figures also do not take into consideration the tremendous expenditure of water needed for raising and processing the grains and livestock and the soil erosion that comes from farms and feedlots. these calculations apply only to livestock fed on grain that is raised on mechanized farms. Pastures are usually located on land that is too poor or where water resources are too scarce for raising crops. cattle raised on pastures provide meat that is not at the expense of other food. also, in some cases, animal feed contains waste material that could not be consumed by humans. this practice, while enhancing the energy efficiency of livestock production, can result in public health disasters. For example, the use of leftover animal parts, such as brains, in animal feed has allowed the spread of the prions that cause bovine spongiform encephalopathy (BSe, otherwise known as mad cow disease).

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ecosystems  211 Effects on Earth Surface Heat (in Watts Per Square Meter)   of Different Processes* Process

Difference in Heating

Human-caused Accumulation of carbon dioxide

+1.66

Accumulation of other greenhouse gases

+0.98

Accumulation of ozone: In lower atmosphere

+0.35

In upper atmosphere

-0.05

Water from methane breakdown in upper atmosphere

+0.07

Reflected light: Destruction of natural plant cover

-0.20

Black carbon from pollution

+0.10

Air pollution particles: Reflection of sunlight

-0.50

Enhanced cloud formation

-0.70

Contrails from jets

+0.01

Natural causes Changes in solar brightness

+0.12

Net human effect

+1.60**

*From International Panel on Climate Change. 1 square meter = 10.5 square feet **Because of error estimates, this number cannot be obtained by simple addition of the components.

Eventually the sunlight energy leaves the planet in the form of infrared radiation, which is just light at wavelengths that humans cannot see and which contains less energy than visible light. Haze and clouds can reduce the loss of infrared radiation into space, because water molecules absorb it. This is the reason that a person feels colder and frost is more likely to form under an open rather than under a cloudy sky. Therefore, clouds alter the energy balance of the Earth in two ways: They reflect sunlight, and they absorb infrared radiation. Greenhouse gases can also absorb infrared radiation and cause the atmosphere to become warmer. Human activities have also altered the energy balance of the Earth in important ways. First, humans have altered the surface of the Earth, causing it to reflect more sunlight back into outer space. This reflection is called albedo. This has occurred as a result of the destruction of plant cover, which absorbs much sunlight, leading to bare earth and sand, which reflects much sunlight. Certain kinds

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of air pollution, especially sulfur dioxide, make the atmosphere hazy and cause it to reflect sunlight. These activities tend to cool the Earth. However, the greenhouse effect, in which humans are causing the Earth to become warmer, far outweighs the activities that make it cooler. Carbon dioxide causes the atmosphere to retain heat that would otherwise radiate into outer space. The net effect of human activity upon the energy balance of the Earth has been to cause significant and dangerous global warming (see table). Global warming enhances the evaporation of water and therefore cloud formation. The enhanced cloud cover may itself absorb infrared radiation and enhance global warming.

Cycling of Matter Wind and water carry many kinds of atoms throughout the Earth. The atoms become incorporated into rocks and are released from rocks. All of these things could happen on a dead Earth and did ­happen before

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212 ecosystems  212 there was life on Earth. The presence of organisms, however, has caused atoms to move in a manner strikingly different from the ways in which they would have moved if Earth had remained a dead planet. Carbon, hydrogen, oxygen, nitrogen, and mineral atoms travel throughout the Earth and through the food web. Because the chemical cycles have biological and geological components, they are called biogeochemical cycles. When a green plant carries out photosynthesis or when an animal eats food, they are participating not only in the flow of energy through the Earth but also in the cycling of matter on the Earth. Everything, matter as well as energy, goes somewhere. Some kinds of atoms have an atmospheric component in their biogeochemical cycles. Plants remove carbon dioxide (CO2) from the air. Nitrogen-fixing bacteria, some of them in the soil but most of them in the nodules of roots of many kinds of plants, remove nitrogen gas (N2) from the air spaces in the soil. The other kinds of atoms usually do not have a significant atmospheric component. Plants absorb phosphorus, potassium, calcium, iron, and sulfur atoms through their roots directly from the water solution found in soils. Plants obtain most of their nitrogen from soil solution ammonium and nitrates, rather than from nitrogen-fixing bacteria. Carbon, oxygen, nitrogen, and mineral elements absorbed by plants are incorporated into biological molecules. For example, carbohydrates, proteins, lipids, and nucleic acids all contain carbon and oxygen atoms; proteins and nucleic acids contain, in addition, nitrogen atoms; nucleic acids also have phosphorus atoms, and proteins have sulfur atoms. Organisms use calcium primarily for structural uses: between plant cell walls and within the bones of animals. Plants use potassium, and animals use both sodium and potassium, for water balance of cells. Cells use iron for electron transport in metabolism, and animals use iron in hemoglobin. When organisms die, decomposers release the molecular components: CO2 goes back into the atmosphere, while nitrates, phosphates, calcium, potassium, and other minerals enter the soil water solution. Denitrifying bacteria change some of the nitrogenous minerals back into N2 . Water molecules cycle through the ecosystems of the Earth (the hydrological cycle). Unlike the atoms and molecules of most of the other cycles, water molecules are not chemically altered in the hydrologic cycle. Carbon, oxygen, nitrogen, and minerals cycling through the ecosystem constitute a short-term cycle. Atoms and molecules in short-term cycles transfer from one compartment to another in periods of

xviii+598_Biodiversity_F.indd 212

first entry time as short as a few days to a few centuries. If these atoms and molecules become trapped in sediments, they may become components of rocks, from which they are released only when the rocks erode. These atoms and molecules therefore participate in a long-term cycle. Humans, like other animals, obtain nutrition from many atoms and molecules in food and energy and economically valuable materials from recently produced organic materials such as wood. In these ways, humans participate in shortterm cycles. Humans also obtain materials (such as petroleum and natural ores) for all other activities from biogeochemical cycles. In many cases, human activities deplete resources that have accumulated by the action of long-term cycles. Materials that have accumulated by long-term cycles are called nonrenewable resources because their renewal requires millions of years. Serious economic and ecological problems can be avoided if humans adjust their economic activities to a balanced participation in shortterm cycles, for example by use of renewable energy sources and recycling of material resources. While it is easy enough to weigh organisms and to determine how much carbon or nitrogen is in them and therefore to reconstruct a generalized food web, it may be very difficult to determine the complex pathways by which the carbon or nitrogen moves through the food web. In some cases, investigators trace the movement of stable natural isotopes through food webs. One new method is to introduce nanoparticles into a food web and observe where they go. Most organic matter that moves from one trophic level to another is either released as carbon dioxide or used by decomposers, resulting in a ten percent law for matter not very different from the one for energy. Some organic molecules, however, are persistent, which means they are not metabolized by organisms. Many of them are pollutants produced by humans. These persistent organic pollutants (POPs) therefore undergo biomagnification, in which they are highly concentrated in the tissues of animals near the top of the food chain. No ecosystem, aside from the entire Earth, is discrete from others. Lindeman chose to study a bog because bogs are largely distinct from surrounding ecological communities. Some ecosystems are strongly influenced by others. The deep ocean floors are almost entirely dependent on organic material floating down from the surface. Pond ecosystems may depend strongly on detritus from surrounding forests, and terrestrial animals may depend strongly on prey from the ponds. The boundaries between ecosystems are not, however, arbitrary. Each ecosystem, such as a forest or a pond, consists mostly of a self-reinforcing network of ecological interactions

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ecosystem services  213 among its species. These interactions may help reinforce what might otherwise be an arbitrary boundary. Boreal forest trees, for example, do not merely live in places that are a little warmer than the tundra; the trees absorb sunlight and melt the snow, a process by which the boreal forest makes itself warmer than the nearby tundra. See also biogeochemical cycles; biomagnification; carbon cycle; communities, ecological; ecology; greenhouse effect; nitrogen cycle. Further Reading Arím, Matias, et al. “Food web structure and body size: Trophic position and resource acquisition.” Oikos 119 (2010): 147–153. Becker, D. S., and G. N. Bigham. “Distribution of mercury in the aquatic food web of Onondaga Lake, New York.” Water, Air, and Soil Pollution 80 (1995): 563–571. Beer, Christian, et al. “Terrestrial gross carbon dioxide uptake: Global distribution and covariation with climate.” Science 329 (2010): 834–838. Belgrano, Andrea, et al., eds. Aquatic Food Webs: An Ecosystem Approach. Oxford, U.K.: Oxford University Press, 2005. Cabana, Gilbert, and Joseph B. Rasmussen. “Comparison of aquatic food chains using nitrogen isotopes.” Proceedings of the National Academy of Sciences USA 93 (1996): 10,844–10,847. Doucett, Richard R., et al. “Measuring terrestrial subsidies to aquatic food webs using stable isotopes of hydrogen.” Ecology 88 (2007): 1,587–1,592. Golley, Frank Benjamin. A History of the Ecosystem Concept in Ecology: More Than the Sum of the Parts. New Haven, Conn.: Yale University Press, 1993. Holbrook, R. David, et al. “Trophic transfer of nanoparticles in a simplified invertebrate food web.” Nature Nanotechnology 3 (2008): 352–355. Lindeman, Raymond E. “Trophic-dynamic aspect of ecology.” Ecology 23 (1942): 399–418. Pauly, Daniel, et al. “Fishing down aquatic food chains.” American Scientist 88 (2000): 46–52. Persson, A., et al. “Effects of enrichment on simple aquatic food chains.” American Naturalist 157 (2001): 654–669. Rice, Stanley A. Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Shurin, Jonathan B., et al. “All wet or dried up? Real differences between aquatic and terrestrial food chains.” Proceedings of the Royal Society of London B (Biology) 273 (2006): 1–9. Solomon, Susan, and the Intergovernmental Panel on Climate Change. Climate Change 2007: The Physical Science Basis. Available online. URL: http://www.ipcc.

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ch/publications_and_data/ar4/wg1/en/contents.html. Accessed July 31, 2010. Whittaker, Robert H. Communities and Ecosystems, 2nd ed. New York: Macmillan, 1975.

ecosystem services  The ecosystems of the

Earth provide many services to the human economy, free of charge. This is not their purpose. All of the individuals of each species pursue their own fitness. But as trees (for example) photosynthesize, grow roots, and transpire, they end up doing many things upon which human life and the human economy depend. Nearly everyone has at least a vague understanding that, without the natural world, human life would be impossible, and that humans extract many resources from the living world of nature that have great economic value. The ecosystem services approach differs from this widely accepted view in these major ways: ●●

●●

First, it replaces a vague awareness of the value of nature with actual monetary values. The approach usually taken is to calculate how much it would cost for an ecosystem service, such as the production of oxygen by plants, to be replaced by an industrial process. Second, it does not rely solely on the monetary value of extracted resources (such as the value of the timber in a forest) but on all of the services that the ecosystem provides.

As a result of ecosystem services calculations, it becomes obvious that an intact ecosystem is worth much more, even in strictly monetary terms, than the resources that would come from the destruction of the ecosystem. For example, the ecosystem services of a forest exceed the value of the timber by many orders of magnitude. The results are nearly always astonishing. The calculations apply to wild ecosystems or, in urban areas, reconstructed ecosystems such as parks. Ecosystem services, like ecosystem processes, are interconnected and difficult to isolate from one another. Most of these services result from the growth of plants. This should not be surprising since animals (and to a lesser extent fungi and bacteria) perform metabolic roles similar to those of humans, which are to that extent competitors rather than beneficiaries. In other words, most wild animals receive the same ecosystem services from plants that humans receive. Humans, however, are more dependent on ecosystem services than is any wild animal species,

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214 ecosystem services  214

first entry

“Ecosystem Services: Public or Private Costs?”

S

ervices provided by wild ecosystems provide at least $33 trillion dollars of benefits to the human economy each year. Examples of such ecosystem services are plants putting oxygen into and removing carbon dioxide from the atmosphere; forests controlling floods and allowing rain to percolate into the soil and recharge aquifers; and wild plants not only holding down but building up the soil. In every case, the services provided by intact natural ecosystems (such as forests) vastly overshadow the immediate profit to be gained by extraction of resources (such as timber) from them. One problem with ecosystem services calculations is that they often do not convince narrow corporate interests to treat the natural world as a sustainable rather than as an extractive resource. The numerous benefits of an intact forest have tremendous value to the people who live near the forest but will not increase the profit margin of a timber corporation. To such a corporation, the lumber will always be worth more than the forest. It is governments, to the extent that they reflect

the welfare of the people, that can make the most use of ecosystem services calculations. This is because it is governments that have to clean up the mess from, for example, mudslides and floods following deforestation, after the timber corporation has cut the trees and moved on. One of the few ways in which the corporations can have an economic interest in ecosystem services is if governments hold them liable for the disruption of these services. The Gulf oil spill, following the explosion of the Deepwater Horizon drilling rig on April 19, 2010, was the greatest environmental disaster to that point in American history. Initially, much of the cost was borne by Gulf Coast residents and the United States government, but the government insisted that BP, the company whose contractors operated the rig, establish a $20 billion fund to pay all of the direct environmental costs. BP complied with this demand, and most citizens and politicians of both major political parties agreed that it was fair, except for Representative Joe Barton (Republican of Texas) who considered it to be federal

because humans depend upon a complex economy which, in turn, depends to a greater extent on environmental stability than do the lives of other animal species. Fires burn the aerial portions of plants and chase away the animals; afterward, the plants resprout and the animals return. The same fire will probably cause millions of dollars of damage to humans. Hunters and gatherers had many of the options, such as migrating to a new location, which wild animals have, but which civilized humans, living in a thick landscape of land ownership, do not.

●●

●●

Example of Ecosystem Services Here are some processes of intact wild ecosystems that happen to provide benefits to humans, which would take billions of dollars to provide artificially: ●● ●●

Oxygen production.  Photosynthetic organisms release 17.3 million tons (15.7 million metric tons) of oxygen into the atmosphere each year.

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oppression of the corporation. Without government intervention, almost the entire cost of the oil spill would have been borne by the government and citizens, while BP would have lost only the money it spent on the oil rig itself. Another way in which private corporations may take an interest in ecosystem services is when insurance companies (and the reinsurers that insure them) face the possibility of having to pay for the mess caused by an environmental disaster. It is the insurance companies that are becoming concerned with the effects, already beginning to be felt, of global warming. In the short run, they can refuse to issue policies to people along the Gulf Coast, due to hurricanes, oil spills, and rising sea levels. In the long run, as the effects of global warming become more pervasive and worldwide, insurance corporations cannot refuse coverage to very many more people or else they will have very little business. Moreover, the calculated costs of environmental damage almost never include indirect costs, such as greenhouse effect. The 2010 BP blowout released huge

Carbon dioxide removal.  Photosynthetic organisms absorb about 115 million tons (105 million metric tons) of carbon dioxide from the atmosphere each year. Carbon dioxide is the principal long-term cause of the greenhouse effect. Shade. Trees absorb the heat from sunlight, which they transfer into water vapor. The shade of the trees is therefore cooler than the atmosphere above unshaded land. Though the shade of a tree may not make air-conditioning unnecessary in a small shaded building, it will reduce the amount of air conditioning that is needed. Shade saves millions of dollars of air-conditioning costs in the United States each year. Filtering pollution. Trees reduce the amount of many pollutants in the atmosphere of cities, because the pollutants adhere to leaf surfaces and same leaves neutralize the pollutants.

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ecosystem services  215

amounts of methane into the atmosphere, where it is no longer visible and can be ignored by most people. But methane and the carbon dioxide produced from it contribute substantially to greenhouse gases. Also, the blowout has put pressure on American society to become even more heavily dependent on fossil fuels. At the very time that the oil spill was gushing unabated into the Gulf, most Americans remained in favor of continued oil drilling in the deep water at the edges of the continental shelves. None of these greenhouse-related costs are reflected in the $20 billion escrow account that the government required BP to establish for the cleanup. If the full indirect costs of the greenhouse effect are taken into account for environmental disasters, they would overwhelm all private profits. Such calculations will never happen. And these are only the costs associated with disasters, rather than with the slow, persistent depletion of the functions of wild ecosystems. In a few cases, corporations have made contributions to private conservation organizations. It is safe to say that, aside from such voluntary gifts, almost none of the $33 trillion is balanced by corporations setting aside money for environmental restoration.

●●

●●

●●

●●

Corporations generally do not consider it worthwhile to invest in natural capital— that is, the monetary value of nature. The people who depend directly on natural ecosystems for their survival—for example, tribal farmers who have to supplement their diet with wild game—have essentially no economic power in their countries. It is the poorest people and the poorest countries that will suffer most from environmental depletion and from the greenhouse effect. In the valuation of ecosystem services, as in so many other ways, the environment is a medium through which people transmit altruism, or injustice, to one another. Furthermore, it is routine for politicians to make lofty statements about the kind of world they are leaving for their grandchildren, while assigning a value of essentially zero to the kind of environment in which their grandchildren will live (a process known as future discounting). Most people do not care that future generations will resent the present generation for depleting the ecosystem services of the planet, and even fewer are willing to invest money specifically to make a better world for them. See also ecosystem services; environmental ethics.

Flood prevention. Trees slow down the impact of rainfall that reaches the soil. This has two effects. First, trees help to prevent runoff that would cause flooding and mudslides. Second, the rain is more likely to percolate into the soil if the leaves of trees, shrubs, and grasses slow it down. Groundwater recharge.  Much of the water that percolates into the soil recharges the water supplies in aquifers, which is where most people obtain water. Erosion prevention.  By slowing down the wind and the rain at the soil surface, plants reduce the loss of soil by wind and water erosion. It costs a lot of money to compensate for topsoil loss by applying commercial fertilizers and, in severe cases, compensation cannot be made at all. Pest control. Agricultural pests and the pests that spread human diseases are seldom species that live primarily in the wild. Many

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●●

●●

●●

Further Reading Chaddock, Gail Russell. “With Joe Barton’s BP apology, Republicans’ point lost in oblivion.” Christian Science Monitor, June 18, 2010. Available online. URL: http://www.csmonitor.com/USA/ Politics/The-Vote/2010/0618/WithJoe-Barton-s-BP-apology-Republicanspoints-lost-in-oblivion. Accessed August 7, 2011. Costanza, Robert, et al. “The value of the world’s ecosystem services and natural capital.” Nature 387 (1997): 253–260. Davidson, Eric. You Can’t Eat GNP: Economics as if Ecology Mattered. New York: Basic Books, 2001. Hawken, Paul, Amory Lovins, and L. Hunter Lovins. Natural Capitalism: Creating the Next Industrial Revolution. New York: Hachette, 2008. Rehmeyer, Julie. “ ‘Discounting’ the future cost of climate change.” Science News, May 21, 2010. Available online. URL: http://costingthefuture.org/?p=66. Accessed August 7, 2011. Rice, Stanley A. Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers, 2009. Roodman, David Malin. The Natural Wealth of Nations: Harnessing the Market for the Environment. New York: Norton, 1998.

wild animal species help to control pests. Examples include birds and bats, which collectively consume billions of pest insects, and wasps, which parasitize and kill them. Pollination.  Honeybees (Apis mellifera) carry out much agricultural pollination, but wild ecosystems also provide many pollinators, and honeybees may rely on wild nectar sources during times when agricultural sources are not available. Sources of agricultural germplasm.  Wild relatives of crop plants are important sources of genes that plant breeders can use to produce disease-resistant crop varieties. An entire entry in this encyclopedia explores the value of biodiversity for agriculture. Sources of pharmaceuticals.  Wild plants and animals are important sources for the discovery of pharmaceutical compounds. An entire entry in this encyclopedia explores the value of biodiversity for medicine.

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216 ecosystem services  216

first entry

Monetizing Ecosystem Services Among the difficulties in assigning exact monetary values to ecosystem services are the following. Airconditioning is one of the major uses of electricity in the United States. Shade can help reduce the amount of air-conditioning, but only if the building is small enough to be shaded and the trees are on the south side of the building. In many new subdivisions, the original forests have been cut down and replaced with small saplings that will require decades to grow large enough to cast shade. Many new homes are too large for any but the largest trees to shade them. Most city buildings are too large to benefit from shade, even from rooftop trees. It is also difficult to calculate the flood control capacity of a forest. Many rainfall events are so severe that no forest, however intact, could prevent the flooding that ensues. Nevertheless it is quite clear that, on the average, natural or restored plant cover will reduce air-conditioning costs and flooding damage in most cases.

The value of carbon dioxide absorption is particularly difficult to calculate. Global warming is already having so many different and interacting effects on the human economy that it is difficult to identify, much less quantify and monetize, all of them. When intact ecosystems absorb carbon dioxide from the air, they are helping to reduce the greenhouse effect that would reduce the ability of wild ecosystems to perform the other ecosystem services. Global warming is expected to produce stronger storms in coastal areas, which will often exceed the capacity of a forest to control, and to produce droughts, which will degrade the forests and reduce their ability to control even moderate storms. Many important ecosystem services are almost impossible to monetize but are essential nonetheless. Examples include the psychological, spiritual, cultural, and educational uses of natural ecosystems and their value in scientific research.

Global Ecosystem Services Category

Examples

Atmospheric regulation

Oxygen production

Value (billion dollars per year)* 1,341

Carbon dioxide absorption Ultraviolet absorption by ozone Climate regulation

Regulation of rainfall

Disturbance regulation

Storm protection

684 1,779

Flood control Water regulation

Irrigation

1,115

Water supply

Reservoirs and aquifers

1,692

Erosion control

576

Soil formation

53

Nutrient cycling

Nitrogen fixation

Waste treatment

Detoxification by wetlands

Pollination

17,075 2,277 117

Biological control

Wild predators of insect pests

417

Refugia

Habitats for harvested species

124

Food production

Fish, game, wild fruits, and nuts

Raw materials

Lumber, fuel, fodder

Genetic resources

Agriculture and medicine

Recreation Cultural Total

1,396 721 79 815

Psychological, spiritual, scientific

3,015 33,268

*1997 dollars Note: From Costanza et al.

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Ediacaran organisms  217 The difficulty of making these calculations has not stopped economists from trying. Economist Robert Costanza and colleagues have estimated that the total global value of 17 ecosystem services is $33 trillion (in 1997 U.S. dollars), which is almost double the total global gross domestic product ($18 trillion) (see table on page 216). On a smaller scale, New York City Parks Commissioner Adrian Benepe, using a computer program developed at the University of California, Davis, estimates that the 592,130 trees in New York public areas generate $5.60 in savings for each $1.00 spent to plant and maintain them. The value of ecosystem services is calculated only on the basis of renewable production. Accumulated past production (such as coal and oil) are not counted. However, even oil can be considered an ecosystem service, to a very limited extent. In the Gulf of Mexico, organic material continues to accumulate and, after a long time, is compressed into oil. Of most immediate concern to most people is not so much the value of ecosystem services as the costs that are necessary to mitigate disasters that damage them. It will be a long time before the total costs of the Gulf oil spill of 2010, the biggest environmental disaster in American history, are known. The $20 billion that the federal government required BP to set aside for the cleanup is almost certainly not going to be enough. And this is only for the imperfect cleanup of an ecosystem. See also Essay: “Ecosystem Services: Public or Private Costs?”; biodiversity, resources for agriculture; biodiversity, resources for medicine; biogeochemical cycles; ecosystems; environmental psychology; greenhouse effect. Further Reading Costanza, Robert, et al. “The value of the world’s ecosystem services and natural capital.” Nature 387 (1997): 253–260. Randall, David K. “Maybe only God can make a tree, but only people can put a price on it.” New York Times (April 18, 2007). Available online. URL: http:// www.nytimes.com/2007/04/18/nyregion/18trees. html?pagewanted=print. Accessed May 13, 2011. Rice, Stanley A. Green Planet: How Plants Keep the Earth Alive. New Brunswick, N. J.: Rutgers University Press, 2009.

Ediacaran organisms  The Ediacaran organisms were the first notable diversification of multicellular life on Earth. They lived immediately before the Cambrian period, which began about 540 million years ago. The abundance of multicellular forms after the Cambrian explosion contrasts sharply with

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the relatively few multicellular forms represented by the Ediacarans. The earliest Ediacarans lived about 580 million years ago. These marine organisms may have had a worldwide distribution, as their fossils are found in 24 locations on six continents, including Australia (especially the Ediacara Hills after which they are named), Newfoundland, and Namibia. Reginald Sprigg, an Australian geologist, was investigating mines in the Ediacara Hills in 1946. While eating lunch, he turned over a rock. He was not expecting to find any fossils, since the rocks were Precambrian in age, and at the time no multicellular organisms were known from before the Cambrian explosion. But he saw many leaflike impressions in the rock. He reported his findings at meetings, but they were rejected for publication. Then in 1957, John Mason, a student, found a fossil in England, also of Precambrian age, that closely resembled Sprigg’s Australian fossil. Now that these fossils were being found more than once and in such diverse places, they were taken seriously. Sprigg’s priority as discoverer has been recognized by calling them Ediacaran fossils. Nobody is entirely sure what these organisms were. Some of them bear at least a superficial resemblance to existing kinds of marine invertebrates. For example, Tribrachidium, Arkarua, and Albumares resemble modern echinoderm “sand dollars”; Mawsonites resembles a modern cnidarian sea anemone; Spriggina and Bomakellia resemble the arthropod trilobites that were abundant in oceans until about 250 million years ago; and Charniodiscus and Pteridinium resemble modern sea pens, all of them invertebrate animals known from the Cambrian period. These resemblances are often pointed out because it is reasonable to expect the immediate ancestors of Cambrian animals to have lived during the Ediacaran period. There are numerous puzzling differences between the Ediacaran organisms and the invertebrate animals they resemble. In particular, the Ediacarans are not known to have had legs or mouths. While many invertebrate animals lack legs, none lack mouths. If Ediacarans were animals, how and what did they eat? Another difficulty in identifying Ediacarans as animals related to modern invertebrates is the question of whether the modern phyla of animals were yet in existence. Molecular studies suggest that the diversification of the modern groups of invertebrates had already begun. Precambrian fossils of what are clearly animal embryos and what were probably bilaterally symmetrical animals have been found. These observations suggest that some modern groups of invertebrates were in existence during Ediacaran times.

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218 endangered species  218 Some researchers claim that the Ediacarans had to be animals because they moved. In several examples, Ediacaran fossils are found in groups of four: three depression fossils and one with positive relief. The interpretation given in this case is that the Ediacaran organism flopped around four times, leaving three prints in the bottom of the sea where they lived; the fourth, positive structure is the fossil of the organism itself. However, this does not prove that they moved themselves; they may have been moved by ocean currents. Other researchers believe that the Ediacarans were organisms that are completely unrelated to modern animals; in fact, they may not have been animals at all. Consider, for example, the Spriggina fossil. To human observers it looks like a worm or trilobite with a head. But if an observer turns it upside down he or she may see a seaweedlike structure with a holdfast to anchor it to the bottom of the ocean. Researchers generally accept that animals were present at that time. Fossilized burrows and other trace fossils (evidence of things the organisms did, rather than the organisms themselves) have been found, although some of the burrows may have been caused by single-celled protists rolling through the mud. This does not prove that the Ediacarans were the animals that left the traces. Although red algae are known from 1.2 billion years ago, long before the Ediacaran organisms, the Ediacarans possess no structures that identify them as seaweeds, just as they possess no structures clearly identifying them as animals. Researchers such as paleontologists Dolf Seilacher and Mark McMenamin have suggested that the Ediacarans were actually symbiotic combinations of protist cells, some of which were photosynthetic. Many symbiotic combinations of plantlike and animallike protist cells are known from the modern world, such as Ophrydium, a protist colony that lives underwater. The symbiosis would explain how the Ediacarans obtained food without having mouths: The plantlike cells made food from sunlight. It might even explain why many of these fossils were sometimes found to be filled with sand: They contained sand, as ballast, while alive, which would have been inconvenient for an animal, but perfectly workable for symbiotic bags of cells. Alternatively, these organisms could have lived by absorbing dissolved organic materials. They may even have been large single-celled protists, similar to the modern oceanic xenophyophores. In 1992, Dolf Seilacher proposed that the Ediacaran organisms were a separate kingdom of life, which he called Vendobionta. It is possible that some of the Ediacarans were members of modern invertebrate phyla, while some were not. After all, the resemblance of Charniodis-

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first entry cus to the Cambrian cnidarian Thaumaptilon and to modern sea pens is very close. Sea pens, like many other cnidarians, form symbiotic associations the way many researchers claim the Ediacarans did. Therefore, some Ediacarans may have been cnidarians but also had endosymbiotic algae living in their tissues, just as many coelenterates such as jellyfish and corals do today. One of the major features of the Ediacarans is that they had no hard shells, spines, or other defenses against predators. The implication is that predatory animals had not yet evolved. Once predators evolved, the Ediacarans may have been driven to extinction by them; only the hard-shelled animals or chemically defended seaweeds could survive. It has been suggested that the appearance of the first predators was the stimulus for the Cambrian explosion. Ediacaran organisms were the first to become prominent after prolonged periods of global cooling that have been called Snowball Earth. A long period of Earth history, in which (aside from some seaweeds) most organisms were colonies of single cells (such as stromatolites), came to an end with the global spread of ice on land and over most of the oceans as well. Organisms survived only underneath a few openings in the ice. It was in the rapid and possibly severe period of global warming that followed Snowball Earth that multicellular organisms, first the Ediacarans, then the Cambrian organisms, evolved. See also animals; Cambrian explosion; Cambrian period, biodiversity in. Further Reading Conway Morris, Simon. The Crucible of Creation: The Burgess Shale and the Rise of Animals. New York: Oxford University Press, 1998. McMenamin, Mark A. S. The Garden of Ediacara: Discovering the First Complex Life. New York: Columbia University Press, 1998.

endangered species  Endangered species are species that are at risk of extinction in their natural habitats. Other than the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES), there are few international protections for endangered species or even international standards for what constitutes an endangered species. The International Union for Conservation of Nature (IUCN), an environmental network that brings together more than 1,000 governments and NGOs (nongovernmental organizations), maintains a list of species all over the world that are critically endangered, endangered, extinct in the wild, vulnerable, or near-threatened. IUCN is universally recognized as the international information source about

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endangered species  219 endangered species because of the quality of information it collects and the consistency of standards by which it evaluates this information. Another organization, Earth’s Endangered Creatures, lists 16,547 species as endangered as of mid-2010. In the United States, endangered species can attain legal protection as a result of the Endangered Species Act (ESA) of 1973. Under this law, legal protection can prevent or stop government or private activities that put the species at risk of extinction. Responsibility for listing endangered terrestrial and freshwater species lies with the United States Fish and Wildlife Service (FWS), while responsibility for marine species lies with the National Marine Fisheries Service Office of Protected Resources. Because of the inevitable legal repercussions of restricting economic activity to protect a species, the FWS has established a process for listing a species as endangered or threatened and standards for evaluation of the status of a species. The process begins when FWS staff members prepare a report. FWS staffers do a lot of their own fieldwork, but rely heavily on outside information regarding which species should be listed and for much of the information upon which they base their reports. The outside information comes primarily from state agencies and from universities. Information includes the sizes of the populations, their locations, and the threats that the species is experiencing. According to section 4 of the ESA, in order to be considered endangered or threatened, the species must be at risk because of: ●● ●● ●● ●●

the present or possible destruction or modification of its habitat or range; disease or predation; the inadequacy of existing protection; or other natural or man-made factors affecting the species’ continued existence.

Note that the risk does not have to come from human activity. The report is submitted to a regional supervisor, then to the director of FWS. The director decides if the species should be included in the candidate list. As of August 2011, there were 265 candidate species awaiting evaluation. Each candidate species also receives a priority rating, from 1 to 12, based on “the magnitude and immediacy of threats to it, as well as its taxonomic distinctiveness.” The FWS next needs to periodically review the list to determine if a species should be elevated to protected status, removed from the list, or have its priority rating changed. A summary document of candidate species is made public on the FWS Web site and in the Federal Register. A total of 1,372 species are now listed by the FWS as endangered or threatened (see table).

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Numbers of Endangered   and Threatened Species   Listed by USFWS* Endangered Mammals

Threatened

Total

68

15

83

0

2

2

Reptiles

13

24

37

Amphibians

14

10

24

Fishes

72

67

139

Clams

63

8

71

Snails

24

12

36

Insects

50

10

60

Arachnids

12

0

12

Crustaceans

19

3

22

Birds

76

15

91

Total animals

411

166

577

Conifers and cycads

2

1

3

27

2

29

2

0

2

Flowering plants

614

147

761

Total plants

646

149

795

1,057

315

1,372

Corals

Ferns and allies Lichens

Total *As of August 2011

In order for a species to be listed for protection, there must be a recovery plan that will eventually allow the species to be delisted. A federal status of endangered or threatened is not intended to be permanent. The goal is to protect or restore habitat to a condition that the species is no longer threatened or endangered. The delisting of an endangered species is celebrated as a sign of success, as when the bald eagle was removed from the list in 2006. Even though the federal government had begun the process of delisting the eagle, and mainstream environmentalist groups supported the move, it was a lawsuit from a private landowner that prompted the delisting. It is still illegal to kill bald eagles, which are protected under a special piece of legislation that protects them and golden eagles.

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220 endangered species  220

first entry

The wolf was not as fortunate. Listing the wolf as endangered meant that it was illegal for hunters to kill it. The National Park Service reintroduced wolves to Yellowstone National Park, where they had been eradicated. Wolf populations returned to levels that were not considered dangerously low. When the wolf was delisted in March 2008, Wyoming officials immediately declared nearly the entire state a “free-fire zone.” Some hunters immediately began killing as many wolves as they could. In some cases, they even trespassed on private property (whose landowners did not approve of the hunting) to do so. Within months, nearly one-tenth of the wolves of the Rocky Mountain region had been shot. The hunters claimed that wolves were killing their sheep, which did in fact sometimes happen. But according to research conducted by the United States Department of Agriculture (which manages the national forests), only 1 percent of sheep deaths were caused by wolves, less than the number caused by bears, cougars, or even wild dogs (see table). More than a quarter of the sheep deaths were caused by coyotes, and almost a quarter of them died due to the weather. Then a federal judge put a stop to the hunting of wolves, restoring them to protected status. Just days before leaving office, on January 14, 2009, President George W. Bush once again removed federal protection from wolves. A federal judge restored wolves to the endangered species list in 2010. Another federal judge revoked their protected status in 2011.

Causes of Sheep Deaths,   According to the United States Department of Agriculture* Source of death

Percentage of deaths

Wolves

1

Coyotes

25.3

Weather

22.6

Disease

11

Complications during lambing

9

Other predators

6.5

Old age

5.8

Bear

1.8

Cougar

1.4

Dog

1.1

Other

7

Unknown

7.7

*Data from Chadwick

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The administration of George W. Bush slowed the process of protection for endangered species to a historic low. As of 2004, the Bush administration added an average of 9.5 species a year to the endangered list, compared with 65 a year under President Bill Clinton and 59 a year under President George H. W. Bush. The period from May 2006 to May 2007 was the first time since 1981 that an entire year had passed without a single species being approved for endangered species listing. Even for those that they did list, Bush administration appointees approved only half as much critical habitat as FWS staffers had recommended based upon scientific research. Julie MacDonald, a deputy assistant secretary for Fish and Wildlife appointed in 2004, personally instructed FWS staffers to not find any more species to be at risk of extinction. As a result of these activities, she resigned in 2007. Republican lawmakers, in particular California representative Richard Pombo and Utah representative James V. Hansen, were strongly supportive of strangling the Endangered Species Act. Hansen proposed, in 2002, that all private property, all military bases, and all plant life be excluded from the Endangered Species Act. He predicted that, as a result, “we would, in short order, have a more prosperous and secure nation.” After the election of Barack Obama but before his inauguration, President Bush eliminated the requirement for independent scientific review of the potential environmental impact of federal projects (in particular, leases for oil drilling). The Endangered Species Act has, since its inception, been the law that conservatives have loved to hate, and it will continue to be so. But it remains the only significant process by which endangered species can receive protection. Alternative strategies, such as cloning, have proven to be expensive failures. In 2001, Advanced Cell Technologies, a Massachusetts biotechnology company, successfully cloned a guar, an endangered relative of the domestic cow, by implanting a genetically modified egg cell in a cow. Full of hope, they named the little guar Noah. It quickly died of a bacterial infection. Had the guar survived, what could be done then, if the wild habitat has been destroyed? Habitat preservation, made possible by the ESA, remains the only cost-effective way to rescue endangered species. See also federal government role in conservation (United States). Further Reading BBC News. “Endangered animal clone dies.” Available online. URL: http://news.bbc.co.uk/2/hi/science/ nature/1113719.stm. Accessed May 13, 2011. Brooke, M. de L., et al. “Potential for rat predation to cause decline of the globally threatened Henderson

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endemic species  221 petrel Pterodroma atrata: Evidence from the field, stable isotopes and population modelling.” Endangered Species Research 11 (2010): 47–59. Cart, Julie. “Predator becomes prey in Wyoming.” Los Angeles Times, September 28, 2008. Available online. URL: http://articles.latimes.com/2008/sep/28/nation/ na-wolf28/2. Accessed May 13, 2011. ———. “Endangered Species Act is modified.” Los Angeles Times, December 12, 2008. Available online. URL: http://articles.latimes.com/2008/dec/31/local/me-spe cies31. Accessed May 13, 2011. Chadwick, Douglas H. “Wolf wars.” National Geographic, March 2010, 34–55. Christiansen, F., et al. “Effects of tourist boats on the behaviour of Indo-Pacific bottlenose dolphins off the south coast of Zanzibar.” Endangered Species Research 11 (2010): 91–99. Earth’s Endangered Creatures. “World Endangered Species List.” Available online. URL: http://www.earthsendangered.com/full_list_html.asp. Accessed August 8, 2011. Eilperin, Juliet. “Endangered Species Act’s protections are trimmed.” Washington Post, July 4, 2004: A01. International Union for the Conservation of Nature. “IUCN.” Available online. URL: http://www.iucn.org. Accessed August 8, 2011. Loi, Pasqualino, et al. “Genetic rescue of an endangered mammal by cross-species nuclear transfer using postmortem somatic cells.” Nature Biotechnology 19 (2001): 962–964. Loomis, John B., and Douglas S. White. “Economic benefits of rare and endangered species: Summary and metaanalysis.” Ecological Economics 18 (1996): 197–206. Sherley, R. B., et al. “Spotting the difference: Towards fullyautomated population monitoring of African penguins Spheniscus demersus.” Endangered Species Research 11 (2010): 101–111. Slevin, Peter. “Bald eagle to be taken off endangered list.” Washington Post, December 25, 2006. Available online. URL: http://www.washingtonpost.com/wpdyn/content/article/2006/12/24/AR2006122400666. html. Accessed May 13, 2011. U.S. Fish and Wildlife Service. “Endangered Species Program.” Available online. URL: http://www.fws.gov/ endangered/. Accessed May 13, 2011.

endemic species  Endemic species are species whose entire range is a single, limited locality. They may be locally abundant within that locality but are rare on a regional and global level. Biodiversity hot spots have many endemic species. Many endemic species are endangered because if local populations become extinct there are no others to replace them. There are two main reasons that may cause a species to be endemic. First, the species may have

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evolved only in the one location in which it persists. This is the case with many species that are endemic to geographical islands. Second, the species may have formerly had a wide range but has become extinct everywhere except that one location. This is the case with many species that are endemic to ecological islands on continents. There are many examples in which a disjunct species consists only of endemic subspecies. The seaside alder, Alnus maritima, is a disjunct species that consists only of three endemic subspecies: ssp. maritima, which lives only on the Delmarva Peninsula east of Chesapeake Bay; ssp. georgiensis, which lives in a single swamp in Bartow County, in northwestern Georgia; and ssp. oklahomensis, which lives only in south central Oklahoma, primarily in Johnston County. There are also examples of endemic subspecies of a widespread species. Cervus canadensis, the elk, has populations across North America. One subspecies, ssp. nannodes, the tule elk, is endemic to the marshes of central California and has nearly become extinct as these marshes have been drained and transformed into an agricultural and urban landscape. In 1895, only 28 tule elk survived. Habitat preservation has allowed their numbers to expand to a few thousand.

Geographic Island Endemics Some large islands are actually continental fragments that have remained separate from the larger continents for many millions of years. Madagascar, a large island off the coast of Africa, has a very large number of endemic species, most notably the 99 species of lemurs. Another continent-island is New Caledonia, which has many endemic species, including about half of the trees in the conifer family Araucariaceae. The flowering plant that most nearly resembles the ancestral flowering plant, Amborella trichopoda, is endemic to New Caledonia. Taiwan, the world’s fourth largest island, has also been isolated for many millions of years and has many endemic species. Twenty percent of its animals (including 64 percent of its mammals, such as the Formosan rock macaque) and 26 percent of its plants are endemic. Young volcanic islands have had much less time for the evolution of endemic species, yet they have many. The oldest islands of the Hawaiian archipelago are only about 5 million years old. Despite its youth, the Hawaiian archipelago has (or had, prior to extinction caused by the aboriginal Polynesian humans) many endemic bird species, including 51 species of honeycreepers. The Galápagos Islands, off the coast of Ecuador, also have many endemic ­species, most famously the giant tortoises. The crocodile Crocodylus mindorensis is found only on the Philippine islands.

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222 endemic species  222

Ecological Island Endemics Ecological islands are small habitats surrounded by large expanses of an environment unsuitable for its species. Frequently they are remnants of previously large habitats. Examples include the following: ●●

●●

●●

●●

●●

●●

●●

●●

●●

Cloud forests are deciduous forests at the tops of tropical mountains. Some of the species are the same as those of temperate deciduous forests, while others are endemics. In California, all of the coastal closed-cone pine species and coastal dry temperate oak species are endemic. Some oak species, such as Quercus carmenensis and Q. deliquescens, are endemic to mountaintop dry forests surrounded by desert in northern Mexico and southwestern United States. Ginkgoes were once widespread in temperate forests, but by modern times were nearly extinct. Just one species, Ginkgo biloba, survived as an endemic species in small patches of forest in China. The dawn redwood (Metasequoia glyptostroboides) once grew widely in the forests of Asia but today is endemic to a small region in Sichuan and Hubei Provinces of China. The giant redwood (Sequoiadendron giganteum) was once widespread in western North America but is now restricted to a few moist coniferous forests in the Sierra Nevada. The Serbian spruce (Picea omorika), which today grows only in the Drina River Valley, was once more widespread in Eurasia. The Santa Lucia fir (Abies bracteata) now grows only in moist microenvironments of the Santa Lucia Mountains of coastal California. Torreya taxifolia is a conifer now endemic to the Apalachicola River area of northern Florida and southwestern Georgia.

Isolated lakes can also have numerous endemic species. The food web of Lake Baikal in Siberia is based upon an endemic zooplankton species, Epischura baikalensis. Among the endemic fishes in Lake Baikal are the Baikal oil fish species Comephorus baikalensis and C. dybowskii and the Baikal sturgeon subspecies Asipenser baerri baicalensis. Lake Baikal has an endemic seal species Phoca sibirica. Some endemic plants have proven to be popular ornamentals, partly because they can tolerate a greater range of climatic conditions than their restricted natural range would suggest and partly

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first entry because of the allure of their rarity. Ginkgoes are now planted worldwide, and dawn redwoods are not uncommon in parks and gardens. A few people have planted seaside alders in their yards, and a volunteer group of citizen-naturalists has planted Torreya trees at several other locations in the southeastern United States. The umbrella palm (actually a sedge, Cyperus alternifolius) is endemic to Madagascar but is now a popular water garden ornamental. The traveler’s palm (Ravenala madagascariensis, actually a relative of the bird of paradise plant), endemic to Madagascar, is also a popular ornamental in warm regions of the world. See also biogeography; cloud forests; disjunct species; endangered species; Galápagos Islands; island biogeography. Further Reading Bowen, Lizabeth, and Dirk van Vuren. “Insular endemic plants lack defenses against herbivores.” Conservation Biology 11 (1997): 1,249–1,254. Harrison, Susan. “Local and regional diversity in a patchy landscape: Native, alien, and endemic herbs on serpentine.” Ecology 80 (1999): 70–80. Lavergne, Sébastien, et al. “The biology and ecology of narrow endemic and widespread plants: a comparative study of trait variation in 20 congeneric pairs.” Oikos 107 (2004): 505–518. Malcolm, Jay R., et al. “Global warming and extinction of endemic species from biodiversity hotspots.” Conservation Biology 20 (2006): 538–548. Médail, Frédéric, and Régine Verlauque. “Ecological characteristics and rarity of endemic plants from southeast France and Corsica: Implications for biodiversity conservation.” Biological Conservation 80 (1997): 269–281. Orme, C. David L., et al. “Global hotspots of species richness are not congruent with endemism or threat.” Nature 436 (2005): 1,016–1,019. Park, Young-Seuk, et al. “Conservation for endemic fish species threatened by the Three Gorges Dam.” Biological Conservation 17 (2003): 1,748–1,758. Philippart, Jean Claude. “Is captive breeding an effective solution for the preservation of endemic species?” Biological Conservation 72 (1995): 281–295. Silvertown, Jonathan. “The ghost of competition past in the phylogeny of island endemic plants.” Journal of Ecology 92 (2004): 168–173. Thompson, John D. “Population differentiation in Mediterranean plants: insights into colonization history and the evolution and conservation of endemic species.” Heredity 82 (1999): 229–236. Van der Werff, Henk, and Trisha Consiglio. “Distribution and conservation significance of endemic species of flowering plants in Peru.” Biodiversity and Conservation 13 (2004): 1,699–1,713.

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environmental ethics  223

environmental ethics  Members of the human species are unique in having the need to invent ethical systems to determine the actions that they should take. Ethical systems evolved first for local then national and then international relationships among human beings. Environmental ethics prescribe correct actions of humans toward other species and toward the Earth as a whole. It was the last to evolve and is still in rudimentary stages of development. While wide consensus has been reached on international ethical issues such the condemnation of nuclear war and torture, such consensus is a long way off for environmental issues. Many people see environmental ethics as an inevitable extension of the trajectory of the ethics of human interactions. At the time that Odysseus hung all of his disobedient household slaves on one rope, such action was accepted as ethical. Today it is considered murder. Many people say it is time to consider the abuse of nonhuman creatures and of the Earth just as evil as the abuse of one human or human group by another. A magazine article in 2008 described the slaughter

of gorillas in Africa; it was entitled, “Who Murdered the Mountain Gorillas?” In the United States in the 1930s, the massive soil erosion of the dust bowl in the western plains was considered a natural resource disaster, but many observers also considered it an immoral violation of the Earth (see illustration). Any group of organisms acting only in its own interests has the capacity of destroying its local environment or the entire Earth. While the Gaia hypothesis, first proposed by climate scientist James Lovelock, describes the many ways in which organisms have promoted their own success through cooperation with others, and the ways in which such cooperation has influenced the entire Earth (especially its atmosphere), biologist Peter Ward has proposed an alternative. The Medea hypothesis describes the ways in which organisms have devastated their local environments and the entire Earth through the pursuit of their own interests. He cites the Permian extinction, caused by bacterial hydrogen sulfide, as an example. It appears that, without environmental ethics, humans metabolizing

Alexandre Hogue painted Erosion No. 2—Mother Earth Laid Bare during the dust bowl in the central United States—it depicts erosion, caused principally by irresponsible farming, as a violation of a sacred, living planet.  (Philbrook Museum, Tulsa, Oklahoma)

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224 environmental ethics  224 their way through the biosphere cannot avoid environmental destruction perhaps as disastrous as that of the Permian extinction. Most if not all of the world’s environmental problems could be solved by pragmatism. Global warming should be curbed because of the devastating effects it will have on all aspects of human activity. Heavy metal pollution should be prevented because the metals concentrate in the food chain and can endanger human health. Biodiversity should be protected because many of the species may provide immense economic benefit in the future. Ecologist Aldo Leopold, considered by many to be the founder of environmental ethics, stated that the first law of intelligent tinkering was to not throw out any of the parts. These pragmatic arguments apply to human society as a whole; it is usually profitable for corporations to continue releasing carbon dioxide and heavy metals as long as they can get away with it, since the profit is theirs and the damage is shared by everyone. It may not be necessary to go beyond merely pragmatic arguments, since the implementation of these arguments appears to be beyond human capacity at this time: The human species appears incapable of reducing its carbon output enough to prevent disaster. What is the point of going beyond a practical argument? This question is difficult to answer, other than to point out that many people are simply not any more satisfied with a pragmatic argument for environmental preservation than for a pragmatic argument against genocide. Nearly everyone admits the necessity of moral, rather than just pragmatic, environmental ethics—some from a desire to conform, others out of passion. Proposed systems of environmental ethics can be roughly classified on the basis of what a person considers the environment to be: creation or nature. The first considers the environment and all of its living and nonliving components to be the product of a deity that has made humankind separate from it in some way, while the second considers the environment to be the source of humankind (“nature” comes from the Latin for “birth”).

first entry pre-ecological scriptures and pick out passages that were not written for the purpose of answering such questions and try to base systems of environmental ethics upon them. Because of the importance of the Judeo-­ Christian Bible in the history of western culture, historian Lynn White, Jr., wrote in 1967 that Christianity, guided by the first chapter of Genesis, had been in the forefront of a largely successful attempt to conquer the created world. It is beyond dispute that, according to this chapter, God gives humans the command to conquer and subdue the Earth and have dominion over it. The words clearly refer to the kind of conquest that kings exercised over vanquished nations. White did not, however, say that Christianity should be rejected, but that Christians should use Saint Francis of Assisi, a medieval Italian monk who considered the Sun, Moon, wind, fire, and all creatures to be his brothers and sisters, as the model of ethical behavior rather than the Bible. Not surprisingly, many Christians became defensive and claimed that White had misinterpreted the first chapter of Genesis. Since 1967, Christian writers have found many passages in the Bible that paint a very different picture of the creation. Here are a few examples: ●●

●●

●●

●●

The Environment as Creation The major monotheistic religions of the world (Judaism, Christianity, and Islam) believe that a single, allpowerful deity created the world and made humans the rulers of it. Moreover, these religions base their beliefs upon scriptures written long before people even imagined the questions of environmental ethics. Until the last few centuries, humans quite rightly viewed the Earth as unconquerable and usually dangerous. The Earth could take care of itself. Modern adherents of these religions therefore turn to their

xviii+598_Biodiversity_F.indd 224

●●

The second chapter of Genesis depicts God as commanding humans to take care of the Earth the way one would care for a garden (the Garden of Eden). The third chapter of Genesis depicts expulsion from the Garden of Eden and a host of environmental problems (“cursed is the ground . . . thorns and thistles it shall bring forth”) as consequences of sin. The sixth chapter of Genesis describes Noah, whose family was to be the sole survivors of a worldwide flood. God told Noah to build an ark big enough for a pair of each species of terrestrial animal, presumably even those that Noah did not especially care about. The Ten Commandments included a prohibition against work on one day of the week, called the sabbath. The result of this commandment, according to conservative Jewish scholars, is the deliberate interruption of the momentum of acquisition—to desist, once a week, from using other people (and the Earth) as a source of profit. The Old Testament law included some commandments that dealt directly with the Earth. Most famous is the Sabbath of the Fields, in which agricultural fields were supposed to be left fallow every seventh year.

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environmental ethics  225 ●●

●●

●●

In the book of Job, God addresses Job from a whirlwind and describes a vast unknowable and unconquerable world of creatures, from large ones such as Behemoth and Leviathan to humble ones such as donkeys and conies. The message is clear that the purposes of these creatures have absolutely nothing to do with humans. The fact that these creatures are untamed was a perfectly acceptable part of God’s order of the world. Many passages in the psalms and prophets describe the beauty of creation entirely apart from any benefit it may confer on humans. A passage from the prophet Isaiah describes trees reclaiming wasteland and restoring its water resources and claims that this process, which would now be called ecological, was the work of God. Jesus frequently used symbolism from the creation, from wildflowers to sparrows, in his parables—frequently things that would be noticed only by people who stopped to carefully observe them.

Ecology-minded Christians, who focus attention on these passages, claim that God has given humans the responsibility to be stewards, or caretakers, of the Earth, rather than its conquerors. This is an important concept, even though the terms steward and caretaker do not appear in the Bible in connection with the Earth. The above examples aside, White was right in his conclusion. One reason is that the Bible is not a book. It is a collection of books, written by many people over many centuries, and it does not have a single coherent message. Most of the biblical books are themselves the product of editorial redaction from different primordial traditions. The first chapter of Genesis, correctly interpreted by White, presents a different view of creation from the second chapter, which was originally written by a different person. Each part of the Bible potentially contradicts every other part. An adherent of Christianity may choose to accept a biblical image of conquering the Earth or a biblical image of taking care of it. It all depends on which passage is chosen. Adherents of Christianity, Judaism, or Islam can, however, force these passages into harmony, and in this way they can use the second chapter of Genesis to ameliorate the first. White was right for another reason. Christian theologians have forced all the biblical passages into harmony, and the climax of this harmonized Bible is the book of Revelation, also known as the Apocalypse. Revelation, the last book of the Bible, is the only example of an entire style of literature, popular

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in the Mediterranean world about 100 c.e., which is familiar to most modern readers. In this book, the entire biosphere of the Earth is destroyed during cosmic battles between good and evil, and those who are saved live in Heaven. The Heavenly City there described is the antithesis of biodiversity and contains virtually nothing of the original creation. There is a river and a single tree. Everything else is gold and jewels—an utterly artificial environment. If this is, as about half of Americans believe, the future of the universe, what is the point of saving species and ecosystems? For this reason also, if Christians are to participate in the rescue of the environment, they must look beyond the Bible and perhaps, as White suggests, emulate St. Francis. The extreme popularity of apocalyptic Christianity meant that Christians, as a whole, were a feeble source of support for environmental protection. Their main passion was to support the politically conservative George W. Bush administration, which rejected the evidence of global warming and paid little attention to environmental protection. In fact, after the end of the Bush administration, the full extent of conservative neglect for even the most basic environmental protection became obvious. The Minerals Management Service of the Department of the Interior was supposed to license fossil fuel extraction on federal lands with due consideration of the impact that this extraction would have on natural habitats. Instead, they gave licenses to corporations in return for bribes and sexual favors. When President Bush left the 2007 economic summit, he said, “Goodbye from the world’s biggest polluter,” making environmental ethics into what he considered to be a joke. Edward O. Wilson, perhaps the world’s leading defender of biodiversity, wrote a book that was addressed to an unnamed Baptist minister. Wilson said that a conservative Christian could find common ground with even a secular humanist like himself by defending the Earth, which Wilson called the Creation. Wilson, however, wrote this book only after originally considering the Christian environmental movement to be a hopeless cause. With the end of the Bush administration and the disgrace of several leading Christian antienvironmentalists, a tide of opinion has turned toward Christian environmentalism. Despite this, many conservative Christians still consider the Earth to be unworthy of serious attention. They focus their attention instead on fighting against evolutionary science. When Edward O. Wilson visited Oklahoma in March 2009, a group of creationists disputed him about whether Charles Darwin did or did not believe in a Creator, and in the process Wilson’s impassioned plea for saving the Earth’s biodiversity was

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226 environmental ethics  226 largely obscured. The view of the Earth that many conservative Christians have can be summarized in this way: “It’s okay to spit on it, to drive a truck over it, to spill oil on it, to chop it down, or to shoot it, so long as you don’t believe that it evolved!” All during this time, a significant minority of Christians continued to insist that protecting the Earth was a Christian responsibility because the Earth is God’s creation.

The Environment as Nature Other religious traditions consider the Earth to be nature, from which humans evolved and of which humans are a part, just like every other species. Some of these religions are polytheistic, such as Buddhism and paganism, while others are more akin to spiritual philosophies, such as Taoism. There is even a little of this viewpoint in the Bible. The 104th psalm describes a world of creatures, of which humans are depicted as merely one component. Although these religions have not led their adherents on a deliberate conquest of the Earth, the homelands of these religions have suffered their share of environmental problems. The natives of North and South America experienced collapsed civilizations just like the Europeans. The person most responsible for the emergence of environmental ethics based upon ecology was Aldo Leopold. As mentioned previously, Leopold made a pragmatic argument for the preservation of biodiversity. But he also promoted what he called the “land ethic” and championed what he called “thinking like a mountain.” Humans, rather than rulers or even stewards, would be merely “plain member and citizen” of the world of species. Right and wrong were defined as those actions that contributed to or detracted from the health of nature. His essays in A Sand County Almanac remain a classic, even though they do not develop a complete ethical system. More recently, writer Wendell Berry has called for an ecological humility as the proper ethical system for humans. Biologist Wes Jackson promoted a very pragmatic view of the stewardship of natural resources, particularly soil, in New Roots for Agriculture and by founding The Land Institute in Salina, Kansas. Like Leopold, Jackson then went beyond pragmatism and calls for humans to recognize their membership in the world of interacting species. Attention is now being given to evolution, as well as ecology, as a foundation for environmental ethics. Humans are one of several million species and, like the rest of them, evolved by natural selection; humans therefore have no rights not possessed by the other species. Some thinkers have gone so far as to develop a viewpoint known as Deep Ecology,

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first entry in which the human species has become a disease upon the Earth that needs to be brought into control. Most environmentalists seek peaceful and orderly solutions to environmental problems—for both ethical and pragmatic reasons. A few organizations, however, use violent tactics to gain attention, even though they have little hope of actually counteracting the economic forces behind environmental destruction. These tactics usually take the form of arson on resorts that are closed for the season. Although no one has yet died from what conservatives call “environmental terrorism,” Senator James Inhofe, Republican of Oklahoma, said that these organizations were the greatest threat of domestic terrorism in the United States. He said this even though Oklahoma was the site of the largest act of domestic terrorism that has ever occurred in the United States—the Oklahoma City bombing, which had nothing to do with environmentalism. Conservatives conveniently ignore acts of violence carried out by extremists on the political right (again, without deaths) against government agencies, such as the Bureau of Land Management, whose charge is to protect natural areas.

The Problem of Fragmentation Perhaps the major impediment to environmental ethics is academic fragmentation. Nearly everything that humans do and every area of study have environmental implications and a role to play in the development of environmental ethics. Science, religion, business, psychology, sociology, and the humanities are all necessary components of environmental ethics. Yet all of these fields of study are largely separate from one another. Environmental issues are largely left to environmental scientists. Meanwhile, economists often continue to do their work as if the world were understood the same today as in the time of Adam Smith. Economist Kenneth Boulding said, “Anyone who believes that exponential growth can go on forever in a finite world is either a madman or an economist.” Only by bringing environmental science and ethics into all fields of study will humankind have a coordinated response to the threat of environmental disaster. Edward O. Wilson calls for a “consilience” of all academic disciplines, centered around the recognition of environmental and evolutionary realities of the human species. This idea, necessary as it is, has made little progress. The most promising direction for success in environmental ethics is to work toward a convergence. If people become aware of the pragmatic reasons for protecting the environment and biodiversity, they will turn to their own ethical background—whether monotheistic religion, natural religion, ecology, or

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environmental ethics  227 evolution—and join with others to implement solutions to environmental problems, even people who have reached the same conclusion from a different starting point.

The Inevitability of Dilemmas When a species with as much technological potential as Homo sapiens evolves, whatever happens next is going to be wrong. Every action taken by such a species is going to have a destructive impact, if only because of enormous population growth. Dilemmas, therefore, are inevitable. One example of such a dilemma involves the use of plastics. Objects made of plastics, such as containers and sacks, never decompose. If they become litter they end up in the ocean, often in gigantic gyres filled with garbage. Over a dozen such oceanic trash heaps exist, some as large as Texas. Marine animals such as turtles and birds have not evolved the ability to distinguish between garbage and their normal food items and often die after eating large numbers of plastic objects. The plastic in aquatic ecosystems may become brittle from exposure to ultraviolet light and break into ever smaller pieces. These pieces then become part of the plankton and are consumed by other aquatic animals. No one knows what will happen when all of the plastic that today consists of large chunks eventually breaks into plankton-sized pieces. Even when most people are careful about proper refuse disposal and recycling, much plastic garbage ends up in the environment: Wind can rip plastic bags right out of refuse bins when their contents are being transferred to garbage trucks. Some cities and even entire countries (such as Ireland) have banned plastic bags, and shoppers increasingly bring their own bags, some made from recycled plastic. If plastic containers had not been invented, many more containers would have been made of metal or glass. Transportation of these heavier containers would have resulted in the burning of more fossil fuels and a greater contribution to the greenhouse effect. Plastics, therefore, have contributed to a major worldwide pollution problem but relieved the Earth from some of its greenhouse effect. Should the use of plastics be encouraged or prohibited? The only way around such a dilemma is to find an altogether different solution. For example, if consumers buy and use less material, there will be less need for containers. Meanwhile, the dilemma remains. Environmental scholar Martin Lewis points out another dilemma. Burning coal has contributed immensely to air pollution and the greenhouse effect. Yet it was coal, as a new energy source, that spared the English forests from complete destruc-

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tion at the beginning of the Industrial Revolution. The dilemma—is coal good or bad?—can be solved only by finding an altogether different solution, which is to use neither coal nor wood, an option that was not available in the 19th century. Dilemmas are unavoidable in environmental ethics and can only be resolved if dedicated people employ creative thinking. See also Essay: “Ecosystem Services: Public or Private Costs?”; ecosystem services; greenhouse effect; Wilson, Edward O. Further Reading Bailey, Liberty Hyde. The Holy Earth. Ithaca, N.Y.: Cornell University Press, 1915/1980. Berry, Thomas. The Dream of the Earth. San Francisco: Sierra Club, 1988. Berry, Wendell. The Gift of Good Land. San Francisco: North Point Press, 1981. ———. The Unsettling of America. San Francisco: Sierra Club, 1977. Douglas, William O. “Mineral King and the Rights of Rocks.” Supreme Court of the United States, Sierra Club v. Morton, 70–34, April 19, 1972. Foreman, Dave. Confessions of an Eco-Warrior. New York: Random House, 1993. Hardin, Garrett. “Ecology and the death of providence.” Zygon 15 (1980): 57–68. Jackson, Wes. Becoming Native to This Place. Berkeley, Calif.: Counterpoint, 1996. ———. New Roots for Agriculture. Lincoln: University of Nebraska Press, 1980. Jenkins, Mark. “Who murdered the Virunga gorillas?” National Geographic, July 2008, 34–65. Leopold, Aldo. A Sand County Almanac: With Essays on Conservation from Round River. New York: Sierra Club/Ballantine Books, 1974. Lewis, Martin H. Green Delusions: An Environmentalist Critique of Radical Environmentalism. Durham, N.C.: Duke University Press, 1992. Lovelock, James. The Vanishing Face of Gaia: A Final Warning. New York: Basic Books, 2009. Manes, Christopher. Green Rage: Radical Environmentalism and the Unmaking of Civilization. Boston, Mass.: Little, Brown, 1990. McKibben, Bill. The Comforting Whirlwind: God, Job, and the Scale of Creation. Cambridge, Mass.: Cowley, 2005. Orr, David W. Earth in Mind: On Education, Environment, and the Human Prospect. Washington, D.C.: Island Press, 1994. Shaw, James H. “Assessing the progress toward Leopold’s Land Ethic.” Wildlife Society Bulletin 15 (1987): 470–472. Snyder, Gary. The Practice of the Wild. San Francisco: North Point Press, 1990.

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228 environmental psychology  228 Stone, Christopher D. Should Trees Have Standing?: Towards Legal Rights for Natural Objects. Los Altos, Calif.: W. Kaufmann, 1981. Van Dyke, Fred, David C. Mahan, Joseph K. Sheldon, and Raymond H. Brand. Redeeming Creation: The Biblical Basis for Environmental Stewardship. Downers Grove, Ill.: Inter-Varsity Press, 1996. Ward, Peter. The Medea Hypothesis: Is Life on Earth Ultimately Self-Destructive? Princeton, N.J.: Princeton University Press, 2009. White, Lynn, Jr. “The historical roots of our ecologic crisis.” Science 155 (1967): 1,203–1,207. Wilson, Edward O. Consilience: The Unity of Knowledge. New York: Knopf, 1998. ———. The Creation: An Appeal to Save Life on Earth. New York: Norton, 2006.

environmental psychology  Environmental (or conservation) psychology is the study of the beneficial effects of nature on the human mind. This includes a person’s frequent presence within natural settings and direct contact with a diversity of wild organisms. It is widely recognized that humans have an innate desire for direct contact with the natural world. Evolutionary biologist E. O. Wilson coined the term biophilia for the universal human love (-philia) of nature and life (bio-). It may have a genetic component, as well as a learning component that is acquired by children during exposure to the outdoors. It will perhaps be impossible for scientists to rescue the biodiversity of the Earth without drawing upon the psychological resources of citizens of countries all over the world—to tap into the feelings of biophilia. Biophilia, contends Wilson, was as much the product of natural selection as any other aspect of human psychology such as the fear of strangers. Biophilia provided a fitness advantage for humans and their evolutionary ancestors. The enjoyment of birds, trees, and mammals encouraged learning about them. By carefully watching the other species, primitive humans could learn to make more effective use of them as natural resources. The people who enjoyed listening to birds would be more likely to recognize a bird alarm call that might indicate the presence of a dangerous predator. While a feeling of biophilia was not necessary to these beneficial actions, it made them easier and more effective. The extensive use of animal motifs in such paintings as those in the caves of Lascaux and Altamira suggests that biophilia may have been closely connected to religion, which also provided important advantages to primitive human societies. An appreciation of the beauty of the landscape and a love for its living

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first entry community of species may have kept some primitive humans from giving up in the frequently harsh circumstances of life, and these were the humans who were the ancestors of modern people. Modern humans are, according to this concept, happiest in environments that most closely resemble the savanna in which the human genus first evolved 2 million years ago. Psychologists and urban planners have independently arrived at a concept similar to biophilia. Psychologists have found that humans are happier in, and choose environments that contain, a balance of trees and open areas. Urban planners have been careful to include trees and landscaping with buildings and parks between them. Biophilia may also explain the frequent success of horticultural therapy in the recovery of patients from physical and mental diseases. Programs to help guide children away from social problems often include an outdoor component. Even though many people can be as happy in a big city as if it were canyons, most people seek occasional escape into the natural world. Biophilia may be essential to the successful preservation of natural areas simply because most people cannot conceive of living in a world in which natural areas have been destroyed. In modern society, the learning component of biophilia has overlooked a great deal of biodiversity. Many people like trees but do not particularly care which ones. While Central American native tribal children can identify many plant species, as could rural American children just a few decades ago, modern children in the United States can identify very few. Moreover, when modern humans visit the outdoors, they usually take a great deal of their manufactured environment with them. Wilson and many others believe that, in order to rescue biodiversity from what appears to be the sixth of the mass extinctions that is now resulting from human activity, humans must rediscover the love not just of nature but of species. In this regard, evolutionbased biological and environmental education may be essential for the protection of the natural world. It is not just modern scholars who have claimed that exposure to the natural world may be essential to healthy psychological development in children. In one of his last essays, “The Dispersion of Seeds,” 19th-century American naturalist Henry David Thoreau wrote: A man fits out a ship at a great expense and sends it to the West Indies with a crew of men and boys, and after six months or a year, it comes back with a load of pine-apples; now, if no more gets accomplished than the speculator commonly aims at, if it simply turns out what is called a

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environmental psychology  229 successful venture, I am less interested in this expedition than in some child’s first excursions a-huckleberrying, in which it is introduced into a new world, experiences a new development, though it brings home only a gill of berries in its basket.

Research, such as that conducted by landscape ecologist Frances E. Kuo, has clearly demonstrated that humans receive psychological benefits from contact with natural landscapes. It is well known that children with attention deficit hyperactivity disorder (ADHD) have reduced symptoms if they have time for recess. Kuo has shown that ADHD symptoms were reduced more by outdoor playtime than by indoor play, and by outdoor play in the vicinity of trees and other plants than by play on cement or asphalt. She has also shown that girls growing up in a Chicago housing project score higher on tests of self-discipline (concentration, control of compulsive behavior, delay of gratification) when their apartments have views of trees and green spaces than when they do not. There was a similar effect of green spaces on the ability of inner-city women to deal with major life issues. Green surroundings can even reduce crime. Within a Chicago housing project, areas that have trees and grass had 48 percent fewer property crimes and 56 percent fewer violent crimes than areas that lacked vegetation. Reasons may include that green landscaping encourages people to spend more time outdoors, thus increasing their surveillance and preventing crime, and that green landscaping is an indication that residents take better care of the property in which they live. These results run directly counter to the misconception that trees are dangerous because criminals can hide behind them. Residents that live in housing project buildings surrounded by trees and grass report in surveys that they knew their neighbors better, socialized with them more often, and had a stronger sense of community than residents of buildings without green surroundings. These results show that natural settings do more than just make people feel better; they have measurable effects on reducing crime and on the quality of life in a community. Other researchers have also shown the medical and social benefits of green environments. In one study, volunteers watched a stressful movie, followed by pictures of either urban or natural settings. Those who watched the natural images recovered from the stress more quickly, as measured by blood pressure, heartbeat rate, and facial muscle tension. Other studies have demonstrated that patients experience less stress prior to surgery if the waiting room has plants, aquaria, or windows with a natural view.

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After surgery, patients recover more quickly and require less painkiller if they have a window with a view of trees. Studies with psychiatric patients and prisoners also show that views of nature can reduce symptoms of stress. All of this is in addition to the enhancement of physical health that comes from regular exercise, such as hiking and jogging, in natural settings. Nature is not just a place to kill time but an essential investment in physical and mental health. National legislation called No Child Left Inside (a counterpart to the educational legislation No Child Left Behind) was introduced to Congress in 2011. It would seem to be the easiest thing in the world to enhance the health of both children and adults by preserving and creating urban natural areas. There are problems, however. One is liability. If a child, or anyone else, is injured while hiking or climbing in a natural area, the government or private owner risks a lawsuit. The fear of litigation is one reason that many schools have reduced the amount of recess and limited most of this to highly supervised and very unnatural playgrounds. In addition, green spaces are often not readily accessible because developed residential areas are cut off from them by busy streets and highways. Not all ways of spending time in nature are equally good. In several places around the United States, desert dunes have been set aside on which people can ride all-terrain vehicles; these vehicles are also permitted on some trails on Forest Service land. This sort of recreation does not encourage close observation and appreciation of nature and biodiversity, nor does it tap into the psychological benefits of contact with nature. Frequently, users of all-terrain vehicles wander from designated areas and destroy natural and archaeological sites. Just being outdoors is, therefore, not enough. One problem that has resulted from lack of contact with nature is that people do not realize what nature is supposed to look like. When a natural habitat is degraded by human activity, a new generation of children grows up thinking that this is the way it is supposed to look—that invasive species are natural components of a habitat, that eutrophication is natural. As a result, they are not motivated to take action to preserve truly natural environments or to remediate degraded environments. Most scientists and environmental professionals agree that the increasing awareness of environmental problems is good, because it will motivate people to change the habits that contribute to these problems (e.g., reducing one’s carbon footprint). But this awareness can have a negative effect also. Psychologists Jessica Frizte and colleagues have pointed out that the changes associated with the greenhouse effect, particularly disastrous storms and droughts,

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230 Eocene epoch  230 may significantly contribute to anxiety and mental health problems. By encouraging people to have more direct contact with nature, it is nearly inevitable that they will not only begin to care more about biodiversity but will begin to experience nature not as a problem to be solved but as a world to be enjoyed and protected. See also greenhouse effect; Thoreau, Henry David; Wilson, Edward O. Further Reading California Roundtable on Recreation, Parks, and Tourism. “California Children’s Outdoor Bill of Rights.” Available online. URL: http://www.calroundtable.org. Accessed August 26, 2009. Chicago Wildnerness. “Leave No Child Inside.” Available online. URL: http://www.kidsoutside.info. Accessed August 25, 2009. Children and Nature Network. “Children and nature network: Building a movement to reconnect children and nature.” Available online. URL: http://www.children andnature.org. Accessed August 8, 2011. Clayton, Susan, and Gene Myers. Conservation Psychology: Understanding and Promoting Human Care for Nature. Oxford, U.K.: Wiley-Blackwell, 2009. Connecticut Department of Environmental Protection. “No child left inside.” Available online. URL: http:// www.nochildleftinside.org. Accessed May 13, 2011. Dean, Bradley P., ed. Faith in a Seed: The First Publication of Thoreau’s Last Manuscript. Covelo, Calif.: Island Press, 1993. Faber Taylor, A., et al. “Coping with ADD: The surprising connection to green play settings.” Environment and Behavior 33 (2001): 54–77. ———, et al. “Views of nature and self-discipline: Evidence from inner city children.” Journal of Environmental Psychology 22 (2002): 49–63. Fritze, Jessica G., et al. “Hope, despair, and transformation: Climate change and the promotion of mental health and wellbeing.” International Journal of Mental Health Systems 2 (2008): 13–22. Hooked on Nature. “Tools, resources, and workshops to help people deepen their relationship with the natural world.” Available online. URL: http://www.hookedonnature.org/. Accessed May 13, 2011. Kuo, Frances E., et al. “Fertile ground for community: Inner-city neighborhood common spaces.” American Journal of Community Psychology 26 (1998): 823–851. Kuo, Frances E., and A. Faber Taylor. “A potential natural treatment for Attention-Deficit/Hyperactivity Disorder: Evidence from a national study.” American Journal of Public Health 94 (2004): 1,580–1,586. Kuo, Frances E., and W. C. Sullivan. “Environment and crime in the inner city: Does vegetation reduce crime?” Environment and Behavior 33 (2001): 343–367.

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first entry Lewis, Charles A. Green Nature Human Nature: The Meaning of Plants in Our Lives. Urbana: University of Illinois Press, 1996. Louv, Richard. Last Child in the Woods: Saving Our Children from Nature Deficit Disorder. Chapel Hill, N.C.: Algonquin Books, 2008. Takano, T., et al. “Urban residential environments and senior citizens’ longevity in megacity areas: The importance of walkable green spaces.” Journal of Epidemiology and Community Health 56 (2002): 913–918. Ulrich, R. S., et al. “View through a window may influence recovery from surgery.” Science 224 (1984): 420–421. ———, et al. “Effects of environmental simulations and television on blood donor stress.” Journal of Architectural and Planning Research 20 (2003): 38–47. University of Illinois at Urbana-Champaign. “Landscapes and Human Health Laboratory.” Available online. URL: http://lhhl.illinois.edu. Accessed August 8, 2011. Wilson, Edward O. Biophilia. Cambridge, Mass.: Harvard University Press, 1986.

Eocene epoch  See Paleogene period, biodiversity in.

estuaries  See marshes and swamps. eukaryotes  Eukaryotes are organisms that consist of complex cells. All cells have a cell membrane, which is a thin double layer of lipids that maintains a chemical difference between the inside of a cell and the outside; cytoplasm, which is the liquid contents of a cell with its suspended components; ribosomes, which make proteins; and DNA, which stores genetic information. The simplest cells (though by no means simple) are the prokaryotic cells which have very little more than this. Bacteria and archaea have, in addition, a cell wall and, in some cases, internal membranes. The cells of protists, fungi, plants, and animals are eukaryotic cells, which are often about 10 times larger than prokaryotic cells and much more complex. Eukaryotic cells have a nucleus, which contains the DNA in the form of chromosomes inside of a membrane; an internal membrane system involved in making large molecules inside the cell; and organelles such as chloroplasts and mitochondria. Eukaryotic refers to the nucleus (Greek for “true kernel”). The DNA molecules in the nucleus are associated with proteins called histones, and the membrane surrounding the nucleus has pores, which are not merely holes but are passageways controlled by proteins. These pores allow genetic instructions and

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eukaryotes  231 materials, in the form of RNA, to go out into the cytoplasm and allow hormone messages to enter the nucleus. Part of the reason bacteria have rapid metabolism is that as soon as the genetic information of DNA is transcribed into RNA, the ribosomes start using the information to make proteins. In eukaryotic cells, the RNA must travel out to the cytoplasm first, a process that is slower but allows a greater degree of control over the use of genetic information. The events involved in the origin of eukaryotes have not been resolved. It is known that chloroplasts and mitochondria are the degenerate evolutionary descendants of prokaryotes that invaded and persisted in ancestral eukaryotic cells. The bacterial ancestors of chloroplasts and mitochondria had enough DNA to control their own activities, but chloroplasts and mitochondria do not now have enough genes to survive on their own. Many genes transferred from the primitive chloroplasts and mitochondria to the nucleus of the host eukaryote. In some cases, part of a complex gene transferred to the nucleus and part remained behind in the organelle. An important enzyme in photosynthesis, the rbc gene for the rubisco enzyme, is constructed from genetic instructions in both the chloroplast (the large component, rbcL) and the nucleus (the small component). Mitochondrial genes occasionally act in a manner that is against the best interests of the nucleus (for example, cytoplasmic male sterility factors in plants). Smaller cells moving into and living inside a larger cell is an example of symbiosis, and when it leads to the origin of a new species, it is called symbiogenesis. The evolution of the nucleus has proven much more difficult to explain. Three theories have been proposed, each with provocative evidence. The three theories for the origin of the nucleus are symbiogenesis, the evolution of the nucleus from structures in bacterial ancestors, and that the nucleus evolved from a virus. The nucleus originated through symbiogenesis. Some evolutionary scientists propose that a primordial archaea entered into a larger bacterial host cell and became its nucleus. Subsequently, horizontal gene transfer merged the bacterial and the archaeal DNA. According to this theory, the nucleus was originally archaeal, to which eubacterial genes were added. It is not clear what kind of bacterium might have been the original host. It may have resembled today’s myxobacteria, which unlike other bacteria use molecules for intercellular communication and can form multicellular structures, just like eukaryotes. It is also not clear where the membrane that surrounds the nucleus came from. Lynn Margulis, who convinced most evolutionary scientists of the

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symbiogenetic origin of chloroplasts and mitochondria, proposes that the nuclear membrane began as a fusion of the membranes of bacterial and archaeal attachment structures. The nucleus evolved from structures in bacterial ancestors  Most biologists, biology teachers, and biology students assume that eukaryotes have fully formed nuclei, and bacteria have nothing of the sort. It turns out that an obscure group of bacteria called planctomycetes have their DNA almost completely enclosed in a membrane that looks like a nuclear membrane. Another group of recently discovered bacteria, which live only inside of sponges, also appear to have structures that look like nuclei. Some researchers even claim that these bacteria have nuclei and that the eukaryotic nucleus may have evolved from this bacterial nucleus. Critics point out that, despite appearances, the eukaryotic nuclear membrane and the membrane inside these bacteria are structurally very different. The nucleus evolved from a virus. A few researchers point out that nuclei, like viruses, are genetic material surrounded by a protein coat. They maintain that an ancient virus invaded an archaeal cell, and instead of killing the host, the virus maintained a multigenerational mild infection inside of it. Gradually, horizontal gene transfer moved bacterial genes into the virus, which became the nucleus. Their evidence is that nuclei, like viruses, depend on the cell around them for metabolism. And while bacterial DNA molecules are circular, the DNA of viruses is linear, like that of eukaryotic nuclei. Some viruses not only have a protein coat but have an envelope, which they make by stealing a chunk of the host cell membrane, just like the eukaryotic cell uses internal membranes to make the nuclear membrane. Some large viruses even have telomeres, nucleotide sequences at the ends of chromosomes that, in eukaryotes, help keep the process of DNA replication itself from breaking off chunks of essential genes. These three possibilities are not mere guesses but can be framed as scientific hypotheses. If the first eukaryotic cells were mergers between archaea and bacteria, then some eukaryotic genes should more closely resemble those of archaea, while others should more closely resemble those of bacteria. This appears to be the case. DNA sequences for the genes in eukaryotes that are involved in the use of genetic information resemble archaeal genes. This includes the production of histone proteins, known only from eukaryotic and archaeal cells. DNA sequences for the eukaryotic genes involved in metabolism (energy use and construction of molecules) resemble bacterial genes. Cell biologists are pursuing the information necessary to test other hypotheses. If the

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232 eukaryotes  232

first entry

nucleus began as an extension of a flagellum, which began as an embedded spirochete, as proposed by Margulis and associates, then there should be significant similarities between the proteins that move the chromosomes during cell division, the proteins of eukaryotic flagella, and the proteins of spirochetes. If the first eukaryotic cells evolved from planctomycete bacteria, these bacteria should have a closer genetic resemblance to eukaryotes than do other kinds of bacteria. According to two of these views, the first nucleated cell was a chimera, a fusion of two different life-forms. In Greek mythology, a chimera was a combination of two different animals. While it is impossible for two complex multicellular organisms to merge into one, it happens even today on the cellular level and may have been the source of the nucleus. This would mean that the origin of many structures found in the eukaryotic cell occurred through symbiogenesis. If this is the case, the reason that scientists have not found a gradual series of transitional forms in the evolution of eukaryotic cell structures is because they never existed. The evolutionary patterns constructed from DNA analysis show that the three main branches of life are the archaea, bacteria, and eukaryotes. The branches within the eukaryotes cannot be clearly distinguished from one another. Most of the diversity of eukaryotes exists among the primarily singlecelled organisms usually called protists (formerly “algae” and “protozoans”). Being usually small, of relatively simple structure, and living in places humans seldom look (such as oceans, ponds, soil, and inside of animal guts), protists have been less intensively studied than plants and animals. Not only is less known about protists than about plants and animals, but new groups of protists, including some as small as bacteria, continue to be discovered.

Each such discovery has the possibility of changing scientific understanding of eukaryotic evolutionary relationships. Many eukaryotes are multicellular. Multicellularity evolved several times independently (see table): in brown algae, in red algae, in fungi, in plants, and in animals. At least twice, protists have evolved temporary multicellularity: in the cellular and the plasmodial slime molds. Each lineage that contains multicellular organisms also contains single-celled organisms. Some surprises have come from the study of protists. One surprise is that the evolution of chloroplasts from cyanobacteria occurred only in the lineage leading to red algae, green algae, and plants. There are other photosynthetic eukaryotes, such as the brown algae and diatoms in one lineage, some euglenas in another lineage, and dinoflagellates in yet another lineage. The chloroplasts in these last three lineages did not evolve directly from cyanobacteria. Instead, they are the evolutionary descendants of eukaryotic algae. This means that eukaryotes such as brown algae and dinoflagellates do not consist of cells within cells, but rather cells within cells within cells! Another surprise is that fungi and animals are more closely related to each other than to the other eukaryotes. Within the Linnaean system of classification, there are four kingdoms of eukaryotes: protists, fungi, plants, and animals. In this classification, protists are the eukaryotic organisms that do not produce complex tissues. But complex tissues have evolved separately in fungus, plant, and animal lineages. The fungi, plants, and animals are therefore branches of the protist kingdom. The origin of the complex eukaryotic cell allowed an explosion of evolutionary diversification and novelty. Although some bacteria can form mul-

Major Lineages of Eukaryotes Lineage

Examples

Excavates

Single-celled protists without mitochondria (e.g., Giardia)

Discicristates

Euglenas, parasitic protists, cellular slime molds

Heterokonts

Brown algae, diatoms, water “molds”

Alveolates

Ciliates, dinoflagellates, parasitic protists (e.g., Plasmodium)

Cercozoans

Shelled amoebae (e.g., foraminiferans)

Green eukaryotes

Red algae, green algae, plants

Amoebozoans

Plasmodial slime molds, lobed amoebas

Opisthokonts

Choanoflagellates, fungi, animals

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extinction  233 ticellular filaments or clusters, it appears that only eukaryotes can form complex multicellular organisms. The early evolution of eukaryotes occurred during Precambrian time and left few fossils. Today scientists attempt to reconstruct these evolutionary events, and to do so they must study the organisms that most closely resemble the earliest eukaryotes: the protists. See also animals; archaea; bacteria; fungi; Margulis, Lynn; protists; seedless plants; seed plants; symbiogenesis Further Reading Baldauf, S. L. “The deep roots of eukaryotes.” Science 300 (2003): 1,703–1,706. Kurland, G. C., L. J. Collins, and D. Penny. “Genomics and the irreducible nature of eukaryote cells.” Science 312 (2006): 1,011–1,014. Lane, Nick. Power, Sex, and Suicide: Mitochondria and the Meaning of Life. New York: Oxford University Press, 2005. Margulis, Lynn, Michael F. Dolan, and Ricardo Guerrero. “The chimeric eukaryote: origin of the nucleus from the karyomastigont in amitochondriate protists.” Proceedings of the National Academy of Sciences USA 97 (2000): 6,954–6,959. ———, ———, and Jessica H. Whiteside. “ ‘Imperfections and oddities’ in the origin of the nucleus.” Paleobiology 31 (2005): 175–191. Morrison, Hilary G., et al. “Genomic minimalism in the early diverging intestinal parasite Giardia lamblia.” Science 317 (2007): 1,921–1,926. Summary by Keeling, Patrick J. “Deep questions in the tree of life.” Science 317 (2007): 1,875–1,876. Pennisi, Elizabeth. “The birth of the nucleus.” Science 305 (2004): 766–768. Zimmer, Carl. “On the origin of eukaryotes.” Science 325 (2009): 666–668.

eutrophication  See rivers, streams, ponds, and lakes.

extinction  Extinction is the disappearance of a species. It usually involves (1) a decrease in population sizes within a species and (2) a decrease in genetic diversity within a species. These two processes are related, since small populations usually have less genetic diversity than large populations. Extinction usually occurs for a variety of interrelated reasons and occurs one species at a time. When a large number of species becomes extinct at the same time for the same reason, a mass extinction event is said to have occurred. Five mass extinctions have occurred during the history of life and

xviii+598_Biodiversity_F.indd 233

have been important in the pattern of evolutionary history. Many biologists consider that a sixth mass extinction of species is now occurring, largely due to human disturbance of the environment, and that the mass extinction now under way may well prove to be the biggest in the history of life on Earth. Changes in the environment, whether naturally occurring or caused by human activity, may impair the ability of organisms to reproduce; this will cause populations to decline. A species with a small number of populations is in much greater danger of extinction than a species with larger population number and size. For example, a plant species that is limited to a single locality may become extinct if that locality is disturbed by fire, flood, or human activity. The bush Franklinia alatamaha was discovered by the American botanists John and William Bartram in the 18th century. It was growing in just one location in the mountains of the colony of Georgia, on the plateau adjacent to the Altamaha River. The Bartrams took cuttings from these bushes and planted them in a garden; descendants of these bushes are still alive in gardens throughout the United States and Europe. The wild population has disappeared, perhaps when the forest that contained it was cleared for cultivation, perhaps even by a single farmer. The tree Ginkgo biloba was very nearly extinct in its habitat, the forests of north central China. Buddhist priests planted specimens of this tree in their monasteries. Ginkgo trees are now abundant throughout the world where they have been planted in cities and more recently in plantations for the production of medicinal compounds. Franklinias and ginkgos survive today largely because a small sample of them was rescued from their very small and vulnerable wild populations. Loss of genetic diversity also makes a species more vulnerable to extinction. A species with fewer genes is less capable of responding through natural selection to changes in the environment. A species with little diversity of genes that confer resistance to specific diseases runs the risk of being devastated by a disease for which it has no resistance. In addition, the loss of genetic diversity can lead to inbreeding. Within most populations, deadly genetic mutations are hidden in the cells of even apparently healthy individuals. In small populations, the chance that two closely related individuals will mate and produce offspring is greater than in large populations. If two individuals that have the same hidden mutations mate, these mutations may show up in double dose in the offspring, causing the offspring to die before or shortly after birth. This can be a problem even in a population that has begun to recover from a previous decline. The number of individuals in the population may grow but the number of genes will

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234 extinction  234 not, except over a very long period of time. A loss of genetic diversity in the past (a genetic bottleneck) can condemn a population to reduced survival ability even if circumstances should become favorable to its growth. An example of a species that is near extinction because of a genetic bottleneck is the nene, or Hawaiian goose (Nesochen sandiviensis). Due to the efforts of conservation workers and public cooperation, populations of the nene (the Hawaiian state bird) are growing, following its near extinction in the first half of the 20th century. DNA studies that compare modern birds with birds preserved in museums indicate that modern populations of the nene have much lower genetic diversity than did populations in the 19th century. Many goslings, whether hatched in captivity or in the wild, have birth defects, and many of them die. This is the same reason that small, isolated human populations also exhibit traits that remain hidden in larger populations, for example extra fingers and toes (polydactyly) and metabolic disorders. A third risk factor for extinction is the dependence of the species on other species. The fate of a species of butterfly that depends on just one host plant for its caterpillars depends on the fortunes of that host plant. Rescuing species from extinction may involve a lot more than just making sure the survivors have a place to live. An example is the American chestnut (Castanea dentata). Once a dominant tree in Appalachian forests, nearly all adult American chestnut trees were killed by the fungus Cryphonectria (Endothia) parasitica, which was accidentally introduced from Europe near the beginning of the 20th century. Plenty of American chestnuts remain alive as saplings. They never produce seeds, however, because as soon as the saplings become large enough to have mature bark, the fungus that decimated their original populations kills the sapling. New saplings resprout from the rootstock. A few mature individuals survive in areas where they were planted far from and before the fungus outbreak occurred. Bringing the chestnut back from the brink of extinction involves locating or breeding individuals that are resistant to the fungus. Rescuing animal species from extinction poses its own set of challenges. Reintroduction of zoo animals into the wild has proven largely unsuccessful because animal species that have lived in zoos for several generations have forgotten how to live in the wild and have lost their fear of humans. This is because a lot of animal behavior is passed socially, not genetically, from one generation to the next. On the other hand, some types of natural animal behavior directly hinder the recovery of endangered

xviii+598_Biodiversity_F.indd 234

first entry species. The magpie robin of the Seychelle Islands (Copsychus sechellarum) consisted of only seven breeding pairs in 1988. Its population recovered to about 150 but could not exceed this number, since the dominant breeding pairs suppressed the reproduction of other pairs. Saving species from extinction can provide a tremendous benefit to science and to human well-being. Plant breeders, for example, wish to introduce genes for drought resistance into maize (Zea mays; also called corn) raised in the United States. Droughtresistant genes are available in Tripsacum grass, but Tripsacum cannot crossbreed with maize. A wild species of perennial maize, Zea diploperennis, can crossbreed with both Tripsacum and Zea mays and can thereby act as the bridge for introducing Tripsacum genes into agricultural maize populations. Zea diploperennis was almost extinct when botanist Hugh Iltis discovered it in the 20th century. Most species have not been identified, and many of these species will become extinct before they are identified. Currently, most extinctions occur because of the destruction of habitats, due to urban sprawl, agriculture, soil erosion, and the spread of deserts. Nearly half of the terrestrial surface of the Earth has been significantly altered by humans. Few wild species can survive in places completely changed by humans, and some wild species will become extinct even in places only slightly altered by humans. Most extinctions occur due to habitat destruction in areas with very high species diversity, known as “biodiversity hot spots.” In the future, the greatest cause of extinction will be global warming, which has already begun to alter the climatic conditions in nearly all habitats. A severe change in climate can decimate the species in a habitat, even one set aside to preserve those very species, as surely as can a bulldozer or a tractor. Hunting seldom causes extinction, but there are some exceptions. The Pleistocene extinction may have been caused by overhunting by the first humans to arrive in North America, with similar extinctions in New Zealand and Madagascar. The dodo (Raphus cucullatus) was hunted to extinction on the Indian Ocean island of Mauritius. The passenger pigeon (Ectopistes migratorius), of which billions once darkened the skies and broke the tree boughs of eastern North America, was hunted almost to extinction. Once their populations were small, other processes led to their final disappearance. The last one, a female named Martha, died in the Cincinnati Zoo on September 1, 1914. White Americans with rifles attempted to drive the bison to extinction, partly to undermine the food base of the Native Americans and make them easier to conquer, but some bison were spared, and today their numbers are increasing.

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extinction  235 On the other hand, it is often difficult to prove that a species has become extinct. The fact that experts cannot find them is pretty good evidence of extinction, but one never knows if a golden toad (Bufo periglenes, one of the few species that many scientists claim have become extinct due directly or indirectly to global warming) might turn up somewhere that the experts have not looked. One can be fairly certain that the passenger pigeon is extinct, for surely one would have shown up during the century since Martha died. Mass extinctions occur when major global events cause the simultaneous extinctions of many species. Five mass extinctions have occurred during the history of the Earth and, according to many scientists, a sixth mass extinction is now under way as a result of human impacts upon the global ecosystem. The background rate of extinction, based on the fossil record, is about one species out of 1 million each year. Current extinction rates are at least 100 times as great as this. Many species are almost extinct because their populations are too small. Of the 136 species of native Hawaiian birds, many have become extinct; only 11 of them have populations large enough to ensure survival in the near future. Of the 980 species of native Hawaiian plants, 84 have become extinct, and 133 have populations that consist of fewer than 100 individuals. While the definition of extinction is fairly clear, the definition of an endangered species is less clear. Government agencies and conservation organizations have adopted guidelines to help identify which species are most in danger of extinction. It is an important matter, as an endangered status may qualify the species for protection at some cost to the public and with some restrictions to private land owners. The International Union for Conservation of Nature (IUCN) publishes the IUCN Red List of Threatened Species. A species is considered to be critically threatened if ●●

●● ●●

more than 80 percent of the population has been lost over the last decade or three generations, whichever is longer; or fewer than 250 individuals remain; or less than about four square miles (about 10 square kilometers) of habitat remains.

As of 2010, the IUCN red list had 47,677 species known to be at risk of extinction. This includes 12 percent of bird species; 21 percent of mammal species; 27 percent of reef-building corals; and 30 percent of conifers and cycads. Some species exist as just a single individual. A single wild tree of Carpinus putoensis remains in the wild, on Mount Froding on Putuo Island in China’s

xviii+598_Biodiversity_F.indd 235

Zhoushan Archipelago. A tree hibiscus (Hibiscus liliflorus) of Rodrigues Island became extinct after the single surviving individual died. The story of lonely Martha the passenger pigeon continues to be repeated. In addition to all the other problems faced by endangered species, their novelty and rarity attract collectors. The global black market trade in endangered species is worth $10 billion a year, making it second only to drugs and guns. The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) coordinates efforts of different countries in an attempt to stop the traffic in endangered species. The rhinoceros is threatened with extinction because of the belief that powder made from its horn has medicinal properties and because the horn is used for handles of traditional Arabic jambiya daggers. Sometimes individuals of endangered species are killed out of desperation. Hunger, caused by among other things a collapse in the availability of fish, has driven many Africans to eat bushmeat, which is frequently obtained from endangered species of primates, including gorillas and chimpanzees. In 1993, the United Nations adopted the Convention on Biological Diversity, which included agreements to protect endangered species. According to associates of the United Nations Environment Programme (UNEP) World Conservation Monitoring Centre, the rate of biodiversity loss has not decreased in recent years, despite such international efforts and agreements. There have been consistent increases in protection, as indicated by extent of protected areas and sustainable forests. However, the pressures upon biodiversity are increasing (for example, ecological footprint, pollution, invasive species, and overfishing) and the indicators of biodiversity (such as forest and coral reef extent) are decreasing. Moreover, in most cases, these trends are not very different, per year, since 2000 than since 1970—and in some cases, biodiversity is faring even worse (see table on page 236). This indicates that the threat of extinction has not declined in the most recent decade, despite great increases in conservation efforts—probably because population and resource pressures are greater than ever and overwhelm conservation efforts. The extinction of just one species may not seem significant in the context of a million species. But extinctions keep adding up. Evolutionary biologist Edward O. Wilson says that, through these extinctions, nature is dying a “death of a thousand cuts.” Conservationists frequently say that “extinction is forever.” This statement is obviously true for a species—once it is gone it cannot come back—but is also true of the genetic diversity within a species.

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236 extinction  236

first entry

Trends of Global Biodiversity and Threats to It, Since 1970,   and During the 1990s (Since the Adoption of the United Nations   Convention on Biological Diversity) Average Annual Percent Change since 1970*

Average Annual Percent Change since 2000

-1.0

-0.9

-0.1

+0.6

-2.0

-2.4

-0.3

-0.5

+0.1

+0.1

Forest Extent

-0.2

-0.2

Mangrove Extent

-0.8

-0.7

Seagrass Extent

-0.7

-2.4

Coral Reef Condition (6)

-1.8

+0.2

Water Quality Index (7)

0

-0.2

Number of Biodiversity Indicators Declining

8 of 10

7 of 10

Ecological Footprint (8)

+1.6

+2.1

Nitrogen Deposition Rate

+0.9

+0.2

Number of Alien Species in Europe

+1.5

+1.1

Exploitation of fish stocks (percent)

+0.9

+1.2

Climatic Impact Indicator (9)

+1.2

+1.2

Number of Pressure Indicators Increasing

5 of 5

5 of 5

+4.7

+2.4

+3.4

+0.8

+46

+20

Signatories to Invasive Species Policy

+9.1

+5.1

Invasive Species Policy Adoption

+13

+4.1

Development Assistance for CBD (12)

+8.3

+8.4

Number of Rescue Indicators Increasing

6 of 6

6 of 6

Measures Indicators of Biodiversity Living Planet Index (1) Wild Bird Index (2) Waterbird Population Status Index Red List Index

(3)

(4)

Marine Trophic Index

(5)

Pressures upon Biodiversity

Attempts to Rescue Biodiversity Extent of Protected Areas (PA) PA Coverage of Threatened Sites Area of Certified Forest

(10)

(11)

*Or since earliest date after 1970 for which data are available (1) Mean population trends of vertebrates (2) Population trends of habitat specialists in Europe and North America (3) Changes in shorebird populations (4) Extinction risks of mammals, birds, amphibians, corals (5) Shift in fishing from top predators to fishes lower on the food chain (6) Live hard coral cover (7) Physical and chemical quality of freshwater (8) Humanity’s resource consumption (9) Change of European bird populations in direction expected from global warming (10) Bird Areas and Alliance for Zero Extinction Sites (11) Certified by Forest Stewardship Council as sustainably managed (12) International development assistance for Convention on Biological Diversity Note: From Butchart (United Nations Environment Programme World Conservation Monitoring Centre)

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extinction  237 See also biodiversity, resources for agriculture; biodiversity, resources for medicine; greenhouse effect; mass extinctions; population genetics. Further Reading American Chestnut Foundation. “American Chestnut Foundation.” Available online. URL: http://www.acf. org. Accessed May 13, 2011. Animal Welfare Institute. “Endangered Species Handbook.” Available online. URL: http://www.endangered specieshandbook.org/dinos.php. Accessed May 13, 2011. Barrett, Meredith A., et al. “CITES designation for endangered rosewood in Madagascar.” Science 328 (2010): 1,109–1,110. Barrow, Mark V., Jr. Nature’s Ghosts: Confronting Extinction from the Age of Jefferson to the Age of Ecology. Chicago, Ill.: University of Chicago Press, 2009. Brook, B. W., et al. “Catastrophic extinctions follow deforestation in Singapore.” Nature 424 (2003): 420–423. Bushmeat Crisis Task Force. “Bushmeat Crisis Task Force.” Available online. URL: http://www.bushmeat.org. Accessed May 13, 2011. Butchart, Stuart H. M., et al. “Global biodiversity: Indicators of recent declines.” Science 328 (2010): 1,164–1,168. Cardillo, Marcel, et al. “Multiple causes of high extinction risk in large mammal species.” Science 309 (2005): 1,239–1,241. Collins, James P., and Martha L. Crump. Extinction in Our Times: Global Amphibian Decline. New York: Oxford University Press, 2009. Convention on International Trade in Endangered Species (CITES). “Convention on International Trade in Endangered Species of Wild Fauna and Flora.” Available online. URL: http://www.cites.org. Accessed February 25, 2011.

xviii+598_Biodiversity_F.indd 237

International Union for the Conservation of Nature. “IUCN Red List of Threatened Species.” Available online. URL: http://www.iucnredlist.org. Accessed May 13, 2011. Magurran, Anne E. “Threats to freshwater fish.” Science 325 (2009): 1,215–1,216. Marton-Lefèvre, Julia. “Biodiversity is our life.” Science 327 (2010): 1,179. McGavin, George C. Endangered: Wildlife on the Brink of Extinction. Richmond Hill, Ont.: Firefly Books, 2006. Menino, Holly. Darwin’s Fox and My Coyote: Why Science Alone Can’t Win the Race to Save Wild Animals. Charlottesville, Va.: University of Virginia Press, 2008. Morell, Virginia. “Into the wild: Reintroduced animals face daunting odds.” Science 320 (2008): 742–743. Myers, Norman, and Andrew Knoll. “The biotic crisis and the future of evolution.” Proceedings of the National Academy of Sciences 98 (2001): 5,389–5,392. Paddle, Robert. The Last Tasmanian Tiger: The History and Extinction of the Thylacine. New York: Cambridge University Press, 2002. Passenger Pigeon Society. “Passenger Pigeon Society.” Available online. URL: http://www.passengerpigeon. org. Accessed May 13, 2011. Pimm, Stuart L. “The future of biodiversity.” Science 269 (1995): 347–350. ———, Peter Raven, Alan Peterson, Çag˘an H. S¸ekerciog˘lu, and Paul R. Ehrlich. “Human impacts on the rates of recent, present, and future bird extinctions.” Proceedings of the National Academy of Sciences USA 103 (2006): 10,941–10,946. Pounds, J. A., et al. “Widespread amphibian extinction from epidemic disease driven by global warming.” Nature 439 (2006): 161–167. Thomas, J. A., et al. “Successful conservation of a threatened Maculinea butterfly.” Science 325 (2009): 80–83. Wright, Karen. “Return of the king of trees.” Discover, May 2004, 58–61.

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F federal  government  role  in  conservation  (united states)  the federal government of the

United States has had a larger role in the management of natural resources and the preservation of wilderness and biodiversity than any other institution in the history of the world. the government acquired this role by historical accident rather than by choice. after the american Revolution, most americans considered it the manifest destiny of the United States to rule the entire north american continent between the borders of canada and Mexico. the american government acquired territories both through purchases from France (the louisiana Purchase of 1803) and Mexico (the Gadsden Purchase of 1854) and by war against Mexico and against native american nations. the result was that the government had millions of square miles of public lands under its control. the General land Office was in the Department of the treasury and the indian affairs Office was part of the Department of War until congress created the Department of the interior to oversee all of the federal land and its native inhabitants in 1849. today, the Department of the interior still oversees about one-fi fth of the land area of the United States. the Department of agriculture oversees the national forests. european colonists had driven many native american nations to extinction by massacre and disease before the american Revolution, but hundreds of native nations remained in control of their ancestral lands west of the american frontier. the United States military waged war against many of these nations. after defeating them, the United States government would establish treaties that allowed the nations to keep part of their land—and would then ignore the treaties and take the land. in this

way, native american nations were reduced to poor and generally landless tribes on reservations. in one case, the United States government expelled native americans against the express order of the Supreme court. the cherokee nation sued the United States to prevent its expropriation of their appalachian homelands; the Supreme court, under chief Justice John Marshall, ruled in favor of the cherokees. But President andrew Jackson disregarded the Supreme court order, saying, “let John Marshall enforce it,” and forced the cherokees westward to indian territory (now Oklahoma) in 1835. During the 20th century, some tribes were partially restored to their ancestral lands; for example, some navahos and apaches returned to arizona from Oklahoma. to this day, native american communities remain generally poor, and in some cases (such as northeastern Oklahoma) their land is severely polluted by industrial activities from which the native communities received no profit. Pioneers could generally acquire land from which the government had displaced the native residents by moving to it and establishing residency. Proof of residence included cutting down trees and planting farms or orchards. this right was formalized in the 1862 Homestead act, which permitted any family to establish a 160-acre (65 ha) farm. During the second half of the 19th century, the federal government gave thousands of square miles of land to railroad, lumber, and mining corporations at minimal charge. the railroads were built primarily to establish networks of towns across the continent, connecting the eastern states with california, which had grown to statehood during the gold rush that began in 1849. even when corporations paid the government, it was still practically a giveaway. in the fi rst decade of the

238

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federal government role in conservation (United States)  239 20th century, the Weyerhauser Corporation paid the government a dime a tree for lumber from the lush forests around Mount St. Helens and Mount Rainier in Washington State. Wholesale destruction of natural resources was the rule of the day in the late 19th century. Entire forests were clear-cut and abandoned. Lumberjacks cut down the giant sequoias and coast redwoods of California as fast as they could. People rode trains out into the prairie for the express purpose of shooting entire herds of bison and leaving the carcasses to rot. The federal government supported the bison massacres because they undermined the subsistence economy of the last Native American nations to avoid subjugation. A few pioneers looked up long enough to notice that the land that they were destroying was beautiful, often breathtakingly so. There seemed, however, to be no way to preserve any of it. Geologist Ferdinand V. Hayden conducted a geological expedition in 1871 to the Yellowstone Basin of Wyoming and made a detailed map of its natural wonders, including geysers and hot springs. His documentation included large photographs by photographer William Henry Jackson and huge paintings by American landscape artist Thomas Moran. It was the pictures as much as the facts that convinced Congress in 1872 to withdraw the land from public auction and make it into the first national park in the United States and in the world. The major purpose of the park was not to preserve natural habitats or species but to create a tourist destination for people riding the newly built railroads. It was not until the last decade of the 19th century that the federal government began to preserve a serious amount of public land. Prior to that time the General Land Office transferred public land to large railroad, timber, and mining corporations for a minimal price or no price at all. But a clause in an 1891 act of Congress gave the president the power to set aside forestlands. In 1897, just 10 days before leaving office, President Grover Cleveland used that power to protect 21 million acres (8.4 million hectares) of forestland in the western United States. Congress quickly passed a bill to nullify this protection—a bill that Cleveland vetoed as he walked out of the door. The incoming president, William McKinley, transferred the land to the General Land Office, which continued the land giveaway. President McKinley was assassinated in 1901, and his vice president, Theodore Roosevelt, took his place. Roosevelt was an avid outdoorsman and nature enthusiast. He formed the United States Forest Service in 1905 with Gifford Pinchot as its first director. With the establishment of the national forests, the federal government retained ownership of

xviii+598_Biodiversity_F.indd 239

the land, established the rules for how it could be used, and collected fees on an ongoing basis for sustainable resource extraction. In 1907, a congressional bill forbade the further creation of government forest preserves. In the last days before the bill took effect, Roosevelt and Pinchot set aside 16 million acres (65,000 sq km) of forestland. During the dust bowl era, the federal government acquired much eroded land in the western Great Plains that had been abandoned by farmers, and this land is today the National Grasslands.

Public Lands in the United States Most of the public lands (owned by the federal government) are managed by the following agencies in the Department of the Interior (DOI), Department of Defense (DOD), and Department of Agriculture (DOA): ●●

●●

National Park Service (DOI). The NPS manages national parks, national monuments, and other locations whose principal purpose is preservation of natural landscapes and wildlife and public recreation (see table on pages 240–241). Yellowstone was the only national park for almost two decades. Three more were created before the end of the 19th century: Yosemite National Park and Sequoia National Park (California) in 1890, and Mount Rainier National Park (Washington) in 1899. Congress passed a national parks bill, formalizing the role of ­national parks, in 1899. Twenty-two more national parks were created between 1900 and 1935. There are now 58 national parks in the United States. The national park Service was created as an agency within the DOI in 1916 by a bill that required the agency “to conserve the scenery and the natural and historic objects and wildlife therein, and to provide for the enjoyment of the same in such manner and by such means as will leave them unimpaired for the enjoyment of future generations.” National parks are, therefore, intended for the preservation of nature and of historically important sites. National monuments are lands that are not considered quite significant enough to qualify for national park status, but in recent decades many national monuments (such as Death Valley) have become national parks. United States Forest Service (DOA).  National parks are intended for preservation, following the vision of American conservationist John Muir. In contrast, the national forests are intended for managed

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240 federal government role in conservation (United States)  240

first entry

National Parks in the United States and the   Terrestrial Plant Communities that They Protect National Park (location)

Principal Terrestrial Plant Communities

Acadia (Maine)

Boreal forest; temperate deciduous forest

American Samoa

Tropical rain forest

Arches (Utah)

Desert, cool

Badlands (South Dakota)

Grassland (shortgrass prairie)

Big Bend (Texas)

Desert, warm

Biscayne (Florida)

Marshes and swamps

Black Canyon of the Gunnison (Colorado)

Temperate coniferous forest

Bryce Canyon (Utah)

Temperate coniferous forest

Canyonlands (Utah)

Desert, cool

Capitol Reef (Utah)

Desert, cool

Carlsbad Caverns (New Mexico)

Desert, warm

Channel Islands (California)

Grassland; chaparral

Congaree (South Carolina)

Temperate deciduous forest

Crater Lake (Oregon)

Subalpine forest

Cuyahoga Valley (Ohio)

Temperate deciduous forest

Death Valley (California)

Desert, warm

Denali (Alaska)

Boreal forest; arctic tundra

Dry Tortugas (Florida) Everglades (Florida)

Marshes and swamps

Gates of the Arctic (Alaska)

Boreal forest; arctic tundra

Glacier (Montana)

Boreal forest; alpine tundra

Glacier Bay (Alaska)

Boreal forest; temperate coniferous forest

Grand Canyon (Arizona)

Temperate coniferous forest; desert, cool

Grand Teton (Wyoming)

Subalpine forest; desert, cool

Great Basin (Nevada)

Desert, cool; temperate coniferous forest

Great Sand Dunes (Colorado)

Temperate coniferous forest

Great Smoky Mountains (North Carolina, Tennessee)

Temperate deciduous forest, subalpine forest

Guadalupe Mountains (Texas)

Desert, warm

Haleakala (Hawaii)

Tropical rain forest

Hawaii Volcanoes (Hawaii)

Tropical rain forest

Hot Springs (Arkansas)

Temperate deciduous forest

Isle Royale (Michigan)

Boreal forest

Joshua Tree (California)

Desert, warm

Katmai (Alaska)

Boreal forest; alpine tundra

Kenai Fjords (Alaska)

Boreal forest; alpine tundra

Kings Canyon (California)

Temperate coniferous forest; subalpine forest

Kobuk Valley (Alaska)

Boreal forest; arctic tundra

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federal government role in conservation (United States)  241 National Park (location)

Principal Terrestrial Plant Communities

Lake Clark (Alaska)

Boreal forest; alpine tundra

Lassen Volcanic (California)

Subalpine forest; alpine tundra

Mammoth Cave (Kentucky)

Temperate deciduous forest

Mesa Verde (Colorado)

Temperate coniferous forest

Mount Rainier (Washington)

Subalpine forest; alpine tundra

North Cascades (Washington)

Subalpine forest; alpine tundra

Olympic National Park (Washington)

Temperate coniferous forest; subalpine forest

Petrified Forest (Arizona)

Desert, warm

Redwood (California)

Temperate coniferous forest

Rocky Mountain (Colorado)

Subalpine forest, alpine tundra

Saguaro (Arizona)

Desert, warm

Sequoia (California)

Temperate coniferous forest; subalpine forest; alpine tundra

Shenandoah (Virginia)

Temperate deciduous forest

Theodore Roosevelt (North Dakota)

Grassland (shortgrass prairie)

Virgin Islands

Tropical rain forest

Voyageurs (Minnesota)

Boreal forest

Wind Cave (South Dakota)

Temperate coniferous forest

Wrangell-St. Elias (Alaska)

Boreal forest; subalpine tundra

Yellowstone (Wyoming)

Subalpine forest; alpine tundra

Yosemite (California)

Temperate coniferous forest; subalpine forest

Zion (Utah)

Desert, cool

●●

use, following the vision of American forester Gifford Pinchot. The national forest slogan is “Land of Many Uses,” of which recreation and protection of species and habitats is just one. Timber and mineral extraction is permitted from national forests, and they contain many private landholdings. There are 155 national forests. The federal government controls which trees can be removed and how. For example, timber extraction, but not of giant sequoia trees, is permitted in Sequoia National Forest in California. Bureau of Land Management (DOI). The BLM manages hundreds of thousands of square miles of woodland, grassland, and desert in the western United States. One example is the National Grasslands. The National Grasslands system began when the federal government bought eroded land from farmers who moved out of the western Great Plains during the dust bowl of the 1930s. Today, the government leases most

xviii+598_Biodiversity_F.indd 241

●●

●●

of these grasslands to ranchers for cattle grazing. The federal government sets conservation rules for these lands: For example, they control the number of cattle and the conservation of endangered black-footed ferrets in the Buffalo Gap National Grassland in South Dakota. Fish and Wildlife Service (DOI). The FWS oversees the system of National Wildlife Refuges. They are small areas set aside as habitat for wildlife. There are 551 National Wildlife Refuges and 37 wetland management districts in the National Wildlife Refuge system. The first National Wildlife Refuge was Pelican Island, off the coast of Florida. It was created by President Theodore Roosevelt in 1903. He asked his advisers if there was any law that prohibited him from establishing this refuge. Hearing no objections, Roosevelt said, “Then I do so declare it.” Department of Defense.  Military bases around the United States contain thousands of square miles of uninhabited and largely

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242 federal government role in conservation (United States)  242

●●

●●

natural land. Since the military uses these lands for military training and as bombing ranges, they are not undisturbed, but there are no trespassers. In recent decades, the Department of Defense has made serious efforts to protect habitats and wildlife in these areas as far as is possible consistent with military uses, and scientific research is often conducted on these lands. Army Corps of Engineers (DOD).  Beginning in the 1930s, the federal government used federal land and acquired private land to create reservoirs for flood control. Because reservoirs get larger as they store floodwater, the Army Corps has also acquired much of the land around the margins of the reservoirs. Much of this land is leased for limited recreational development or used for ecological research. Bureau of Reclamation (DOI). This government agency, like the Army Corps, created reservoirs, but with a different purpose: the development of irrigation.

In addition, there are 756 Wilderness Areas. The Wilderness Act of 1964 gave the federal government the power to designate Wilderness Areas within federal lands that were already protected by one of the foregoing agencies. For example, Black Elk Wilderness Area was established within the Black Hills National Forest. Wilderness Areas have no development and only primitive trail access.

Federal Jurisdiction in the Control of Environmental Problems During the 20th century, it became apparent that many environmental problems could not be solved by uncoordinated actions of state and local governments or private corporations. Primary examples are soil erosion, water resources, pollution, and endangered species. Soil erosion  During the dust bowl of the late 1920s and 1930s, millions of tons of topsoil from the western great plains of the United States blew for thousands of miles in the air, leaving a withered and almost sterile substrate that would grow very little food or forage. In many Midwestern towns, midday became as black as night, and some people even died from the inhalation of dust. This was at the end of a long drought; but the dust storms were not completely the fault of the drought. They were also the result of overgrazing and excessive plowing, which left the soil that could otherwise have survived a drought vulnerable to the relentless wind. In April 1935, during the height of the dust bowl, soil scientist Hugh Bennett met with the U.S.

xviii+598_Biodiversity_F.indd 242

first entry Senate Public Lands Committee. He wanted to convince them to create a government agency to combat soil erosion. When the clouds of dust blew over Washington D.C., he invited the senators to look out the window. They saw the nation’s farmlands, upon which both the present and the future of the country depended, blowing out to sea. The Senate established the Soil Conservation Service (now the Natural Resources Conservation Service) of the U.S. Department of Agriculture on April 27, 1935. This agency helps farmers to incorporate new techniques that will reduce the loss of topsoil to the forces of wind and rain. Although cooperation is voluntary, nearly every county in the United States is also a Soil Conservation District. Water resources.  During the 20th century, the federal government also began to assume an important role in the management of water resources, primarily by the construction of large dams, which not only created reservoirs but also electricity. Dam construction was a major component of federal job creation during the depression. As explained previously, the Army Corps of Engineers constructed dams that were primarily intended for flood control, while the Bureau of Reclamation built dams that fed into irrigation systems. Aside from this, however, water resource policy in the United States, and the federal government’s role in it, are often unclear. For example, the Tarrant Regional Water District (Fort Worth, Texas) sued the state of Oklahoma in 2007 because, it claimed, Oklahoma’s moratorium on out-of-state water sales violated the commerce clause of the Constitution. The case continues in court as of 2011. Pollution and endangered species. Environmental problems such as pollution went largely unchecked into the 1960s. A government biologist, Rachel Carson, wrote a book in 1962 that quickly gained national and international attention. Silent Spring presented extensive documentation that the widespread use of pesticides on the American landscape was producing severe pollution, much of which was concentrated up the food chain and killing unintended targets such as birds (hence the title of her book). Chemical corporations attacked her, but congressional hearings substantiated her claims. Scientists verified that birds at the top of the food chain, such as eagles and pelicans, were dying because the pesticide DDT, concentrated in their tissues, interfered with their ability to lay eggs. Carson demonstrated, moreover, that insect and other pest populations evolved resistance to those pesticides, making them ineffective. At this same time, awareness of the world population explosion was spreading. Among the iconic events that spurred environmentalism were the Santa Barbara oil spill and the Cuyahoga River in Ohio, which

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federal government role in conservation (United States)  243 caught on fire due to petroleum pollution, both in 1969. The environmentalism of the 1960s was a brief moment of intense social and political transformation, because it occurred at the same time as protests against the Vietnam War and against racial segregation. Protestors saw corporate profits as a motivating force behind pollution as well as the war. Since that time, much larger environmental disasters have failed to generate nearly as much protest. The Deepwater Horizon (BP) oil spill of 2010 is the largest environmental disaster in American history to date, yet did not have the kind of effect on national policy that the comparatively small disasters of the 1960s did. It is therefore no surprise that, in quick succession, the federal government adopted sweeping changes in environmental protection, including the following: ●●

●●

National Environmental Policy Act (NEPA).  This law, passed by Congress in 1969, created the Environmental Protection Agency (EPA), which has the authority to enforce environmental legislation. EPA monitors state and local governments and corporations for compliance with federal environmental laws and must approve Environmental Impact Statements before the federal government can undertake any significant activity that may have an impact on the environment. The EPA banned the widespread use of the pesticide DDT in 1972, allowing its use to control the spread of disease vector insects. Clean Air Act. This law, passed by Congress in 1970, required that industry, utilities, and transportation reduce air pollution. One example of a technology that arose to control air pollution is the catalytic converter. Incomplete combustion in internal combustion engines produces toxic carbon monoxide; the converter uses a palladium catalyst to make the carbon monoxide into carbon dioxide. The law, still in effect, has been very successful. Emissions of lead, primarily from gasoline, have dropped 98 percent. Emissions of sulfur dioxide, mostly from power plants, have dropped by 35 percent even though the gross domestic product has more than doubled since 1970. Emissions of carbon monoxide have dropped by 32 percent even though driving has increased 127 percent. Amendments to the act helped to reduce acid rain and fog, and in 2009 the EPA declared carbon dioxide to be a pollutant because of its role in the greenhouse effect.

xviii+598_Biodiversity_F.indd 243

●●

●●

Clean Water Act. This law, passed by Congress in 1972, prohibited pollution from point sources, that is, specific locations from which pollution was released, which includes industries and feedlots. Nonpoint sources, such as storm runoff and drainage from agricultural lands, were exempted, although a 1987 amendment required the separation of sewage from storm runoff in municipal drainage systems that had previously combined them. Endangered Species Act (ESA). This law, passed by Congress in 1973, established a mechanism by which scientific data could be gathered and used to determine which species were threatened by human activities and then to enable protection of those species. The law, administered by the FWS (on land and in freshwater) and the National Oceanic and Atmospheric Administration (in the oceans), protects not only those species but the habitats on which they depend, and for this reason many scientists consider the ESA to be the single most important mechanism for the protection of biodiversity in the United States. The purpose of the law is not, however, to identify species for permanent protection but to restore them to a nonthreatened status. Therefore, whenever an agency or a group of citizens proposes a species for federal protection under this act, they must include a recovery plan, by which the species can be brought back to safe population levels. In some high-profile cases, species that were threatened with extinction have been delisted. The FWS removed the bald eagle from federal protection in 2007, as its populations had sufficiently recovered, largely because of the disappearance of DDT from the food chain and the protection of nesting site habitats. The bald eagle continues to be protected by the Bald and Golden Eagle Protection Act of 1940 and the Migratory Bird Treaty. While this was greeted as evidence of success in conservation, the ­delisting of wolves has proven controversial, because as soon as federal protection for wolves was lifted in 2008, bands of hunters in Wyoming and Montana organized what many conservationists consider pointless slaughters.

All of these laws were enacted during the presidency of Richard Nixon, who was not a particularly passionate environmentalist. He recognized,

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244 ferns  244 ­ owever, that it was political suicide to resist the h environmental movement of the 1960s. Federal government protection of resources on public lands is imperfect. The most notorious example is the Minerals Management Service (DOI) [now the Bureau of Ocean Energy Management, Regulation and Enforcement], which regulates the leasing of public lands for coal, oil, and mineral extraction by private corporations and is responsible for collecting revenues from those corporations. In 2008, the news broke that up to one-third of the employees in the Denver office of the MMS accepted gifts (which included sex and drugs) from corporations in return for profitable leases and lax collection of fees. In 2010, the news broke of lax enforcement of safety violations by the New Orleans office of the MMS, which may have played a direct role in allowing the Deepwater Horizon oil spill to occur. Despite these scandals, public lands appear to be better protected in the United States than in many other countries. Conservationists often refer to national parks in many countries as “paper parks,” meaning that they are protected only by lines drawn on a map, not by enforcement. Although 12 percent of the Earth’s land surface has official protection, conservationists estimate that only about 0.5 percent is protected by meaningful enforcement. The United States participates in some international agreements to protect biodiversity, such as the Convention on International Trade in Endangered Species (CITES). Most of these endangered species on the international market come from outside the United States. However, there is an international market for products from some American species. For example, the eggs of paddlefish, illegally obtained in the United States by the Russian mafia, are marketed as caviar in eastern Europe. Due to limited resources and political pressure, the federal government cannot assume the complete role of protecting biodiversity. Private organizations (most notably The Nature Conservancy) purchase land or receive it by donation, then manage it to protect the integrity of the ecological communities in it. Although the federal government has only the powers delegated to it by the Constitution, it plays an overwhelming part in the protection of biodiversity, because federal lands are so extensive and because many pollution problems as well as species cross state lines. The federal government will remain the single most powerful force in biodiversity protection in the United States indefinitely into the future. It also plays an essential role by approving international agreements on biodiversity protection, pollution, and carbon emissions—and by not approving them. The single most important reason that carbon dioxide emissions have not been ade-

xviii+598_Biodiversity_F.indd 244

first entry quately controlled around the world is probably that the Republican Party has refused to allow the federal government to commit to international agreements that limit them. See also acid rain and fog; biomagnification; Carson, Rachel; endangered species; greenhouse effect; Muir, John; Pinchot, Gifford. Further Reading Brinkley, Douglas. The Wilderness Warrior: Theodore Roosevelt and the Crusade for America. New York: Harper Perennial, 2010. Duncan, Dayton, and Ken Burns. The National Parks: America’s Best Idea. New York: Knopf, 2009. Egan, Timothy. The Big Burn: Teddy Roosevelt and the Fire that Saved America. Boston: Houghton Mifflin, 2009. ———. The Worst Hard Time: The Untold Story of Those Who Survived the Great American Dust Bowl. Boston: Houghton Mifflin, 2006. Flippen, J. Brooks. Nixon and the Environment. Albuquerque: University of New Mexico Press, 2000. Fretwell, Holly Lippke. Who is Minding the Federal Estate?: Political Management of America’s Public Lands. Lanham, Md.: Lexington Books, 2009. Langholz, Jeff. “Saving nature privately.” Worldwatch, September/October 2009, 7–11. Merchant, Carolyn. American Environmental History: An Introduction. New York: Columbia University Press, 2007. Natural Resources Conservation Service. “Biography of Hugh Hammond Bennett.” Available online. URL: http://www.nrcs.usda.gov/about/history/bennett.html. Accessed June 24, 2010. Nature Conservancy. “The Nature Conservancy.” Available online. URL: http://www.nature.org. Accessed August 14, 2010. Savage, Charlie. “Sex, drug use and graft cited in Interior Department.” New York Times, September 11, 2008. Available online. URL: http://www. nytimes.com/2008/09/11/washington/11royalty. html?pagewanted=print. Accessed May 13, 2011.

ferns  See seedless plants. fishes  Fishes were the first vertebrates. There are more species of fishes than of amphibians, reptiles, birds, or mammals. They are the only group of vertebrates that is almost exclusively aquatic, which was the primitive condition of all life. When referring to more than one individual of the same species, “fish” is the correct plural; for more than one species, “fishes” is correct. Since one of the lineages of fishes evolved into the tetrapods (amphibians, reptiles,

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fishes  245 Major Groups of Fishes Lineage

Common Examples

Approximate Number of Species

Agnathans

lampreys, hagfishes

100

Batoidea

rays and skates

200

Selachimorpha

sharks

400

Holocephali

chimaeras

8

Chondrostei

sturgeons and relatives

50

Neopterygii, Holostei

gar, bowfin

8

Osteoglossomorpha

bony tongues

7

Elopomorpha

eels and relatives

600

Clupeomorpha

herring and anchovies

320

Ostariophysi

carp, catfish, minnow

ca. 8,000

Proacanthopterygii

salmon, trout, pike

540

Stenopterygii

hatchetfishes

330

Cyclosquamata

grinners

200

Scolepomorpha

lanternfishes

250

Lampridiomorpha

oarfishes

50

Polymyxiomorpha

beardfishes

10

Paracanthopterygii

anglerfishes, cod, toadfishes

ca. 12,300

Acanthopterygii

flying fishes, seahorses, flatfishes, perch, tuna

ca. 16,000

Coelacanthomorpha

coelacanths

2

Dipnoi

lungfishes

3

Chondrichthyes

Osteichthyes

Neopterygii, teleosts

Sarcopterygii

Total species

birds, mammals), “fishes” is a group that consists of all vertebrates except tetrapods; it is a paraphyletic cladistic group. All vertebrates are chordates and have evolved from invertebrate ancestors that resembled modern lancelets. Lancelets have a cartilaginous rod along the back (a notochord) in association with the main nerve cord and gill slits. All vertebrates have these features, although in most adult vertebrates the notochord is replaced by a backbone of vertebrae and may possess the gill slits only during the embryonic stage. Lancelets do not have jaws. An animal

xviii+598_Biodiversity_F.indd 245

ca. 40,000

of the Cambrian period known as Pikaia closely resembled a lancelet.

Jawless Fishes The earliest known fishes lived during the Cambrian period. Examples include Myllokunmingia and Haikouichthys, found in fossil deposits in China. These true fishes lived millions of years before Pikaia. Conodont animals also appeared in the Cambrian period and were probably fishes. Known for many years only from their fossilized eating structures, conodonts were finally identified as early Paleozoic

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246 fishes  246 fishes when a fossil was found in which numerous conodont eating structures were imbedded within a shadowy eel-like creature with large eyes at the locations where one would expect teeth to be. (Since the exact function of the “teeth” is unknown, the eating structures are called “conodont elements.”) Neither conodonts nor the fishes of the Cambrian or early Ordovician period had jaws. Two classes of modern agnathan (jawless) fishes survive: Lampreys live by sucking blood from larger fishes (see figure), and hagfishes feed on carrion. Hagfishes are classified together with the vertebrates even though they have no vertebrae, ribs, or jaws. Agnathans do not have paired fins; they have fins only along the dorsal (back) and ventral (front or belly) surfaces. They do not have eyes that are homologous to the eyes of most vertebrates; they have a pineal eye that is homologous to the pineal gland in the heads of vertebrates. They do not have scales. Lampreys dig shallow nests in the bottom of the body of water, into which they place eggs and sperm. The fertilized eggs hatch into a larval form that looks more like a lancelet than an adult lamprey. One lineage of fishes evolved jaws during the Ordovician period. This allowed a major evolutionary advancement in the efficiency of predation. Many of the earliest jawed fishes, including the placoderms, were covered with bony armor, as the predatory arms race became severe. Placoderms had bony plates in their mouths that served in place of teeth. Placoderms apparently became extinct without descendants. Other lineages of jawed fishes survived to become the Chondrichthyes (cartilaginous fishes) and the Osteichthyes (bony fishes). Modern fishes have less armor and are more maneuverable than placoderms were.

Mouth of a lamprey, which is a jawless fish that has invaded the Great Lakes. It embeds its teeth into the skins of larger fishes and sucks blood from them.  (Great Lakes Image Collection, EPA)

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first entry

Cartilaginous Fishes Cartilaginous fishes include the sharks and rays. Their skeletons consist only of cartilage. As everyone knows, they have teeth; but teeth are not bones— shark teeth are structurally similar to their scales and are often the only part of the shark to be preserved as fossils. Sharks have sharp incurved teeth, sometimes several rows of them. Sharks are continually producing new teeth; an individual shark can lose many thousands of teeth in a lifetime. Their jaws are not connected to their skulls. Shark bones do not have marrow. Their red blood cells are produced in the spleen. Sharks and rays have the following kinds of fins: ●●

●●

They have unpaired fins which include the dorsal fin along the back (top); the anal fin along the front (bottom); and the caudal fin (the tail). Rays do not have anal fins. They have paired pectoral (“breast”) and pelvic (“hip”) fins, on each side, connected to one another. The inflexible horizontal pectoral fins of sharks make them much less maneuverable than other fishes; once they have begun moving rapidly, they cannot stop or back up. The pectoral fins of rays are much more flexible.

Not all sharks are large. The dwarf lantern shark Etmopterus perryi is only seven inches (17 cm) long. The largest shark, and the largest fish, is the whale shark Rhincodon typus, which can be almost 40 feet (12 m) long. Whale sharks, like the baleen whales to which they are quite unrelated, eat only by filter feeding, though sometimes they swallow squid and fishes. Sharks have keen senses. They can detect blood at a concentration of as little as a part per million. They have good senses of sight and hearing but also rely very much on electroreception. All muscle movements produce electric fields, and sharks may have thousands of receptors that are sensitive to these electric fields. This allows sharks to find even prey that are hidden in the sand, as their muscles produce electrical fields. Hammerhead sharks have nostrils and electroreceptors spaced widely apart on the front of the head, allowing a more accurate detection of the locations of prey. Most sharks have internal fertilization, in which males transfer sperm directly to females. Some shark species have live birth, in which the embryos, connected by an umbilical cord, develop inside the mother. Live birth in sharks evolved independently from live birth in some reptiles and the live birth that characterizes most mammals. Other sharks release an egg capsule, containing the developing embryo, into the environment.

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fishes  247 Sharks have tremendous evolutionary diversity. Tiger sharks, the “garbage cans of the sea,” will eat almost anything. Biologist Edward O. Wilson reports that one giant tiger shark’s stomach contained three overcoats, a raincoat, a driver’s license, a cow’s hoof, the antlers of a deer, twelve lobsters, and a chicken coop with feathers and bones still inside. In contrast, the great white shark selectively hunts seals, sometimes catching humans by mistake. Sharks are fierce predators but not of humans; worldwide, there are about four people killed each year in unprovoked attacks. The small cookie-cutter shark takes shallow bites out of the skins of larger animals, sometimes chewing the plastic coatings of submarine navigation equipment by mistake. Chimaeras, or ghost sharks, resemble sharks but have no scales and instead of sharp teeth have three pairs of grinding tooth plates in their mouths. The largest shark to have ever lived, Carcharodon megalodon, could reach over 50 feet (16 m) in length. It became extinct only about a million and a half years ago. Rays are vertically flattened, very broad cartilaginous fishes that swim along the bottom of the sea in search of prey. Their gill slits are on the ventral surface, behind the mouth, rather than on the side of the head as in sharks. The pectoral fins can be very broad and winglike. Muscles in the “wings” of some ray species generate enough electric current to immobilize prey (these are called “electric rays”). They have tails that can be much longer than the rest of the body, and in one family of rays (the stingrays), venomous spines in the tail can kill a humansized animal.

Bony Fishes Bony fishes evolved in freshwater conditions and were restricted to freshwater for the first 160 million years of their existence. Evolutionary scientists speculate that their bones were more important as a way of storing calcium, a mineral that could be scarce in freshwater, than as a skeletal reinforcement. Today, 41 percent of fish species are freshwater species. This may have resulted because systems of lakes and rivers are largely isolated from one another, while marine fishes can swim over large areas. Bony fishes diverged into two major lineages: ●●

●●

the ray-finned fishes, which have fins reinforced with bony rays that do not correspond to the fingers or toes of other vertebrates. The major lineage of ray-finned fishes is the teleosts, which includes most modern fish species. the flesh-finned fishes diverged into two lineages: the lungfishes and the crossopterygians. Some lungfishes survive today in

xviii+598_Biodiversity_F.indd 247

shallow tropical ponds. When the ponds have water, the oxygen levels are low and the lungfishes gulp air. When the ponds dry up, the lungfishes continue to breathe while estivating in the mud. The crossopterygian fishes have bones at the bases of their fins that correspond to the one upper and two lower limb bones of tetrapods (four-legged animals). Two branches of crossopterygian fishes became the coelacanths and the tetrapods. Ray-finned fishes live in nearly all aquatic environments. They have an astonishing variety of body forms and range in size from Paedocypris progenetica, in which adults can be as small as a third of an inch (8 mm), to the ocean sunfish Mola mola, which can weigh more than 5,000 pounds (2,300 kg), and the oarfish Regalecus glesne, which can be 36 feet (11 m) long. The sturgeons and their relatives are among the most primitive bony fishes, having changed little over the last 200 million years. They do not have scales, and their skeletons are primarily cartilaginous. They spawn in freshwater, where some of them remain while others migrate to shallow marine waters. Because they grow slowly and mature after only many years, overfishing is particularly dangerous to the survival of these species. Among the relatives of sturgeons are African fishes known as bichirs. They have undergone less evolutionary change since the common ancestor of ray-finned and flesh-finned fishes; they share some characteristics with the fleshfinned fishes, including primitive lungs. The sturgeons, bichirs, and paddlefishes constitute a separate lineage (Chondrostei) from all the other ray-finned fishes (Neopterygii). The gars and bowfins are the most primitive members of the Neopterygii lineage of ray-finned fishes. Gars live in shallow water and catch prey with their sharp teeth in elongated snouts. Their swim bladders function partly as lungs. All of the Neopterygii other than gars and bowfins are teleosts. Teleost fishes can protrude their jaws outward, and (unlike other bony fishes and unlike sharks) their vertebrae do not extend into their tails. The relatively minor anatomical difference between teleosts and other fishes does not explain why teleosts have had explosive evolutionary success. Major lineages of teleosts are listed in the table on page 245, and major superorders of teleosts are presented below: Eels (see figure on page 248) are long skinny fishes that have no pelvic fins and most also lack pectoral fins. Their dorsal, anal, and caudal fins are fused into a single ribbon that runs along the entire body.

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248 fishes  248

Geometric moray eels in Rocktail Bay, Australia  (Clacherty and Associates)

The giant moray eel (Gymnothorax javanicus) can be over 12 feet (almost 4 m) in length. Eels are predators. Herrings and anchovies are small, narrow, silvery fishes that live in large groups and consume mostly plankton. Especially because of their large numbers, they are important to marine food webs. The ostariophysians are the second largest superorder of fishes and the largest group of freshwater fishes. Examples include the following: ●●

●● ●●

●●

●●

Carp and minnows Carp (Cyprinus carpio) are often farmed inland and are an important food source. Domesticated Asian koi are just colorful carp. Goldfishes (Carassius auratus) Catfishes are bottom-feeders in freshwater. Their flattened heads, lack of buoyancy, and their sensory barbels (which they use more than their small eyes) allow them to navigate on the bottoms of ponds. The front sac of the air bladder is connected by bone to the inner ear, greatly enhancing their sense of hearing. They have no scales, and many breathe through their skin. Catfishes are also farmed inland and an important food source. Electric eels (Electrophorus electricus), even though they are long and skinny, are ostariophysians, not eels. They live in rivers of the Amazon basin. The organs that produce electricity make up four-fifths of their bodies. They can produce a 500-volt charge that can kill prey. They also use electric fields for electrolocation of prey and landmarks. Piranhas have big teeth and a reputation for group ferocity against prey. However, they are not known for unprovoked attacks. Some piranha species are scavengers or eat seeds.

xviii+598_Biodiversity_F.indd 248

first entry Salmon and trout are the best-known members of the superorder Protacanthopterygii. They are predators that breed in fresh cool upstream waters. Trout remain in these waters throughout their lives, but salmon are anadromous, which means that they live in the ocean but return to the streams in which they hatched to spawn. Upstream migration of salmon (salmon runs) are dramatic, as the fish even jump up waterfalls (see figure on page 249). They have fatty adipose fins behind their dorsal fins. Most members of the superorder Stenopterygii, such as dragonfishes and hatchetfishes, live in deep oceans and have special organs that produce white, yellow, red, or purple bioluminescence. Most of the light in marine bioluminescent animals comes from bacteria. The light-producing structures of these fishes, however, are not produced by bacteria, although the presence of bacterial DNA suggests that symbiotic bacteria were originally present. Members of the superorder Paracanthopterygii include the following: ●●

●●

Toadfishes have no scales; they have large eyes on large heads. They can remain out of water for 24 hours as they push themselves across mud flats with their pectoral fins. They are omnivores but can also ambush their prey when under water. They are also able to “sing” with their air bladders and have well-developed parental care. Some have venom glands on their fins. Many anglerfishes live in deep water. They have enormous mouths and inwardly curved teeth. They can consume prey up to twice their size. They are famous for the way that they can attract their prey. The front spines of their dorsal fins develop into a filament (a “fishing pole”) from which a fleshy tip protrudes. The fleshy tip may be bioluminescent. The pole attracts other fishes which they quickly consume. They can “walk” along the bottom of the sea with modified fins.

The Acanthopterygii is the largest superorder of teleosts, containing half of the known species. Examples include: ●●

●●

Flying fishes have large pectoral fins that allow them to glide through the air near the ocean surface. They do not actually fly. They propel themselves from the water, then glide for up to 160 feet (50 m), often for a half a minute. Their pectoral fins are shapes somewhat like bird wings. Pipefishes and sea horses are long, slender fishes that swim vertically, often camou-

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fishes  249

●●

●●

flaged in the vegetation of estuaries and coastal swamps (see figure on page 250). They are among the most famous evolutionary novelties because the males have the babies. Females deposit eggs in a pouch in the male’s body, where the eggs are fertilized, develop, and hatch. Sea horses (genus Hippocampus) have plates instead of scales as their outer surface and have no tail fin. Flatfishes swim on their sides. In newly hatched flatfishes, one eye is on each side of the head but during development one eye migrates, so that both eyes are on the upper side of the fish as it lies on its side in the mud. The flatfish group contains a large number of economically important fishes, such as flounders, sole, turbot, and halibut. The perciform fishes are one of the largest groups. Among them are the gobies, tunas, and perches. Tuna have red meat because of the very high concentration of myoglobin, which supplies oxygen to the muscles. Therefore they can swim rapidly (up to 45 miles [70 km] per hour). Some tunas are warm-blooded, also due to muscular activity.

Ray-finned fishes have been the evolutionary success story of the aquatic vertebrates. In contrast, the flesh-finned fishes are far less diverse, but it is from this group that the tetrapods evolved. The sarcopterygians (flesh-finned fishes) were abundant in the middle Paleozoic era but are rare today. Their pectoral and pelvic fins have bonelike lobes that are

homologous to the limbs of tetrapods: pectoral lobes to arms or front legs, and pelvic lobes to back legs. Two lineages of sarcopterygians evolved during the Paleozoic. The coelacanths evolved and remain in deep ocean waters, while the lungfishes lived and live in shallow freshwater. Lungfishes can use their fins to push themselves from one body of shallow water to another. Their lungs allow them to breathe air while embedded in mud for long periods during the dry season and to survive in murky water that contains little dissolved oxygen. Coelacanths were thought to have been extinct since the Cretaceous extinction 65 million years ago. However, in 1938, Captain Hendrick Goosen of the trawler Nerine brought a fish that had been caught deep in the Indian Ocean to Marjorie Courtenay-Latimer, curator of a museum in East London, South Africa. She identified the fish, now named Latimeria chalumnae, as a crossopterygian. Subsequent searches revealed that native fishermen of the Comoro Islands (in the Indian Ocean off the coast of Africa) reported that they had caught these fish for years and had thrown them back as inedible. In 1998, another species, Latimeria menadoensis, was found several thousand miles away, in Indonesia, by a scientist on his honeymoon. The lineage of fishes that became tetrapods included fishes such as Eusthenopteron, which had skeletal characteristics intermediate between those of earlier fishes and later amphibians. Later species in this lineage had legs but still retained many fish skeletal characteristics. As is the case with any socalled missing links, there is no clear line of division between ancestor and descendant. Most bony fishes release eggs and sperm into the water, where external fertilization occurs. In some bony fishes, such as sea horses and pipefish (see above), fathers may hold fertilized eggs within their bodies while the eggs undergo embryonic development. Bony fishes display a great variety of reproductive habits. In some species, individual males and females form pairs, while in other species they form large reproductive groups. In some species, a fish may begin its life as a female then develop into a male, while other species contain some individuals that are hermaphroditic (both male and female at the same time).

Adaptations to Aquatic Environments

Salmon migrate from the ocean upstream to the ponds in which they hatched, often jumping upstream over waterfalls to do so. Bears easily catch some of them during this migration.  (Sandra vom Stein; iStockPhoto.com)

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Most fishes, except for the tuna and the great white shark, are ectothermic (from the Greek, roughly translating to “outside temperature”), which means their temperatures fluctuate with those of their environments. The tuna and the great white shark generate some internal body heat, which makes them at least partly endothermic (Greek for “inside

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250 fishes  250

first entry fishes today, the lung has evolved into the air bladder, not connected to the pharynx, which the fish uses for buoyancy. Fishes have a single opening through which both nitrogenous wastes and gametes are released. In some fish, this opening is a cloaca (plural cloacae) through which intestinal wastes are also eliminated. Hagfishes cannot regulate their tissue salt concentration, which is therefore the same as that of the water surrounding them. However, some lampreys live in freshwater and can regulate their internal salt concentration. The tissues of cartilaginous fishes contain less salt than the ocean water surrounding them, but they maintain isotonic balance with the seawater by accumulating urea in their blood. Sharks also release ammonia into the water through their gills. The blood of marine bony fishes contains less salt than the hypertonic seawater, and they must continually drink water to replace the osmotic water loss. Freshwater bony fishes must continually excrete the water that diffuses into their bodies from the hypotonic environment.

Conservation of Fishes

A male pink pygmy sea horse (Hippocampus bargibanti), with its pouch full of young offspring, is excellently camouflaged against a Muricella sea fan coral.  (Dan Schmitt; iStockPhoto.com)

t­ emperature”). There are no fishes that maintain a constant body temperature. Therefore, fishes are all heterothermic (Greek for “variable temperature”) rather than homeothermic (Greek for “constant temperature”). Fishes need to maintain buoyancy so that they do not have to swim continually to keep from sinking. In sharks, buoyancy is provided by a large liver filled with fat (which is less dense than water). The liver can counterbalance only about one-third of the shark’s weight, however; sharks therefore do need to keep swimming, if only slowly, to keep from sinking. Most sharks also need to keep swimming in order to provide oxygenated water to their gills, which are inside of slits behind the head. Some sharks, however, can rest in caves or on the bottom of the sea while they pump water past their gills. Bony fishes, however, use air bladders or lungs. Lungs are a primitive condition for bony fishes. Lungs began as expansions of the upper digestive tract that were open to the pharynx, allowing the fish to gulp air. Gars and bowfins can still do this. In most bony

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Many fishes are rare and in danger of extinction. But there are many threats to the survival of even the more common fish species. These include: Overfishing.  Many species of commercially important fishes have large populations and fill large expanses of the oceans. They appear to be inexhaustible resources. But commercial fishing fleets use advanced technologies to capture prodigious numbers of them: nets that are many miles long, for example. As a result, many commercial fish species have experienced steep population declines. Because the open oceans are international, the only controls of ocean fishing are international agreements and voluntary measures by fishing corporations, neither of which have been satisfactory. Significant overfishing has occurred even in the shallow waters of continental shelves that are under the jurisdiction of specific nations. In some places, such as California, New England, and Iceland, sustainable harvest standards were adopted. In 2009, after about a decade of these standards, fish populations began to recover. Nevertheless, some fish species such as the northern bluefin tuna (Thunnus thynnus) are critically endangered and unlikely to recover soon. Their very rarity contributes to their decline: a single bluefin can sell for $100,000 on the Japanese wholesale sushi market. Pollution. The oceans have been significantly polluted, particularly with garbage. Ocean currents have deposited large accumulations of floating garbage in numerous locations. The largest of these, the Great Pacific Garbage Patch, is located in the North

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fishes  251 Pacific Ocean and is the size of Texas. The garbage is mostly plastic, which decomposers cannot break down. Some of the plastic garbage is toxic or has surfaces upon which persistent organic pollutants can be carried. Even though they cover 70 percent of the Earth’s surface, the oceans are not in fact too large to pollute. Protection of spawning grounds.  Many species of fish spawn in habitats different from those in which they live their adult lives. Many marine fishes spawn and hatch in estuaries, which is where freshwater and salt water meet. Estuaries are highly productive because of the nutrients from the freshwater and the sunlight penetrating the shallow depths and are, therefore, rich sources of food for young fish. They are also a focal point for industrial pollution and for commercial development. Anadromous fishes, such as salmon, return to the streams in which they hatched to lay their eggs. It is a dangerous enough journey as it is, but becomes nearly impossible when the streams are blocked by dams. Many dams have salmon ladders, which allow salmon to bypass the dam. This has proven an imperfect solution, and in some cases dams that are not of great economic importance have been destroyed by the same agencies that built them—not only allowing fish migrations, but the recovery of entire aquatic ecosystems. Releases from hatcheries and selection by fishing.  It would seem strange to consider the replenishment of fish populations by the release of young fish from hatcheries to be a conservation problem. However, when large numbers of fish are released and then many of them are caught by fishermen, natural selection favors the fish that reproduce before they reach the legal size limit for capture. These fish evolve the ability to reproduce at smaller sizes. Their genes spread into wild populations may cause a reduction in average fish size in those populations as well. There is special concern about the escape of genetically modified fish, such as salmon, resulting in the introduction of transgenes into wild populations. See also amphibians; animals; cladistics; deep oceans, biodiversity in. Further Reading Allen, Thomas B. Shark Almanac: A Fully Illustrated History of Sharks, Skates, and Rays. Guilford, Conn.: Lyons Press, 1999, 2003. Barlow, George. The Cichlid Fishes: Nature’s Grand Experiment in Evolution. New York: Perseus, 2002. Berra, Tim M. Freshwater Fish Distribution. San Diego: Academic Press, 2001. Briggs, D. “Conodonts: A major extinct group added to the vertebrates.” Science 256 (1992): 1,285–1,286.

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Chapleau, Francois, et al., eds. Encyclopedia of Fishes. San Diego: Academic Press, 1998. Ford, Michael J. “Selection in captivity during supportive breeding may reduce fitness in the wild.” Conservation Biology 16 (2002): 815–825. Fountain, Henry. “Red-bellied piranha is really yellow.” New York Times, May 24, 2005. Available online. URL: http://www.nytimes.com/2005/05/24/ science/24obse.html. Accessed August 7, 2011. Froese, R., and D. Pauly, eds. “FishBase.” Available online. URL: http://www.fishbase.org. Accessed August 8, 2011. Hutchings, J. A., and D. A Fraser. “The nature of fisheriesand farming-induced evolution.” Molecular Ecology 17 (2008): 294–313. Jackson, J. B. C., et al. “Historical overfishing and the recent collapse of coastal ecosystems.” Science 293 (2002): 629–638. Long, John A. The Rise of Fishes: 500 Million Years of Evolution. Johns Hopkins University Press, 1996. Martin, R. Aidan. “ReefQuest Center for Shark Research.” Available online. URL: http://www.elasmo-research. org. Accessed August 8, 2011. Monterey Bay Aquarium. “Seafood watch.” Available online. URL: http://www.montereybayaquarium.org/ cr/seafoodwatch.aspx. Accessed May 13, 2011. Moritz, T., and K. E. Lisenmair. “The air-breathing behaviour of Brevimyrus niger (Osteoglossomorpha, Mormyridae).” Journal of Fish Biology 71 (2007): 279–283. National Oceanic and Atmospheric Administration. “Our fear of and fascination with sharks.” Available online. URL: http://www.magazine.noaa.gov/stories/mag36. htm. Accessed May 13, 2011. Nelson, Joseph S. Fishes of the World. Hoboken, N.J.: John Wiley & Sons, 2006. Quammen, David. “Where the salmon rule.” National Geographic, August 2009, 28–55. Rios, L. M., Charles Moore, and P. R. Jones. “Persistent organic pollutants carried by synthetic polymers in the ocean environment.” Marine Pollution Bulletin 54 (2007): 1,230–1,237. Shubin, Neal. Your Inner Fish: A Journey into the 3.5-billion-year History of the Human Body. New York: Basic Books, 2007. Sweet, W. C., and Donoghue, P. C. J. (2001), “Conodonts: past, present and future.” Journal of Paleontology 75 (2001): 1,174–1,184. United Nations Environmental Programme. “Overfishing: A threat to marine biodiversity.” Available online. URL: http://www.un.org/events/tenstories/06/story. asp?storyID=800. Accessed May 13, 2011. Xian-guang, H., et al. “New evidence on the anatomy and phylogeny of the earliest vertebrates.” Proceedings of the Royal Society B: Biological Sciences 269 (2002): 1,865–1,869.

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252 flowering plants  (angiosperms)  252

flowering plants  (angiosperms)  The flower-

ing plants (angiosperms) are the largest groups of plants, with at least 260,000 living species in 453 families. Angiosperms live in nearly every habitat except the deep oceans. They range in size from large trees to tiny floating duckweeds. Despite their tremendous diversity, angiosperms all evolved from a common ancestral species. Most species of eukaryotes have life cycles in which meiosis alternates with fertilization. Meiosis eventually produces haploid eggs and sperm that fuse together during fertilization. Plant life cycles differ from those of protists, animals, and fungi by having a multicellular haploid phase. The multicellular haploid structures produce eggs and/or sperm. The haploid structures of the seedless land plants, which evolved earliest, live in water or moist soil. In seed plants, however, the male haploid structures are pollen grains, which contain sperm and travel through the air from one plant to another and the female haploid structures remain within the immature seed. Seeds contain, feed, and protect embryonic plants. Angiosperms and gymnosperms are the seed plants. The unique features shared by all flowering plants include flowers, fruits, and double fertiliza-

first entry tion. Flowers produce fruits and consist of the following parts (see figure): ●● ●●

●●

●●

Sepals are leaflike structures that protect unopened flowers. Petals attract pollinators (see photograph on page 253). In some cases, flowers may lack petals, and the sepals assume the role of attracting the pollinators. Stamens produce pollen. Pollen develops inside of anthers, each of which has two pairs of pollen sacs. Filaments hold the anthers up from the base of the flower. Stamens are the male component of a flower. Carpels produce seeds. Tissue of the female parent completely surrounds the seeds during their development, forming a carpel. Pollen grains attach to the stigma, which is a surface at the top of the carpel; the immature seeds are protected within an ovary at the base of the carpel. Two or more carpels may be fused together into pistils. The base of the pistil, known as the ovary, develops into a fruit, which assists in the dispersal of the seed to a new location. Carpels are the female component of a flower.

Parts of a flower may include protective sepals, petals that attract pollinators, male stamens, and female carpels. Many flowers lack one or more parts. The parts may assume different functions. For example, in some flowers the sepals or stamens attract pollinators.

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Not all flowers have all of these parts. A flower may lack sepals or petals or both. While most flowers are hermaphroditic (have both male and female parts), a flower may have only stamens (a staminate flower) or only carpels (a pistillate flower). A plant may have flowers all of which are hermaphroditic or have both staminate and pistillate flowers or may have only one or the other. The other unique feature shared by all angiosperms is double fertilization, in which each pollen grain contains two sperm nuclei. One of the sperm nuclei fertilizes the egg nucleus, and the other fertilizes female polar nuclei that develop into endosperm, a nutritive tissue inside the seed. The earliest undisputed fossils of angiosperms date back about 130 million years to the Cretaceous period. Some researchers interpret a few earlier fossils to be those of angiosperms. Unlike

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flowering plants  (angiosperms)  253

Many flowers, such as this Linanthus montanus from the Sierra Nevada of California, have colorful markings that show pollinators where to find the nectar.  (Stanley A. Rice)

the dinosaurs, the angiosperms as a group survived and recuperated from the asteroid impact of the Cretaceous extinction, perhaps because their seeds remained dormant and sprouted after the Earth recovered from this event. Botanists understand that the angiosperms evolved from a gymnosperm ancestor. This had to occur, unless seeds evolved more than once, which is unlikely. However, fossil evidence of the ancestor of angiosperms is lacking. The earliest angiosperms in the fossil record are already differentiated into distinct evolutionary lineages. Based just upon fossil evidence, the origin of angiosperms remains today as it was when Charles Darwin called it an “abominable mystery.” Fortunately, there is evidence, much of it molecular, that allows botanists to reconstruct the origin of angiosperms. One major difference between gymnosperms and angiosperms is that the wood of most angiosperms contains large water-conducting vessels, while most gymnosperms have only small conducting tubes. A few gymnosperms, including the now extinct Bennettitales and the modern group often classified as Gnetales, have wood with large vessels, while a few angiosperms have wood without

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large vessels. The Bennettitales and Gnetales had or have reproductive structures that are not flowers but resemble them in some ways. The angiosperms that have wood without vessels are those that have also been identified, for other reasons, as the most primitive angiosperms. One major difference between angiosperms and gymnosperms is that most angiosperms have a much faster life cycle than that of gymnosperms. In gymnosperms, a year may be required for the pollen nucleus to reach the egg and bring about fertilization. There are therefore no annual gymnosperms (i.e. that live only for a year, completing their reproduction at the end of the same year in which they germinated). In angiosperms, fertilization can happen in a few days or less. This observation has led many researchers to believe that the earliest angiosperms lived in disturbed environments. These disturbed areas may have included places that experienced a forest fire or landslide, seasonal drought, or even damage by dinosaurs. Rapid growth provides an evolutionary advantage in disturbed areas. If the earliest angiosperms lived in such environments, it may not be surprising that no fossils of them have been found, as such environments are very unsuitable for fossilization. There is also widespread recognition among botanists that angiosperms have proliferated largely because of coevolution with animals, as in these examples: ●●

●●

Although many lineages of angiosperms retain or have re-evolved wind pollination, most angiosperms have coevolved with the insects and other animals that pollinate their flowers. Insects as a whole did not experience an increased burst of diversity during the Cretaceous period. But insect lineages such as bees and butterflies, in which the adults pollinate flowers, have proliferated, along with the angiosperms, since the Cretaceous period. Although many lineages of angiosperms have re-evolved wind dispersal of seeds, most angiosperms have coevolved with mammals and other animals that disperse their seeds. The fact that many mammals ate fruits, while dinosaurs appeared to rarely do so, paralleled the decline of dinosaurs during the Cretaceous and the proliferation of mammals since the Cretaceous.

The earliest angiosperm fossils do not provide a clear indication of what the earliest flowers were like, because by the time of these earliest fossils, angiosperms had already evolved a great diversity

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254 flowering plants  (angiosperms)  254 of flowers, from small, simple flowers to large magnolia-like flowers. Angiosperms radiated into many diverse forms very early in their evolutionary history. Since botanists have no fossils of the ancestral angiosperm, they have attempted to reconstruct the earliest flower by cladistics, an evolutionary analysis of existing groups of angiosperms. Most of these analyses have clearly identified a small woody plant that today exists only in the cloud forests of New Caledonia, Amborella trichopoda, as the only surviving member of the lineage that most closely resembles the ancestor of all flowering plants. Characteristics of Amborella include the following:

first entry In many lineages of flowers, a mosaic of such changes has occurred. In roses, for example, all of the floral parts are still separate, the stamens are still numerous, but there are only five petals. In geraniums, all of the floral parts are still separate, but there are only five stamens and five petals. Mallow flowers have five separate petals but numerous stamens that have fused together. The traditional classification of angiosperms divides them into monocots and dicots. Monocots have characteristics such as these: ●●

five to eight sepals and petals, which are small, greenish-yellow, and largely separate from one another numerous stamens, largely separate from one another five to six separate carpels, each of which has an ovary with a single seed. The carpel does not completely close with tissue during growth. It is sealed by a secreted liquid.

●●

If these characteristics represent what the first flowers were like, then the following major changes have occurred during the evolution of the angiosperms:

●●

●●

●● ●●

●●

●●

●●

In many but not all lineages, the floral parts have fused together. Two kinds of floral fusion are connate fusion, in which similar parts have fused, and adnate fusion, in which different parts have fused. In some lineages, petals have fused together to form a tube or to form a landing platform that accommodates pollinators; in many lineages, carpels have fused into pistils; in a few, stamens have fused together. All these are examples of connate fusion. In some lineages, stamens have fused to petals, an example of adnate fusion. In many but not all lineages, the numbers of floral parts have changed. In many lineages, the numerous stamens have been replaced by a small number of stamens, usually the same as the number of petals. In some lineages, the number of parts has increased, as in the lineages in which the flowers have dozens or even hundreds of petals. Amborella and other primitive flowering plants are woody. The herbaceous condition, in which extensive woody tissue never develops, has evolved numerous times in separate lineages of flowering plants.

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●● ●●

The embryo has one leaf (mono- for one, -cot for cotyledon). The leaves usually have parallel veins. The stems usually have scattered bundles of veins. The flowers usually have parts in threes or multiples of three. Dicots have characteristics such as these:

●●

●● ●●

The embryo has two leaves (di- for two, -cot for cotyledon). The leaves usually have netlike veins. The veins usually form a ring just underneath the surface of the young stem. The flowers usually have parts that are numerous, or in fours, fives, or multiples thereof.

The arrangement of the stem veins results in important differences between monocots and dicots. Each vein contains both xylem (which conducts water upward from the roots to the leaves) and phloem (which conducts sugar water primarily downward from the leaves to the stems and roots). The phloem is oriented toward the outside of the stem. Between the xylem and phloem there are cells that produce new xylem and phloem cells. In young dicot stems, since the xylem of the veins forms a discontinuous ring, the production of new xylem cells produces a continuous ring of xylem, or wood. Furthermore, a new layer of wood can be produced each year. Meanwhile, the discontinuous ring of phloem can become a continuous ring of phloem, or inner bark. Many dicots are therefore capable of producing large woody trunks that increase in diameter throughout the life of the tree (see photographs on page 255). (The bark does not accumulate, as it is pushed outward by the accumulating wood.) In contrast, the scattered veins in monocot stems do not produce very many new xylem and phloem cells. If they were to do so, the result would be an unstable mixture of wood and bark. Most monocots are therefore small, herbaceous plants. Only a few, such as palm trees, grow large. The trunks of

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flowering plants  (angiosperms)  255

Most trees are dicots, which produce xylem (wood) and phloem (bark) in orderly layers, allowing a strong trunk to develop (left). Palm trees produce xylem and phloem in scattered bundles throughout the trunk, which produces a trunk that is not as strong (right).  (Stanley A. Rice)

these trees do not increase in diameter as the plant becomes older: The trunk of a palm tree is no thicker at the bottom than it is at the top (see figure). Evolutionary analysis has allowed the classification of angiosperms into the following lineages: ●●

●● ●●

Basal angiosperms include several independent evolutionary lineages, such as Amborella, water lilies, magnolias, and laurels. All of these basal lineages have sepals, petals, stamens, and carpels that are not attached to one another, and their trunks are woody. Monocots are a distinct lineage of flowering plants. Eudicots, or true dicots, are a lineage that includes all of the rest of the flowering plants and are described in a separate entry.

Therefore, although the monocots are a monophyletic group, the dicots are a paraphyletic group. The 260,000 species of flowering plants far surpass the species diversity of any other plant group.

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See also cladistics; coevolution; Cretaceous period, biodiversity in; dicots; monocots; pollination; seedless plants; seed plants. Further Reading Crepet, William L., and Karl J. Niklas. “Darwin’s second ‘abominable mystery’: Why are there so many angiosperm species?” American Journal of Botany 96 (2009): 366–381. Endress, Peter K., and James A. Doyle. “Reconstructing the ancestral angiosperm flower and its initial specializations.” American Journal of Botany 96 (2009): 22–66. Friedman, William E. “The meaning of Darwin’s ‘abominable mystery.’ ” American Journal of Botany 96 (2009): 5–21. Klesius, Michael. “The big bloom: How flowering plants changed the world.” National Geographic, July 2002, 102–121. Magallon, Susana, and Amanda Castillo. “Angiosperm diversification through time.” American Journal of Botany 96 (2009): 349–365. Soltis, Douglas E., et al. Phylogeny and Evolution of Angiosperms. Sunderland, Mass.: Sinauer Associates, 2005.

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256 food web  256 Soltis, Pamela S. and Douglas E. Soltis. “The origin and diversification of angiosperms.” American Journal of Botany 91 (2004): 1,614–1,626. Taylor, Edith L., and Thomas N. Taylor. “Seed ferns from the late Paleozoic and Mesozoic: Any angiosperm ancestors lurking there?” American Journal of Botany 96 (2009): 237–251.

food web  See ecosystems. fossils and fossilization  Fossils are the evi-

dence of past biodiversity and therefore the basis upon which scientists can reconstruct the evolutionary history of biodiversity. Fossils are the physical evidence of organisms that have been dead for many years, past the normal duration of decomposition; fossilization is the set of processes by which they are formed. When volcanic or other rocks erode, water carries sediment to the continental shelves at the edges of the oceans, where it accumulates in layers called strata. This process is occurring right now. As silt and mud layers are buried, the increased temperature and pressure transform them into sedimentary rocks. The layers in sedimentary rocks are visually distinguishable. Clay particles become shale, while sand particles become sandstone. Fossils are usually found in sedimentary rocks, since dead plants and animals are often buried in the sediment. Intense heat and pressure can transform volcanic or sedimentary rocks into metamorphic rocks, in which the fossils are usually destroyed. Fossils are not always destroyed by metamorphosis. Structures that may be fossilized cyanobacteria can be seen in the 3.5-billion-yearold Apex chert of Australia. Fossils have been known for millennia, but until the last three centuries, most people thought fossils were simply peculiar rocks that just happened to look like plants and animals, rather than being the remains of actual plants and animals. Leonardo da Vinci was one of the earliest scholars to recognize fossils for what they really were, and he puzzled about why fossils of seashells were found at the tops of mountains. His solution to the problem reflected more of the medieval than the modern mind. He conceived of the Earth as an organism, therefore it must have a circulatory system, which means that ocean water must circulate underground to the tops of mountains, where it comes out as creeks and rivers—and sometimes brings seashells with it. He was right about the fossils, though wrong about how they got there. Another early scholar to recognize fossils as remnants of formerly living organisms was Danish geologist Niels Stensen (Nicholas Steno).

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first entry When an organism dies, it almost always decays. Under some circumstances, decomposition is delayed, such as in the presence of water and the absence of oxygen. As the organism decays slowly, the space inside its body, sometimes even inside of its cells, is filled with mineral deposits from the water (see figure on page 257). The fossil may be completely mineralized; alternatively, permineralization occurs when minerals enter the dead organism without completely replacing the original molecules. Under conditions of high temperature and pressure, the sediments surrounding the organism and the organism itself are both transformed into rock. Because of chemical differences between the fossil and its surrounding matrix, fossils usually stand out and may cause a zone of weakness in the rock that contains them. Fossils are therefore frequently found by geologists who strike the rocks with hammers; the fracture reveals the fossils. Mineral deposits inside of a coal seam (coal balls), rather than the coal itself, often contain fossils of the plants from which the coal was derived. The chemical differences between the fossil and its matrix can sometimes be of help in extracting the fossil. For example, shells of invertebrates can sometimes be isolated if the matrix is dissolved in concentrated hydrofluoric acid. Sediments are the major, but not the only, place to find fossils. Many insects, stumbling into conifer sap, became entangled and engulfed; the sap became amber, and the insects were preserved in exquisite detail. This happened frequently enough that there is a worldwide market for insects preserved in amber. Ancient wood other than petrified wood, human bodies from a bog, and mummies preserved in Andean caves are not usually considered fossils, nor are bodies preserved by human activity (such as Egyptian mummies). Fossils retain the structure of the original organisms, sometimes with considerable internal detail; therefore coal and oil are not considered fossils, since they have been transformed into uniform organic materials (even though they are called fossil fuels). These remains can be as valuable as fossils in scientific research. Leaves that have been preserved for 20 million years in cold, wet, anoxic conditions in deposits near Clarkia, Idaho, are still green, but oxidize into black films upon exposure to air. The leaves were so chemically intact that scientists could extract chloroplast DNA from them. The hard parts of organisms (such as the calcium carbonate shells of invertebrates, and the calcium phosphate bones of vertebrates) are most easily preserved and constitute the vast majority of fossils. Teeth are particularly popular fossils to study, not only because they are hard (and abundantly

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fossils and fossilization  257

Petrified wood is produced when minerals replace biological material during slow decomposition in water. The resulting mineral structure reveals where the tree rings and wood rays used to be (the rays contain red iron in this photograph). The petrified logs at Petrified Forest National Park in Arizona were a forest of conifers related to modern Araucaria more than 200 million years ago.  (Stanley A. Rice)

­ reserved) but also because they can reveal what p kind of diet the animal had—grinding teeth for grazers, sharp teeth for carnivores. The study of fossil bones can also reveal more than just the anatomical structure of the animal. Study of tissue layers inside of bones reveals the growth rate of the animal and its age at death. This is how scientists have determined that Tyrannosaurus dinosaurs had a high metabolic rate and grew rapidly, up to 880 pounds (400 kg) by the age of 20 years. Under conditions of very slow decomposition and very thorough burial, soft parts of organisms, and entire organisms without hard parts, can be preserved. A famous example is the Burgess Shale in Canada. Impressions of soft-bodied animals, many parts of plants, and even single-celled microbes have frequently been preserved. Since fossilization almost

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always requires burial in sediment, most fossils are of the aquatic organisms that already live in or near the sediments. Aquatic invertebrates therefore constitute the best fossil assemblages. Terrestrial organisms are fossilized when they fall into or are washed into the sediments, as when primitive birds fell into low-oxygen pools that later became the limestone deposits of Solnhofen limestone in Germany, where ancient Archaeopteryx birds were fossilized. The odds are very much against the preservation of fossils from terrestrial organisms: It is estimated that only one bone in a billion is preserved as a fossil. If all 300 million Americans, most of whom have 206 bones, were to die, only about 60 bones would be fossilized under normal conditions. The odds are not even good for organisms of shallow oceans, where only 40 percent of the organisms have even the possibility of being fossilized. Rarely, massive graveyards of fossils (Lagerstätten) such as the Burgess Shale or the Solnhofen limestone have resulted from conditions that were remarkably good for preservation. An intimate knowledge of biology is necessary in the study of fossils. This allows a great deal of information about the living animal to be reconstructed from the fossils of just its bones. Sites of muscle attachment leave traces on the bones, therefore the musculature of an extinct animal can be reconstructed from bone fossils. Blood vessels inside the living bones may have left traces in the fossilized bones, allowing scientists to determine the extent of blood vessel formation and, hence, whether the animal was warm-blooded. Occasional lucky finds reveal even more about the animal’s life. Gastroliths are smooth stones found associated with dinosaur skeletons. Like modern birds, many dinosaurs swallowed stones that helped to grind plant food in their stomachs. The grinding action caused the stones to become smooth. Coprolites (fossilized feces) often allow scientists to reconstruct the diet of the animal. It is usually easy to tell which structures in sedimentary rocks are fossils and which are inorganic in origin, but not always. There was some controversy about whether a “shell” that was found in a Russian fossil deposit was actually a shell or a percussion fracture from the drill bit that extracted the sample. Unfortunately for researchers, fossils are usually found in fragments and have to be put back together. Examples include: ●●

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Plants often shed their organs separately or are torn apart during fossilization. Thus it is often impossible to tell which leaf grew in connection with which trunk. The same thing can happen to animals. The largest animal of the Cambrian seas,

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258 fossils and fossilization  258

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­ nomalocaris, was formerly described as A three separate animal species. The animal’s body had been described as a sea cucumber; its mouth had been described as a jellyfish; and its front legs had been described as headless shrimp. The true identity of these fragments was revealed only when a fossil was found that had these fragments together. One of the most abundant kinds of Paleozoic fossils was the conodont (cone-tooth). Everybody suspected that it was an animal tooth but nobody could find the animal. In 1983, after many decades of research, a conodont was found in association with a soft-bodied vertebrate and then only from a faint minnowlike depression. When fossils are found individually, it is often impossible to determine which of them belonged to the same species. Juvenile dinosaurs have sometimes been classified as a separate species from the parents. When whole herds or populations of dinosaurs are found fossilized together, it may be possible to determine which ones were the juvenile forms.

There are a few huge deposits of fossils, such as the hills of diatomaceous earth near Lompoc, California, and the white hills of Dover in England, which consist of billions of shells of tiny single-celled organisms. A huge graveyard of dinosaur bones, turned to stone, can be seen at Dinosaur National Monument in Colorado. Numerous skeletons of rhinoceroses and horses that died from breathing ash from a volcanic eruption 12 million years ago are preserved, in exquisite detail and still in their original arrangement, at Ashfall Beds State Historic Park in Nebraska. Trace fossils are the preserved evidence of the activities of the organisms. This includes worm burrows and animal footprints. Dinosaur footprints have allowed the analysis of how large the dinosaurs were and how fast they ran, which has fueled the suggestion that some of them, at least, were warm-blooded. Perhaps the most convincing evidence that the human ancestor Australopithecus afarensis walked on two legs was the discovery, by Mary Leakey, of a trail of remarkably human footprints produced by this species. Mistakes can be made in the interpretation of trace fossils. What was believed to be worm burrows, before the beginning of the Cambrian period, were considered the earliest signs of the rapid evolution of animal life. It is likely, however, that these burrows were created by singlecelled protists rolling in the seafloor mud. Fossils can be used to reconstruct the climate in which the organisms lived.

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Plants with large leaves today grow in moist areas, and plants with smaller leaves in drier areas. Serrated leaf margins allow modern plants to cool more efficiently than plants with smooth margins, without the evaporation of as much water. The study of leaf shapes can help reconstruct ancient temperature and moisture conditions. The pollen of seed plants has an outer covering that is very resistant to decay, and usually each genus of plant has its own visually distinguishable kind of pollen. Even when all other parts of a plant have decomposed, the pollen (though dead) may still be recognizable. Pollen from mud deposited during the most recent ice age, for example, indicates that spruce trees (now found only far north and on mountaintops) grew as far south as Oklahoma and that much of what is now Amazonian rain forest was grassland. The study of ancient pollen is called palynology.

The isotope ratios of fossils may also help determine the climate in which they grew. One example is the isotopes of carbon. Carbon dioxide molecules (CO2) in the atmosphere contain mostly carbon-12 (12C) but also a little bit of the heavier isotope carbon-13 (13C). The kind of photosynthesis that occurs in most plants discriminates against 13CO , with the result that organic matter contains 2 relatively less 13C than does the atmosphere. Many grasses that live in warm, dry grasslands have a different kind of photosynthesis, which does not discriminate against 13CO2 and produces organic matter that contains more 13C than is usually the case with organic matter. Animals that eat fruits may contain relatively less 13C in their bodies than animals that eat grains. Tooth enamel that contains more 13C may therefore reflect a diet of grains in a grassland or savanna setting, while tooth enamel with less 13C may indicate a diet of fruits and nuts in a forest setting. This has proven very important for reconstructing the behavior of human ancestors. The human lineage was assumed to have evolved in the savanna, until the analysis of tooth enamel carbon indicated in 2009 that Ardipithecus ramidus, a human ancestor that lived about a million years after the earliest hominids, lived in forests. See also birds; dinosaurs; fishes. Further Reading DeSalle, Rob, et al. “DNA sequences from a fossil termite in Oligo-Miocene amber and their phylogenetic implications.” Science 257 (1992): 1,933–1,936.

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founder effect and genetic drift  259 Fortey, Richard. Earth: An Intimate History. New York: Knopf, 2004. Gould, Stephen Jay. “The lying stones of Marrakech.” Chap. 1 in The Lying Stones of Marrakech: Penultimate Reflections in Natural History. New York: Harmony, 2000. ———. “Magnolias from Moscow.” Chap. 31 in Dinosaur in a Haystack: Reflections in Natural History. New York: Harmony, 1995. ———. “The upwardly mobile fossils of Leonardo’s living earth.” Chap 1. in Leonardo’s Mountain of Clams and the Diet of Worms. New York: Three Rivers, 1998. Masterson, Jane. “Stomatal size in fossil plants: Evidence of polyploidy in majority of angiosperms.” Science 264 (1994): 421–424. Niklas, Karl J., Robert M. Brown, Jr., and R. Santos. “Ultrastructural states of preservation in Clarkia angiosperm leaf tissues: Implications on modes of fossilization in late Cenozoic history of the Pacific.” In Late Cenozoic History of the Pacific, edited by Charles J. Smiley, 143–159. San Francisco: American Association for the Advancement of Science, 1985. Olson, Storrs L., and Helen F. James. “Fossil birds from the Hawaiian Islands: Evidence for wholesale extinction by man before western contact.” Science 217 (1982): 633–635. Palmer, Douglas. Fossil Revolutions: The Finds That Changed Our View of the Past. New York: Collins, 2004. WoldeGabriel, Giday, et al. “The geological, isotopic, botanical, invertebrate, and lower vertebrate surroundings of Ardipithecus ramidus.” Science 326 (2009): 65.

founder effect and genetic drift  The founder effect and genetic drift occur when a population is reduced in size (undergoing a population “bottleneck”), either soon after it is established as an offshoot of a larger population or as a result of bad luck that it experiences afterward. These circumstances allow random events, rather than processes such as natural selection, to control the genetic makeup of the population. Consider a large population that diminishes in size and becomes a small population. In this small population, just by chance, some of the genes may be lost. Consider a population consisting of some plants with red flowers and some plants with white flowers. If the population experiences a crash, the red-flowered individuals may be the only ones to survive, even though their survival had nothing to do with the color of their flowers. By chance, the genes for white flowers have been lost. Such genetic drift can almost permanently reduce the genetic diversity in a population. Then, when the population begins to grow, genetic diversity remains low.

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Consider a new population that is founded (for example, on an island) by a small number of emigrants that disperse from a larger, central population. The small number of founders will not carry all of the genetic diversity that was present in the central population. If a central population contains individual plants with red and with white flowers and a few seeds disperse to an island, the seeds may happen to be from red-flowered individuals. From the moment that the island population is founded, it already has lower genetic diversity than the population that produced it. It is unlikely that red flowers confer any advantage on the island population; the fact that the island population has no white-flowered plants is due to chance. This is the founder effect. The founder effect can result in a population in which, even if it grows, genetic diversity remains low. Both the founder effect and genetic drift reduce genetic diversity in a population: the founder effect, when a new population is formed, and genetic drift, when the old population suffers a bottleneck event. Both the founder effect and genetic drift were investigated by geneticist Sewall Wright. Genetic drift has been experimentally confirmed. In one experiment with fruit flies, geneticist Peter Buri investigated a gene with two alleles. At the beginning of each experiment, all of the flies were heterozygous, therefore both of the alleles were equally common. Every generation, Buri chose a small sample of males and females, from which he raised the next generation. Every generation of flies experienced a genetic bottleneck. By the 19th generation, in over half of the populations, one or the other of the two alleles became more and more common until it was the only allele that was present. Genetic drift can leave its mark on a population for many generations afterward. One in 20 humans who live on Pingelap Atoll in the Pacific Ocean has a mutation that causes color blindness and extreme light sensitivity. The usual population average for this mutation is one in 20,000 people. The reason the mutation is so common on Pingelap Atoll is that it was carried by one of the few survivors of a typhoon and famine that struck in 1776. Genetic drift can affect entire species, which is why it is of immense interest to conservation biologists. The Hawaiian goose, or nene (Branta sandiviensis), experienced a genetic bottleneck which greatly reduced the genetic variability in its populations and now faces extinction. Even when a species consists of a large number of individuals, the fragmentation of the species into many small populations can cause genetic drift to occur in each of the small populations, resulting in the catastrophic loss of genetic diversity. This is occurring in many

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260 fungi  260 ­ atural habitats, which are being set aside as only n small, disconnected nature preserves. Humans provide one of the best examples of a genetic bottleneck. The human species has a remarkably low genetic diversity. Geneticists estimate that the entire human species experienced a genetic bottleneck event about 70,000 years ago, at which time the entire human species consisted of only a few thousand individuals. See also natural selection; population genetics. Further Reading Aguilée, Robin, et al. “Allele fixation in a dynamic metapopulation: Founder effects vs. refuge effects.” Theoretical Population Biology 76 (2009): 105–117. Buri, Peter. “Gene frequencies in small populations of mutant Drosophila.” Evolution 10 (1956): 367–402. Chung, Mi Yoon. “Low levels of genetic variation within populations of the four rare orchids Gymnadenia cucullata, Gymnadenia camtschatica, Amitostigma gracile, and Pogonia minor in South Korea: Indication of genetic drift and implications for conservation.” Plant Systematics and Evolution 281 (2009): 65–76. Ramírez-Valiente, J. A., et al. “Elucidating the role of genetic drift and natural selection in cork oak differentiation regarding drought tolerance.” Molecular Ecology 18 (2009): 3,803–3,815. Templeton, Alan, et al. “The genetic consequences of habitat fragmentation.” Annals of the Missouri Botanical Garden 77 (1990): 13–27. Wright, Shane D., et al. “Slower tempo of microevolution in island birds: implications for conservation biology.” Evolution 63 (2009): 2,275–2,287. Young, Andrew, et al. “The population genetic consequences of habitat fragmentation for plants.” Trends in Ecology and Evolution 11 (1996): 413–418. Zlojutro, Mark, et al. “Coalescent simulations of Yakut mtDNA variation suggest small founding population.” American Journal of Physical Anthropology 139 (2009): 474–482.

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They have external digestion. They release digestive enzymes into their immediate surroundings and absorb the products of digestion. They consist of strands (hyphae, making up a mycelium) of haploid cells. During sexual reproduction, some hyphal cells fuse together to form dikaryotic cells, which have two haploid nuclei that do not fuse together in most cells. Fungi do not have diploid tissue. In some dikaryotic cells, the nuclei fuse together; the resulting diploid cell immediately undergoes meiosis and produces haploid spores, which are the tiny cells that blow through the air and disperse to a new location (see figure on page 261).

Because of these unique characteristics, fungi are classified into their own kingdom within the eukaryotic domain. Most of the time, fungi consist of hyphae that grow through living or dead organic material and consume it. Haploid hyphae often produce asexual sporangia, which release spores. The spores are genetically identical to the hyphae. Occasionally, two genetically different hyphae of the same species of fungus may encounter one another. When this occurs, they may fuse together, forming dikaryotic cells that are characteristic of their evolutionary lineage. Fungi do not have male and female gender. They carry out sexual reproduction with genetically different fungi of the same species. Many fungi release their spores directly into the wind. Some fungi, such as puffballs, allow collisions to release the spores (for example, raindrops propel the spores of earth stars into the air). Some fungi attract animals to disperse their spores. Stinkhorns produce a putrid scent that attracts flies, while truffles are famous for producing a version of the sex

Estimated Number of   Fungus Species

fungi  Fungi are eukaryotic multicellular organisms with the following distinctive characteristics: ●●

Their cells have cell walls made of chitin. Fungus cell walls represent an example of evolutionary convergence: Bacterial cell walls consist of peptidoglycan, and plant cell walls consist of cellulose (often with other materials) and evolved separately from the cell walls of fungi. Chitin is the same molecule that makes up the exoskeleton of arthropods.

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Number of Species

Division

Common Name

Chytridiomycota

chytrids

1,000

Microsporidia

microsporidians

1,500

Zygomycota

bread molds

1,000

Ascomycota

sac fungi

30,000

Basidiomycota

club fungi

30,000

Total

33,500

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fungi 261

When two fungal hyphae meet, they may form a joint reproductive structure, such as a mushroom. The mushroom consists of cells, each of which has two separate nuclei, one from each hypha. In some of the cells beneath the cap the nuclei fuse and then sexual cell division produces spores, which blow away in the wind.

hormone of a female pig. Male pigs dig them up, eat them, and transport the spores to a new location. Several groups of organisms, such as slime molds and water molds, have traditionally been classified with the fungi but do not share a common ancestor with fungi. these funguslike lineages are classified with the protists.

EvoluTIoNary dIvErSITy of fuNGI there are several lineages within the kingdom Fungi, of which two (ascomycota and Basidiomycota) are considered the “higher fungi” (see table on page 260). the table presents a rough estimate of the number of identified species, but many mycologists (biologists who study fungi) estimate that there may be a million and a half species. the lineages of fungi are distinguished by their sexual reproductive structures. the category “Deuteromycota” refers to fungi that have never been observed to reproduce sexually. in many cases, their identity has been determined by Dna analysis, and they have now been assigned to fungus lineages. Division Zygomycota are mostly terrestrial decomposers; a well-known example is bread mold, Rhizopus nigricans. its haploid hyphae spread over moist bread and absorb nutrients from it. During its asexual phase, it produces a stalk with a sphere on top, inside of which haploid spores form. When the sphere breaks open, the spores float away and may grow on another piece of bread. When two genetically different hyphae meet, they may form a spiky sphere known as a zygosporangium, in which sexual recombination produces haploid spores with a mixture of genes from the two parental hyphae.

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these spores are resistant to environmental conditions and are the form in which zygomycotes often persist in a dormant state. Pilobolus fungi grow on dung. the zygosporangium stalk is sensitive to light, aims the sporangium at the Sun, and explosively shoots the spores into the air. the spores may land up to seven feet (two m) away, far away from the dung, on vegetation that a grazing herbivore is likely to eat. the spores pass through the digestive system of the animal and end up on another lump of dung. another zygomycote is Empusa muscae, which grows inside the bodies of fl ies and kills them. the fungus reproductive structures emerge and release spores onto vegetation, where more fl ies will encounter them. Divisions Chytridiomycota and Blastocladiomycota are fungi that often live in water and are unique in producing spores that swim with flagella. Division Microsporidia consists of single-celled parasites of animals. Because of their simple structure and lack of mitochondria, they were once classified as primitive protists. Genetic analyses, however, identify them as degenerate fungi. Division Neocallimastigomycota consists of anaerobic fungi that live in the stomachs of ruminant animals and aid in the digestion of coarse plant material. Division Ascomycota, when they reproduce sexually, produce an ascus (plural asci), or sac, with eight spores: four produced by meiosis, each of which divides once by mitosis. Many ascomycota, however, do not reproduce sexually. there is a tremendous diversity of ascomycote forms. they include the following:

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262 fungi  262 ●●

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fungi that produce large reproductive structures on which the asci form, such as morels and truffles fungi that decompose food in a way that humans like. The best known is baker’s or brewer’s yeast (Saccharomyces cerevesiae), which exists primarily as single cells and reproduces asexually by budding. Yeasts produce the carbon dioxide bubbles in leavened bread and in beer, as well as the alcohol in fermented beverages. In addition, other ascomycotes help in processing foods: Aspergillus oryzae is essential in processing soybeans into soy sauce, and species of Penicillium produce the distinctive flavors of several kinds of cheese. fungi such as Pneumocystis, Candida, and Tinea that live inside the tissues of animals. Pneumocystis is usually harmless, but in people with severely compromised immune systems (especially due to HIV/AIDS), these fungi can produce fatal pneumonia. Candida albicans is responsible for vaginal yeast infections, as well as mouth infections called thrush. Tinea infects the outer, dead layers of the epidermis, forming dark rings as it advances, hence its name ringworm. It is most commonly found on feet (athlete’s foot) or in the genital areas (jock itch). It is annoying, difficult to eliminate, but not dangerous. fungi that are highly toxic to humans. Aspergillus flavus grows on peanuts and produces deadly aflatoxin. the ergot fungus Claviceps and other plant pathogens such as the Dutch elm disease (genus Ophiostoma), which has killed millions of large elm trees throughout the United States. The ascomycote Cryphonectria parasitica causes the chestnut blight that has eliminated almost all native adult chestnut trees in the eastern United States. Penicillium italicum is the green fungus that grows on oranges. powdery mildews on leaf surfaces and molds that grow in houses Penicillium chrysogenum, the hyphae of which produce penicillin, the first antibiotic to be discovered. Tolypocladium niveum is an ascomycote that produces cyclosporin, a very important immune suppressor used during organ transplants. most lichens, which consist primarily of ascomycote hyphae

Division Basidiomycota, when they reproduce sexually, produce spores on the end of basidia (clubs).

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Some fungi, such as this Amanita muscaria, are colorful and deadly.  (Brandon Brooks)

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many fungi with large reproductive structures are basidiomycotes. Examples include mushrooms (see figure), which have gills on the surface of which billions of spores are produced; boletes, which look like mushrooms but have pores instead of gills, through which spores are released into the air; puffballs; and earth stars. many plant pathogens, such as rusts and smuts Cryptococcus is a human pathogen.

Ecological Roles of Fungi Fungi are very important in ecosystems as decomposers of plant material. Their hyphae constitute a single individual fungus. Since in most cases each hyphal cell is on its own to obtain nutrition, the hyphae can extend only as far as there is a rich supply of dead leaves. Some fungi, such as honey mushrooms of the genus Armillaria, form rhizomorphs, which are reinforced cables of parallel hyphae that can transport nutrients. Rhizomorphs can grow through nutrient-poor soil and allow the hyphae to locate new pockets of food and allow the fungus to extend over large areas. Clones of genetically identical hyphal cells can be identified by DNA techniques. One Armillaria clone in Michigan was mapped using these techniques and found to cover 37 acres (15 hectares). It quickly gathered media attention as the world’s largest organism, even though it would not be noticeable to a person standing nearby. The researchers estimated that the clone was 1,500 years old and weighed 100 tons (9,700 kg), which is approximately the mass of an adult blue whale. An even larger fungus, Armillaria ostoyae, was discov-

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fungi  263 ered in Oregon. It covered 2,384 acres (165 hectares) and was estimated to be 2,400 years old. The soils of the world are filled with hyphal strands of decomposer fungi. Many fungi cause diseases. This list of animal diseases caused by fungi is rather short, but fungus diseases of plants are widespread. Every wild plant has a fungus that can kill it, and some fungi are specific to certain plants. In many cases, the fungi have only a single host: Gibberella zeae causes only head blight of cereals, although it can infect more than one kind of cereal. In other cases, fungi such as Scleroctinia and Rhizoctonia can infect a wide range of different agricultural host plants such as peanuts and soybeans. As its name might suggest, Phymatotrichum omnivorum infects many trees other than citrus, its principal host. But in several very interesting cases, pathogenic fungi have specific alternate hosts: The asexual phase of the fungus life cycle lives in the tissues of one host, while the sexual phase lives in the tissues of another. Examples include some astonishing alternations, such as between wheat and barberry bushes, wheat and meadow rue (a wildflower), and between apples and junipers (see table). Usually the fungus causes very different symptoms in the two hosts and appears to be two different species of fungi. To control the spread of agriculturally important fungi, it is only necessary to keep the crop populations apart from the wild plants that serve as alternate hosts. Since fungus spores can spread so widely, however, this has proven more difficult than it sounds. During the cold war, the United States military researched the use of Puccinia cereal rusts as biological weapons to use primarily against the Soviet Union, which depended heavily on wheat, and Magnaporthe grisea as a weapon against the Japanese rice crop during World War II. As important as fungi are as decomposers and pathogens, their role as mutualists is just as important. Hyphae of fungi known as mycorrhizae grow in the cortex of the roots of many plant species. The hyphae extend out into the soil farther than the roots or root hairs. The hyphae then absorb and

transport minerals, especially phosphate, into the roots, for their own use—but the plant makes use of these minerals also. This is particularly important as phosphate is a mineral that diffuses very slowly through soil and is thus frequently a limiting factor to the growth of plants. Evidence of mycorrhizal growth has been found in the fossilized stems of Aglaophyton major that lived 400 million years ago—one of the first land plants. It is therefore possible that, without the assistance of mycorrhizae, plants would not have been able to grow in the poor soils of the previously barren dry land. Ectomycorrhizae grow between the root cells but do not penetrate them, while endomycorrhizae penetrate the walls of root cells. The fungi feed on food-rich exudates from root cells. Ectomycorrhizae. About one-tenth of plant families (including the pine, oak, birch, eucalyptus, and rose families) have ectomycorrhizae. These fungi may belong to any of the three major divisions (Zygomycota, Ascomycota, and Basidiomycota). They form a network of cells inside and outside of the host root. Some ectomycorrhizae chemically attract springtails (small arthropods related to insects) and use the nitrogen in their bodies as a source of fertilizer for themselves and for their host plants. Endomycorrhizae. The most common endomycorrhizae are the arbuscular mycorrhizae, known only from the division Glomeromycota. They form balloonlike structures between the cell membranes and cell walls of root cortex cells, producing an intricate surface area of contact. Most families of plants (and many crop species) are hosts to these fungi. Arbuscular mycorrhizae are not known to have sexual reproduction, although there are genetically diverse nuclei in their cells. Plants in the heath and orchid families have other kinds of endomycorrhizae. In some cases, mycorrhizal fungi can form associations with the roots of more than one plant at a time. In doing so, they can transfer nutrients from a plant that has enough to another plant, even of a different species, that does not have enough. This is an example of mutualism that connects several

Examples of Pathogenic Fungi with Alternate Hosts Fungus

Common Name

Host

Alternate Host

Cronartium ribicola

Pine blister rust

White pine

Currants (Ribes)

Gymnosporangium

Apple cedar rust

Apple

Red cedar (Juniperus)

Puccinia coronata

Cereal crown rust

Cereals

Buckthorn (Rhamnus)

Puccinia graminis

Cereal stem rust

Cereals

Barberries (Berberis)

Puccinia triticina

Wheat leaf rust

Wheat

Meadow rue (Thalictrum)

xviii+598_Biodiversity_F.indd 263

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264 fungi  264 species. Plant ecologist Peter Högberg and associates found that mycorrhizal fungi transferred carbon compounds from overstory Scots pines (Pinus sylvestris) and spruces (Picea abies) to understory birches (Betula pendula) in a Swedish forest. Not only does this keep the conifers and the birches alive but promotes the transformation of a pine to a birch forest. Plant ecologist David Hartnett and associates found that mycorrhizae transferred phosphorus from grasses such as Sorghastrum nutans to forbs (nongrass herbaceous plants) such as Artemisia ludoviciana in the tallgrass prairie. According to mycologist Paul Stamets, it is possible to interpret this activity as the fungi cultivating the forest or the grassland, maintaining the plant cover and the diversity of species as if it were an agricultural field producing food for the fungus. It is not in the evolutionary interest of any plant to promote the growth of a plant of a different species, but it may be in the interest of the fungus to promote the growth of several plant species. Another ecologically important group of fungi is the genus Xylaria. Leafcutter ants (genus Atta) gather pieces of tropical rain forest leaves, bring them into the nests, and chew them up as mulch for growing Xylaria fungi. The fungi are the only food source for the ants. Leafcutter ants can be major “herbivores” in tropical forests even though they do not actually eat the plants. Perhaps the most extraordinary role that fungi play in the world of biodiversity is that their hyphae (usually of ascomycotes) form the structures of lichens. Single-celled eukaryotic green algae and prokaryotic cyanobacteria live amid the hyphae. The algae and cyanobacteria produce food by photosynthesis but cannot tolerate conditions that are both sunny and dry. The fungi protect the algae from excess sunlight during dry conditions. As a result, lichens live in places, such as tree trunks and surfaces of rocks, where neither fungi nor algae could live by themselves. The algal portion of the lichen (the phycobiont), the fungus portion of the lichen (the mycobiont), and the lichen itself each receives a scientific name. Some fungi have played important roles in human history. Examples include the following: ●●

“King Tut’s Curse” is believed to have been Aspergillus fungi. This fungus grew on organic material such as grains that were buried with the pharaohs, and its spores (still alive after millennia) were breathed by the first explorers to open the tombs. The fungus spores then grew in their lungs and killed them by pneumonia.

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The ergot fungus Claviceps purpurea grows in rye plants and produces the hallucinogen lysergic acid diethylamide (LSD). When humans consumed contaminated rye (in the form of rye bread), they hallucinated. This is apparently the cause of many of the witchcraft and werewolf trials in Europe and America several centuries ago. The hallucinogen caused some people to think they were werewolves and others to think they had seen werewolves. Research has shown that witchcraft and werewolf trials were most common in regions and years with mild winters and cool summers (conditions excellent for the growth of fungus) and among the poor, who ate most of the rye bread, rather than the rich, who ate wheat bread.

The conservation of fungi is both very important and very difficult. The main difficulty is that scientists do not even know what most of them are and therefore have no idea how to save them. Many of them live only in undisturbed forests; the destruction of an old-growth forest could, therefore, lead to the extinction of important species of fungi. Researchers such as Paul Stamets have found new species of fungi that can be of immense importance to humans, such as in the processing of organic wastes. Perhaps even more important than their benefit to humans is the way fungi tie together the dominant plants of an ecosystem into interacting units that scientists are only beginning to understand. See also decomposers; lichens; parasitism. Further Reading Burdon, J. J. “Fungal pathogens as selective forces in plant populations and communities.” Austral Ecology 16 (2006): 423–432. Dighton, John, James Francis White, and Peter Oudemans. The Fungal Community: Its Organization and Role in the Ecosystem. Boca Raton, Fla.: CRC Press, 2005. Fischer, W. M., and J. D. Palmer. “Evidence from smallsubunit ribosomal RNA sequences for a fungal origin of Microsporidia.” Molecular Phylogenetics and Evolution 36 (2005): 606–622. Gill, E. E, and N. M. Fast. “Assessing the microsporidiafungi relationship: Combined phylogenetic analysis of eight genes.” Gene 375 (2006): 103–109. Högberg, Peter, et al. “Natural 13C abundance reveals trophic status of fungi and host-origin of carbon in mycorrhizal fungi in mixed forests.” Proceedings of the National Academy of Sciences USA 96 (1999): 8,534–8,539. Klironomos, J. N., and M. M. Hart. “Animal nitrogen swap for plant carbon.” Nature 410 (2001): 651–652.

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fungi  265 Lee, Soo Chan, et al. “Microsporidia evolved from ancestral sexual fungi.” Current Biology 18 (2008): 1,675–1,679. Li, H., et al. “Arbuscular mycorrhizal fungi contribute to phosphorus uptake by wheat grown in a phosphorusfixing soil even in the absence of positive growth responses.” New Phytologist 172 (2006): 536–543. Matossian, Mary Kilbourne. Poisons of the Past: Molds, Epidemics, and History. New Haven, Conn.: Yale University Press, 1991. Money, Nicholas P. The Triumph of the Fungi: A Rotten History. New York: Oxford University Press, 2006. Simard, Suzanne W., et al. “Net transfer of carbon between ectomycorrhizal tree species in the field.” Nature 388 (1997): 579–582. Simon, L., et al. “Origin and diversification of endomycorrhizal fungi and coincidence with vascular land plants.” Nature 363 (1993): 67–69.

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Smith, Myron, Johann Bruhn, and James Anderson. “The fungus Armillaria bulbosa is among the largest and oldest living organisms.” Nature 356 (1992): 428–431. Stamets, Paul. Mycelium Running: How Fungi Can Help Save the World. Berkeley, Calif.: Ten Speed Press, 2005. Stephenson, Steven L. The Kingdom Fungi: The Biology of Mushrooms, Molds, and Lichens. Portland, Ore.: Timber Press, 2010. Wilson, Gail W. T., David C. Hartnett, and C. W. Rice. “Mycorrhizal-mediated phosphorus transfer between tallgrass prairie plants Sorghastrum nutans and Artemisia ludoviciana.” Functional Ecology 20 (2006): 427–435. Yafetto, L., et al. “The fastest flights in nature: High-speed spore discharge mechanisms among fungi.” PLoS One 3 (2008): e3237. Available online. URL: http:// www.plosone.org/article/info:doi/10.1371/journal. pone.0003237. Accessed May 13, 2011.

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G gaia  the Gaia hypothesis claims that organisms have transformed the entire earth and maintain it in a state very different than it would have been without organisms. “Gaia” is the name of an ancient Greek earth goddess and is intended by the scientists who defend the hypothesis as an image, not referring to the earth as a literal organism or person. Biologist lewis thomas proposed the concept that the earth was like a cell in his 1984 book Lives of a Cell. However, thomas’s imagery resulted in no program of scientific investigation. the scientific predictions based upon the Gaia hypothesis began with the work of atmospheric scientist James lovelock. its principal proponent within the world of biological and evolutionary science is evolutionary biologist lynn Margulis. Many biological scientists defend some version of the Gaia hypothesis. the Gaia hypothesis is sometimes worded as “the earth is an organism,” but this is not correct. the scientists who defend the Gaia hypothesis claim not that the earth is an organism but that the atmosphere and water of the earth are a nonliving part of the earth’s living system of interacting organisms the same way that a shell is a nonliving part of a mollusk. the Gaia hypothesis states that organisms transform the earth in a way that has resulted in a regulation of the temperature and chemical composition of the earth. a cell may contain both living components, such as organelles, and nonliving components, such as starch granules, but when viewed from the outside, the whole cell is alive. Similarly, the earth consists of both living components such as organisms and nonliving components such as air molecules and minerals, but when viewed from the outside, the earth is alive. Biological activities of organisms have caused the earth to be very different from other planets

and maintain it in a chemically unstable condition. thus, even without visiting a distant planet, observers should be able to determine whether life exists on the planet. if all of its atmospheric components (which can be studied by analyzing the light that they reflect) are in equilibrium, the planet is either lifeless or nearly so. life creates chemical and physical disequilibrium which can be visible from millions of miles away. this was the basis on which James lovelock predicted that no life would be found on Mars, a prediction that is either entirely or very nearly accurate. as a result of these biological processes, the earth behaves as a system, rather than as simply a stage upon which life-forms act. But the hypothesis goes further than just to say that the earth is an ecosystem. Perhaps the clearest statement of the Gaia hypothesis is the amsterdam Declaration of 2001: “the earth system behaves as a single, selfregulating system comprised of physical, chemical, biological, and human components.” ecosystem science does not include the regulation component. For example: ●

everyone knows that nearly all of the energy that flows through earth ecosystems arrives as photons of light from the Sun. Most of the absorbed sunlight warms the earth, and organisms use a little bit of this energy. eventually this energy radiates into outer space as infrared photons. But the Gaia hypothesis goes further. it claims that the web of interacting organisms regulates the temperature of the earth within certain limits. this, the hypothesis claims, is why the earth does not become too hot or too cold.

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Everyone knows that, in the Earth ecosystem, photosynthesis produces oxygen gas and absorbs carbon dioxide gas, while respiration does the opposite. As a result, carbon and oxygen molecules cycle endlessly through the Earth ecosystem. But the Gaia hypothesis goes further. It claims that the Earth regulates the amount of carbon dioxide and oxygen in the air, within certain limits. This, the hypothesis claims, is why carbon dioxide does not become so abundant in the atmosphere as to become poisonous and oxygen does not become so abundant as to cause the spontaneous combustion of all organic matter on the Earth.

What could cause such regulation to occur? One prevailing idea, called “wasteworld” by ecosystem scientist Tyler Volk, is that what is waste to one type of organism is a resource to another. Consider, for example, the carbon and oxygen cycles described previously. Natural selection favored photosynthesis because it gave cyanobacteria a fitness benefit: It allowed them to manufacture food. To cyanobacteria, carbon dioxide gas was a resource and oxygen gas was a waste product. But it was not long before other bacteria evolved an ability to use oxygen—not as food, but as a way of extracting energy from food, and they produced carbon dioxide as a waste. When the atmosphere contains a lot of carbon dioxide, plants carry out more photosynthesis, which removes carbon dioxide from the air. But when these abundant plants begin to die, decomposers remove oxygen from the air in the process of rotting the plants—and of returning carbon dioxide into the air. Regulation of atmospheric oxygen and carbon is an emergent property of different kinds of metabolism. Natural selection favors organisms that can obtain whatever resources are in short supply. At the beginning of life on Earth, resources were not wastes of other organisms but the primordial molecules of the planet. The original atmosphere of the Earth had so much carbon dioxide that the average temperature of the planet would have been about 122°F (about 50°C) at present levels of sunlight intensity. (Sunlight, however, was dimmer at that time.) Photosynthesis eventually removed enough carbon dioxide from the atmosphere that the average Earth temperature today is about 55°F (13°C). The emergence of the continents from underneath the ocean also helped to remove carbon dioxide from the air, since weathering of minerals consumes it. Organisms capitalize upon the wastes of other organisms not only on the planetary scale but in local regions as well. If the soil in a certain location does not have very much nitrogen in it (in the form

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of ammonia, nitrates, and nitrites), natural selection may favor plants that form mutualistic relationships with bacteria, which fix atmospheric nitrogen gas into ammonia within root nodules. When these plants die, decomposers release nitrogen-containing molecules into the soil. Once the soil contains high levels of nitrogen compounds, there is no longer a selective advantage to the nitrogen fixation symbiosis. In fact, in such circumstances, some bacteria can make a living by turning soil nitrogen compounds back into nitrogen gas. The result is a regulation of soil nitrogen content by organisms, each of which are acting in their own interests. As a result, ecosystem regulation emerges from processes of negative feedback. This is not, however, a completely satisfying explanation, for two reasons, which follow: ●●

●●

Organisms do not always evolve in response to negative feedback. Sometimes they evolve in response to positive feedback. That is, their wastes create an environment that is favorable to them, rather than to the other species of the world. One example is plants that pollute their surroundings with poisonous chemicals that inhibit the growth of other plants, a process known as allelopathy. Their wastes allow them to dominate their habitats more, not less. Another example is plants that are adapted to a fire cycle. They can tolerate fire, and their life cycles allow them to take advantage of fires and even to promote fires. (Some chaparral shrubs produce volatile, flammable chemicals in their old wood.) In a bog, sphagnum moss produces acid and grows as a thick clump, which prevents most other kinds of plants from growing with them. In each case, the plants benefit from creating conditions that are worse for other organisms, and other organisms have been unable to use these conditions as an opportunity for evolution and growth. Therefore, the natural world is as likely to contain examples of positive feedback as of negative feedback. Negative feedback seems unable to explain how the conditions of life are kept within such narrow limits. There is no guarantee that negative feedback will operate quickly enough to keep Earth’s conditions from getting out of control. Eventually, negative feedback will prevail, but in the meantime, any number of conditions—temperature, oxygen, carbon dioxide—may fluctuate outside the limits that life can tolerate. Why has this not occurred?

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268 Gaia  268

first entry

“Life of Earth: Portrait of a Beautiful, Middle-aged, Stressed-out Planet”

E

arth is a middle-aged planet. A little less than 5 billion years ago, the rocks of the Earth’s crust cooled off enough that the oceans could form and, soon thereafter, bacterial life-forms were living in it. A little less than 5 billion years from now, the Sun will have expanded enough that, even if it has not yet engulfed the Earth, life on this planet will have been obliterated, except for some bacteria living deep in the rocks. The universe is about 13.7 billion years old. If the age of the universe were equivalent to the distance across North America, from the Atlantic Ocean to the geographic center of the United States (which is a rock pedestal in Kansas), a human lifetime would be about the width of a finger. All of human civilization could fit into a few feet of space in front of that pedestal. Earth is a planet that does not just contain biodiversity but is held together by biodiversity. Earth is not itself an organism, but it is a living planet, kept alive by its millions of species, most of which (to the human viewpoint) have evolved just in the most recent 10 percent of Earth’s history. Earth’s species have transformed it into a planet almost completely different from what it would otherwise have been or what the other

planets are. Photosynthesis has filled the atmosphere with oxygen and removed most of the carbon dioxide that was originally present. Photosynthetic organisms, and the organisms that eat them, have created vast limestone deposits. Plants transpire a tremendous amount of water vapor into the atmosphere. Decomposers, consuming dead plant tissues, have turned sterile dirt into rich dark soil. Over much of the planet’s surface, the physical conditions (as experienced by mediumsized organisms) are not the direct product of sun and rain but are mediated through the shade cast by trees. All of its species form a living network. And this network appears to have regulated the physical conditions of the planet. Such regulation was not in any way the intention of the organisms making up this network. Natural selection has favored organisms that pass their genes into the next generation most effectively. Period. But, perhaps just by chance, these organisms have stabilized the conditions of the Earth in the process of creating conditions suitable for themselves. Billions of years ago, the Sun was much dimmer, but the high levels of carbon dioxide in the atmosphere created a greenhouse effect. As the Sun has become brighter, photosynthesis

One answer to these objections is simply luck. Plants that release allelopathic chemicals can, by chance, tolerate only a narrow range of conditions, and their polluting activities are limited to areas that have these conditions. Bogs are limited to small wetlands in which dense clay walls them off from the surrounding groundwater. A fire cycle can be established only in warm, dry regions. By chance, no organisms have produced any positive feedbacks that allow them to change the conditions of the whole world. Earth is just lucky that neither oxygen nor carbon dioxide levels have risen or fallen to deadly levels. Other planets may not have been so lucky, and on those planets, there are no people to ask these questions. Astrobiologist Peter Ward has pointed out that biological processes have sometimes in the past cre-

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has removed much of the carbon dioxide. That is, as the Sun became brighter, the greenhouse effect diminished, resulting in temperatures that have remained within the general boundaries in which life is possible during that entire period of time. Organisms appear to be keeping the temperature, oxygen, and carbon dioxide levels within habitable limits. Earth could be said to have had an unstable childhood and adolescence. Until about a half billion years ago, most life on Earth was microscopic. The continents were barren, and there was not as much biomass in the oceans as there is today. Photosynthesis and respiration got out of balance. At least three times, massive ice sheets covered much of the planet, as microbial metabolism proved incapable of maintaining an adequate greenhouse effect. But once Earth entered its young adulthood, life began to proliferate into many, teeming, multicellular forms, first in the oceans and then on the land. Ever since life began to cover the Earth, there have been no massive disruptions of the conditions of life—with a couple of exceptions: the Permian and Cretaceous extinctions. But these were caused by massive volcanic eruptions (in the first) and an asteroid impact (in the second). Neither of these

ated conditions that worsened the Earth as a whole, for example the bacterial production of hydrogen sulfide during the Permian extinction. Ward refers to this as the “Medea hypothesis,” named after a vengeful character in Greek mythology, as a contrast to Gaia. Earth is lucky not only for being just the right distance from the Sun but because negative feedbacks have prevailed over positive ones. Another answer is that Earth has not always been as well regulated as it now is. In fact, atmospheric temperature, carbon dioxide, and oxygen have reached levels in the past that were almost deadly. Two examples follow: ●●

During Precambrian time, the Earth almost completely froze, a condition popularly

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Gaia  269

events tipped the Earth into a spiral of massive heating or cooling. Even during these times of crisis, the atmosphere was never as hot, or as cold, as it had been before and during the primordial greenhouse conditions or worldwide glaciations. Life itself now appeared to be in charge of the planet and of stabilizing its conditions. Earth is now middle-aged and is astonishingly beautiful—primarily because of the very same network of biodiversity that allowed it to survive and keeps it alive. Earth was not always a pleasant place for every species. Species interactions were as likely to be negative (as with predators and parasites) as mutualistically positive. Nevertheless, Earth is at the peak of its beauty and health. With the arrival of the human species, unprecedented levels of intelligence evolved. In an instant of time, relative to Earth’s life, it was as if life had become conscious of itself; and in an even shorter instant, just in the last few centuries, human minds have begun to understand how the Earth and its life-forms evolved. Humans today represent the most extreme examples of many evolutionary processes, such as sexual selection and altruism. And with human intelligence has come the unique ability of a species actually to become a deliberate force of nature. As no other species (except perhaps for the photosynthetic bacteria that

first filled the atmosphere with oxygen), humans have transformed the surface of the Earth, turning over a third of it into managed lands such as farms and cities, and transformed the atmosphere. Global warming has happened many times in the past but never as rapidly as it is occurring today as a result of human activity. Thus just at the moment that Earth might have, by means of human intelligence, begun to appreciate its own beauty, it has entered a period of stress. Earth is unlikely to die from this stress, but it may temporarily lose much of the stability that its biodiversity has allowed it to have— biodiversity that is being rapidly depleted by humans. Conservationists, professional and amateur, who are trying to save the biodiversity of the Earth are doing so not just for the sake of the individual species. The efforts to prevent global warming are not just about polar bears, nor is the campaign against tropical deforestation just about beautiful (and sinister) orchids. It is about saving the integrity of the network of life that allows Earth to maintain its life-supporting conditions. Nobody knows how many species can become extinct without that integrity beginning to unravel. Nobody knows how much environmental destruction it might take to turn the life-sustaining operations into life-effacing ones. This is what nearly happened during the Permian extinction, when oxygen-starved oceans

known as Snowball Earth. The reason may have been that microbial photosynthesis was so effective that it removed too much carbon dioxide from the air, endangering Earth’s protective greenhouse effect. Had the snowball conditions been just a little worse or persisted just a little longer, the Earth might never have warmed back up, since most of the sunlight would have been reflected back into outer space. It is possible that the reason this occurred in the first place is that there simply was not yet enough of either the diversity or the abundance of life. In this case, Gaia was not yet large enough of a system to prevent fluctuations as great as the one that allowed Snowball Earth.

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●●

emitted hydrogen sulfide gas into the atmosphere. The network of life saved the planet that time, just barely. And it will almost certainly do so again this time. Nobody is saying that the Sixth Mass Extinction or the greenhouse effect is going to make humans fall over dead. But the remaining biodiversity of Earth may not stabilize the planet until after the conditions of life have fluctuated outside of the limits in which the network of civilization, upon which most humans depend for survival, have been exceeded. Will Earth enter its old age crippled? See also biogeochemical cycles; Cretaceous extinction; G aia; mass extinctions; mutualism; parasitism; P ermian extinction.

Further Reading Lovelock, James. The Vanishing Face of Gaia: A Final Warning. New York: Basic, 2009. Rice, Stanley A. Life of Earth: Portrait of a Beautiful, Middle-Aged, Stressed-Out World. Amherst, N.Y.: Prometheus Books, 2010. Ward, Peter. Under a Green Sky: Global Warming, the Mass Extinctions of the Past, and What They Can Tell Us About Our Future. New York: HarperCollins, 2007. ———, and Donald Brownlee. The Life and Death of Planet Earth: How the New Science of Astrobiology Charts the Ultimate Fate of Our World. New York: Henry Holt, 2003.

During the Paleozoic era, small trees lived in shallow wetlands all over the continents. Not only were the wetlands extensive, but the small trees were very crowded. These worldwide forests carried out a lot of photosynthesis and put a lot of oxygen in the air. Not only that, but herbivores and decomposers were apparently unable to consume as wide a variety of plant tissues, living and dead, as they do today. The trees in these worldwide forests accumulated as coal. Decomposition did not occur enough to remove very much of the oxygen that these trees produced. Most scientists accept that the atmosphere contained very high levels of oxygen—about 35 percent, rather than

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270 Gaia  270 the 21 percent that is in the air today. In this case, some important processes within the Gaia system had not yet evolved to their current levels of efficiency. The Earth today has more species and perhaps a greater mass of organisms than at any time in the past. If there had been as many organisms during the Precambrian as there are today, Snowball Earth may not have happened. A green scum Earth produced a Snowball Earth, something that would not have happened if there had been an abundance of organisms that could eat the green scum. Today, trees are consumed by animals when they are alive and fungi when they are dead. Photosynthesis would not get a chance to produce a hyperoxygenated atmosphere today as it did during the Paleozoic era. Life itself regulates the Earth much more effectively today than ever before in the past. Positive feedback on a worldwide scale, in which organisms amplify rather than dampen the extremes of Earth conditions, is rare but significant. The main example is the ice ages. The cool periods of glaciation and the warmer periods of glacial retreat are initiated by slight changes in the amount of sunlight that reaches the Earth, as a result of the Milankovi´c cycles, in which changes in the shape of Earth’s orbit and the angle of Earth’s rotation produce an approximately 100,000-year cycle of cooling and warming. The changes in solar radiation are very slight, enough to cause less than one-tenth of the amount of temperature fluctuation that characterized the ice ages. Biological processes, however, appear to enhance the Milankovi´c cycle. The slight increase in sunlight and warmth allows more decomposition, which enhances the greenhouse effect and amplifies the warming. Photosynthesis removes enough carbon dioxide that the greenhouse effect is dampened. Then when the slight decrease in sunlight and warmth occurs, the lack of a greenhouse effect amplifies the cooling. In this way, atmospheric carbon dioxide levels are both a cause and an effect of global warming. The rarity of such positive feedback mechanisms, however, assures that the “butterfly effect” cannot be true. The butterfly effect is a common aphorism that the flapping of a butterfly’s wings in one part of the world can cause a storm to occur in another part. Instead, the second law of thermodynamics insures that the random movement of molecules will drown out small events, such as the movement of a butterfly, rather than amplify them. The Gaia hypothesis indicates that organisms do not simply live upon the Earth; evolution has not simply caused organisms to adapt to the physical conditions of the Earth. Organisms have radi-

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first entry cally transformed the Earth and have partly created the very conditions to which evolution has adapted them. Lynn Margulis says that Gaia is just symbiosis seen from outer space. It may therefore be not just certain species interactions but the entire planet that is symbiotic. Some critics of the Gaia hypothesis claim that it is merely an Earth-goddess religion cloaked in scientific terminology. A religious view of Earth ecosystems is especially threatening to conservative and religiously motivated critics, who react to Gaia as to a pagan religion used in the service of environmentalism, which they oppose. But it is clear that conservative antienvironmentalists have their own, thoroughly unscientific, version of Gaia, upon whose altar they are willing to place the survival of the planet and humankind. They believe that, no matter what humans do, no matter how much carbon is released into the air or how many pesticides into the waters, the Earth will clean up the mess and keep everything—including temperature, rainfall, and soil fertility—in a range that is comfortable to humans. This may be the principal motivation behind conservative, especially religious, opposition to any laws or treaties regarding carbon emissions or pollution. As noted previously, life is much better at regulating the conditions of the Earth than it ever was in the past; but this ability is limited. Human activities are pushing the Earth beyond the ability of Gaia to regulate it. But to the conservatives in the Republican Party, there is nothing that Gaia cannot do. Their opposition to environmentalism is based on a version of Earth-religion far more extreme than has been proposed by any apologist for Gaia. The result is likely to be an Earth that is much warmer— not warm enough to threaten life in general but warm enough to be disastrous to human activities, one that may be known to future generations as “the Republican climate.” See also Essay: “Life of Earth: Portrait of a Beautiful, Middle-aged, Stressed-out Planet”; carbon cycle; competition, ecological; disturbances, ecological; ecosystems; greenhouse effect; ice ages; Margulis, Lynn; nitrogen cycle. Further Reading Gribbin, John, and Mary Gribbin. James Lovelock: In Search of Gaia. Princeton, N.J.: Princeton University Press, 2009. Hamilton, William D. “Ecology in the large: Gaia and Genghis Khan.” Journal of Applied Ecology 32 (1995): 451–453. ———. “Gaia’s benefits.” New Scientist 151 (1996): 62–63. ———, and Timothy M. Lenton. “Spora and Gaia: How microbes fly with their clouds.” Ecology, Ethology and Evolution 10 (1998): 1–16.

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Galápagos Islands  271 Jaenicke, Ruprecht. “Abundance of cellular material and proteins in the atmosphere.” Science 308 (2005): 73. Lenton, Timothy M. “Gaia and natural selection.” Nature 394 (1998): 439–447. ———. “Testing Gaia: The effect of life on Earth’s habitability and regulation.” Climatic Change 52 (2002): 409–422. ———, and M. van Oijen. “Gaia as a complex adaptive system.” Philosophical Transactions of the Royal Society of London B (Biology) 357 (2002): 683–695. Lovelock, James. The Vanishing Face of Gaia: A Final Warning. New York: Basic, 2009. ———. Gaia: A New Look At Life On Earth. New York: Oxford University Press, 1987. ———, and Lynn M. Margulis. “Atmospheric homeostasis by and for the biosphere: The Gaia Hypothesis.” Tellus 26 (1974): 2–10. ———, and M. Whitfield. “Life-span of the biosphere.” Nature 296 (1982): 561–563. Malin, G. and G. O. Kirst. “Algal production of dimethyl sulfide and its atmospheric role.” Journal of Phycology 33 (1997): 889–896. Margulis, Lynn, and James E. Lovelock. “Biological modulation of Earth’s atmosphere.” Icarus 21 (1974): 471–489. ———, and Dorion Sagan. Slanted Truths: Essays on Gaia, Symbiosis, and Evolution. New York: Copernicus, 1997. Rice, Stanley A. Life of Earth: Portrait of a Beautiful, Middle-Aged, Stressed-Out World. Amherst, N.Y.: Prometheus, 2010. Schneider, Stephen H., et al., eds. Scientists Debate Gaia. Cambridge, Mass.: MIT Press, 2004. Schwartzman, D. W., and Tyler Volk. “Biotic enhancement of weathering and the habitability of Earth.” Nature 340 (1989): 457–460. Swenson, W., David Sloan Wilson, and R. Elias. “Artificial ecosystem selection.” Proceedings of the National Academy of Sciences USA 97 (2000): 9,110–9,114. Volk, Tyler. “Gaia is life in a wasteworld of by-products.” In Scientists Debate Gaia, edited by Stephen H. Schneider et al. Cambridge, Mass.: MIT Press, 2004. ———. Gaia’s Body: Toward a Physiology of Earth. New York: Copernicus, 1998. Williams, George C. “Gaia, nature worship, and biocentric fallacies.” Quarterly Review of Biology 76 (2002): 479–486.

about 5 million years ago, which is very recent in evolutionary time. Being directly on the equator, these islands experience almost no variation in sunlight. They are right in the path of oceanic currents that influence temperature and moisture conditions. There is an annual fluctuation of temperature caused by the ocean currents. Because of this, the cactuses can use a temperature cue that allows them to bloom every January. The El Niño Southern Oscillation alternates between dry conditions, when the ocean water near the South American coast is cool, and wet conditions, when the water is warm. During an El Niño year, large amounts of rainfall stimulate plant growth, particularly of grasses, vines, and weeds, but diminish the productivity of the oceans. The food chain of the ocean depends upon the minerals brought up from cool, deep ocean waters; when the water is warm, these minerals are not available. However, periods of heavy rainfall are uncommon, and the lower slopes of the Galápagos Islands are usually hot and dry, with scattered trees and a lot of hot, bare ground. The upland areas of the larger islands are frequently shrouded in mist, which provides enough moisture for forests to grow. The islands are famous for their unusual plant and animal life. There are no large native grazing animals or predators. The native animals have evolved, until recently, in the absence of predators and human contact. From the fur seals to the ground-nesting birds, they show no fear of humans. Many of the species are unique to these islands, or almost so. This is because they evolved on the islands from small founding populations of mainland species. All over the world, islands are home to unique species. The unique species found on islands was one of the observations that led Charles Darwin to begin thinking about the process of evolution. During his round-the-world voyage on HMS Beagle, he visited many islands, including the Galápagos. His 1835 visit to the Galápagos turned out to be perhaps the single most important event that sparked Darwin’s understanding that evolution occurred by means of natural selection. Among the plants and animals that have undergone adaptive radiation on the Galápagos Islands are: ●●

Galápagos Islands  The Galápagos Islands are volcanic islands that have played and continue to play a very important role in evolutionary science and are the showcase of how biodiversity can develop. They belong to Ecuador and are about 600 miles (1,000 km) off the coast of that country. Much of the volcanic activity that produced them occurred

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Finches. These birds have evolved from a single founding population into about 14 species that specialize on different ways of life and types of food. Ever since David Lack studied them in 1947, they have constituted a premier example of adaptive radiation. Since Peter and Rosemary Grant began their studies in the 1970s, the finches have provided some of the most detailed information

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in the world about natural selection, speciation, and hybridization. Mockingbirds. A single founding population, probably of the Ecuadorian long-tailed mockingbird Mimus longicaudatus, has evolved into four species of mockingbirds on the Galápagos: Nesomimus trifasciatus, N. macdonaldi, N. melanotis, and N. parvulus. They are distinct from one another in coloration and behavior; they differ enough from their mainland ancestors that they have been placed in a different genus, Nesomimus, from the genus Mimus of which the North and South American mainland mockingbirds are members. Land iguanas, or lava lizards.  Seven species of land iguanas have evolved on the Galápagos Islands. Tortoises. The giant tortoises after which the Galápagos Islands are named are the most famous animals in the islands. Several of the islands have recognizably different kinds of tortoises—a fact that the governor of the islands pointed out to Charles Darwin when he visited. The tortoises move very slowly and live for a long time; a slow metabolism is a major part of their adaptation to these islands. Darwin rode on some when he visited. A few of the tortoises alive today may have been alive when Darwin visited, though this is unlikely. Daisy trees. The Galápagos Islands have 13 species of Scalesia trees, in the composite (daisy) family Asteraceae. Almost all members of this huge, worldwide family of plants are herbaceous (like the familiar daisies, dandelions, thistles, and ragweeds)—except on islands, such as the Channel Islands of California, St. Helena in the Atlantic, Hawaii, and the Galápagos. These daisy trees are somewhat flimsy and small as trees go and probably could not compete with trees from plant families with a long evolutionary history of producing trees, such as pines and oaks. On these islands, there are relatively few trees, which has allowed natural selection to produce tree-sized daisies. Tree cactuses. Cactuses in mainland North and South American deserts do not have bark; the six species of Galápagos prickly pear cactuses, however, do. The bark may have evolved as protection against the abundant sea animals that eat them.

There are also species that are unique to the Galápagos Islands, although they have not under-

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first entry gone as much adaptive radiation as can be seen in the animals mentioned above. Two hundred of the 700 species of Galápagos plants are unique, including the Galápagos tomato. Marine iguanas are highly unusual in the reptile world because they swim and eat algae. The Galápagos penguin is the only penguin that lives in a warm environment. There are Galápagos species of sharks, doves, hawks, rats, bees, butterflies, centipedes, martins, and flycatchers (see table). Other animals such as frigate birds travel widely in the oceans and have not evolved into unique forms confined to the islands. The isolation of the islands makes them a haven for birds and mammals that travel the oceans.

Some Noteworthy Species   of the Galápagos Islands Plants Brachycereus nesioticus

Lava cactus (Cactaceae)

Bursera graveolens

Palo santo (Burseraceae)

Miconia robinsoniana

Cacaotillo (Melastomataceae)

Opuntia megasperma

Opuntia (Cactaceae)

Scalesia spp.

Daisy trees (Asteraceae)

Scutia pauciflora

Espino bush (Rhamnaceae)

Solanum cheesemanii

Galápagos tomato (Solanaceae)

Animals Anblyrhynchus cristatus

Marine iguana

Buteo galapagoensis

Galápagos hawk

Chelonia mydas agassisi

Galápagos green turtle

Conolophus spp.

Land iguana

Geochelone elephantopus

Galápagos giant tortoise

Grapsus grapsus

Sally lightfoot crab

Phalacrocorax harrisi

Flightless cormorant

Phoebastria irrorata

Waved albatross

Spheniscus mendiculus

Galápagos penguin

Sula nebouxii

Blue-footed booby

Zalophus wollebaeki

Galápagos sea lions

See text for other species.

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Grant, Peter and Rosemary 273 The Galápagos Islands offer very little in the way of natural resources. They have been used for centuries as a place where ships could stop, but they were not even very good for this, for they have very little freshwater. The tortoises were actually a popular attraction for sailing ships. Because of their slow metabolism, the tortoises could survive for many weeks in the cargo holds of the ships and could supply fresh meat on long voyages. When Darwin visited, one of the islands was used as a prison colony. Since none of the native animals (except the tortoises) had economic value to the Europeans, they introduced livestock that could survive the harsh island conditions. Today, populations of feral animals continue to damage the natural vegetation. The most abundant feral animal is the goat. Because of grazing by goats, the native cactus Opuntia megasperma nearly became extinct; the tortoises, now rare, also dispersed the cactus seeds. Goats have been eradicated from some of the islands. Introduced black rats (Rattus rattus) attack young tortoises. Rats prevented tortoises from reproducing on the island of Pinzón for a half century, during which time only adult tortoises lived on the island. Cows and donkeys have been introduced also, which eat the vegetation and compete with native animals for water. Feral dogs and cats often kill birds. A considerable part of the Galápagos Islands is Ecuadorian national parkland. Cruise ships and airplane flights take thousands of tourists each year to see some of what Darwin saw. In 2007, the United Nations Educational, Scientific and Cultural Organization (UNESCO) declared the Galápagos Islands to be endangered by invasive species, immigration, and the impact of tourism. After the Ecuadorian government took measures to control these problems, UNESCO removed the Galápagos Islands from its list of endangered habitats in July 2010. See also adaptive radiation; biogeography; Darwin, Charles; Darwin’s finches; hybridization; invasive species; natural selection; speciation. Further Reading Adsersen, Henning. “The rare plants of the Galápagos Islands and their conservation.” Biological Conservation 47 (1989): 49–77. Campbell, Karl, et al. “Eradication of feral goats Capra hircus from Pinta Island, Galápagos, Ecuador.” Oryx 38 (2004): 328–333. Causton, C. E., et al. “Alien insects: Threats and implications for conservation of Galápagos Islands.” Annals of the Entomological Society of America 99 (2006): 121–143.

xviii+598_Biodiversity_F.indd 273

Charles Darwin Foundation. “Charles Darwin Foundation.” Available online. URL: http://www.darwinfoundation.org/english/pages/index.php. Accessed July 28, 2010. DeRoy, Tui. Galápagos: Preserving Darwin’s Legacy. Ontario: Firefly Books, 2009. Dowler, Robert C., et al. “Rediscovery of rodents (genus Nesoryzomys) considered extinct in the Galápagos Islands.” Oryx 34 (2000): 109–117. Galápagos Conservancy. Available online. URL: http:// www.galapagos.org/2008/index.php?id=68. Accessed August 8, 2011. Kricher, John. Galápagos: A Natural History. Princeton, N.J.: Princeton University Press, 2006. Stewart, Paul D. Galápagos: The Islands that Changed the World. New Haven, Conn.: Yale University Press, 2007. Whiteman, Noah Kerness, et al. “Disease ecology in the Galápagos Hawk (Buteo galapagoensis): host genetic diversity, parasite load and natural antibodies.” Proceedings of the Royal Society of London B (Biology) 273 (2006): 797–804.

genetic drift  See founder effect and genetic

drift.

Grant, Peter and Rosemary  (1936–  ) and

(1936–  )  British  Evolutionary biologists  Peter Raymond Grant and Barbara Rosemary Grant are among the most famous living evolutionary biologists. Their work with Darwin’s finches on the Galápagos Islands has provided the most thorough set of data upon which modern scientists base their understanding of how evolution produces biodiversity. Since 1973, they have spent half of each year on the islands of Daphne Major and Genovesa. They have numbered, tagged, and measured nearly every finch on Daphne Major and recognize most of them. In this way, they can understand the lives of each of the finches as if they were part of a complex Russian novel. They can determine which finches mate with which others and which finches are their offspring. In this way, they have been able to demonstrate the heritability of traits; natural selection acting upon those traits; and character displacement in those traits caused by competition between finch species. Peter Grant was born October 26, 1936, in London, and attended Cambridge University. Rosemary was born on October 8, 1936, in a small village on the northwest coast of England and attended Edinburgh University. Both grew up with a passion for the natural world. Peter met Rosemary when he was a graduate student and she a lecturer at the ­University

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274 grasslands and savannas  274 of British Columbia. They married, and Peter completed his graduate work on the evolution of birds on tropical islands. Peter and Rosemary went to Yale University, he as a postdoctoral researcher and she as a lecturer. They had two daughters, both of whom undertook research projects, later published, in the Galápagos. After university positions in Montreal and Michigan, and after Rosemary completed her doctoral degree, both Peter and Rosemary became faculty members at Princeton University. Both have retired but continue their research. Rosemary’s greatest wish is “that we have transmitted, and will continue to transmit, some of our own sense of wonder, joy, and excitement in curiosity-driven research and in life to our students and to others.” See also Darwin’s finches; Galápagos Islands; natural selection. Further Reading Grant, Peter, and Rosemary Grant. “In Charles Darwin’s footsteps.” Available online. URL: http://www. inamori-f.or.jp/laureates/k25_b_peter/img/lct_e.pdf. Accessed August 15, 2010. Weiner, Jonathan. The Beak of the Finch: A Story of Evolution in Our Time. New York: Knopf, 1994.

grasslands and savannas  Grasslands are

regions dominated by grasses, and savannas are grasslands with individual trees. Even though grasses comprise the majority of the biomass of grasslands, most of the species of plants are forbs, which are herbaceous wildflowers. Grasslands are generally found in regions that are drier than boreal forests or temperate forests but wetter than deserts. Grasslands are not defined by temperature; some grasslands, such as the prairies of Saskatchewan, can be very cold, while others, such as the prairies of Texas, can be very warm, and yet not only be grasslands but contain many of the same grass and forb species. Buffalo grass (Buchloë dactyloides) is one of the species that grows from Texas to Saskatchewan. Grasses, along with sedges, rushes, and cattails, can dominate marshes, such as the Everglades of Florida, which are treeless and flooded; these are not called grasslands. The wettest grasslands in North America are the tallgrass prairies, which once dominated what is now western Minnesota, Iowa, eastern North and South Dakota, eastern Nebraska, eastern Kansas, and north central Oklahoma (see table on page 275). Many of the grasses and forbs could grow over six feet (two m) tall; a person on horseback could hide in some of these grasslands. They received enough rain and snow that deciduous broad-leaved forests could grow in these regions. However, periodic fires burned the tallgrass prairies, killing any trees

xviii+598_Biodiversity_F.indd 274

first entry that happened to grow there. The grasses and forbs would resprout from underground buds. The fire would not only remove the trees but also transform dead grass stalks into ashes that acted as fertilizers and allowed sunshine to warm the ground more quickly in the springtime. Fires, by keeping out the trees and promoting the growth of grasses and forbs, were essential to the tallgrass prairie. Therefore the grasses themselves help to maintain the boundary between prairie and forest. The tallgrass prairie became established during a period of weather after the most recent of the ice ages that was warmer and drier than the present—when it was too dry for forests to grow there. After wetter weather returned, fires kept the deciduous trees from growing there. The tallgrass prairie was one of the last regions to be converted to agriculture; the thick sod, with roots penetrating up to 10 feet (three m) into the soil, could not be plowed until the invention of the steel plow. The topsoil, very rich and deep, proved to be some of the world’s best soil, and nearly the entire tallgrass prairie was converted to farmland. Most of it today is dominated by another tall grass: corn. For the most part, only small parcels of prairie were protected, mostly as pioneer cemeteries and railroad rights-of-way (see photograph). The tallgrass prairie has been more completely destroyed than any other natural habitat on Earth. The driest grasslands are the shortgrass prairies, forming a band across western North and South Dakota, Nebraska, Kansas, and Oklahoma, and eastern Montana, Wyoming, Colorado, and New Mexico. There is also shortgrass prairie (the Palouse)

A remnant tallgrass prairie grows along a railroad track in Illinois. Most original prairies are found near railroads or cemeteries, the only places that were not transformed into farmland by settlers. The railroad company bulldozed the prairie plants that were along the track in the mistaken impression that the plants were a nuisance. Soon thereafter, the embankment began to erode and was soon filled with ragweeds and poison ivy, which the thick prairie sod had previously kept out.  (Stanley A. Rice)

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grasslands and savannas  275 Important Prairie Grass and Forb Species of North America Primarily Associated With: Species

Common Name

Tallgrass

Mixed-Grass

Shortgrass

Forbs Allium textile

Textile onion

x

Amorpha canescens

Leadplant

x

Baptisia australis

Blue wild indigo

x

Baptisia bracteata

Cream wild indigo

Comandra umbellata

False toadflax

Delphinium carolinianum

Prairie larkspur

Echinacea pallida

Pale purple coneflower

Echinacea purpurea

Purple coneflower

Eryngium leavenworthii

Leavenworth eryngo

Eryngium yuccifolium

Rattlesnake master

Gaillardia pulchella

Blanket flower

Geum triflorum

Prairie smoke

Gaura coccinea

Scarlet gaura

Helianthus tuberosus

Jerusalem artichoke

Helianthus maximiliani

Maximilian sunflower

x x x x x x x x x x x x

Liatris punctata

Dotted blazing star

Liatris pycnostachya

Prairie blazing star

Lithospermum incisum

Fringed puccoon

Oenothera caespitosa

Evening primrose

x

Opuntia fragilis

Fragile prickly pear cactus

x

Oxytropis lamberti

Purple locoweed

x

Pediomelum esculentum

Prairie turnip

x

Penstemon cobaea

Showy beardtongue

Pulsatilla patens

Pasqueflower

Ratibida columnifera

Prairie coneflower

Ratibida pinnata

Gray-headed coneflower

Silphium laciniatum

Compass plant

Silphium terebinthinaceum

Prairie dock

Sphaeralcea coccinea

Scarlet globemallow

Zigadenus elegans

White camass

Zigadenus venenosus

Death camass

x x x

x x x x x x x x x

Grasses Andropogon gerardi

Big bluestem

Bouteloua curtipendula

Sideoats grama

Bouteloua gracilis

Glue grama

Buchloë dactyloides

Buffalo grass

Panicum virgatum

Switchgrass

Pascopyrum smithii

Western wheatgrass

x

Schizachyrium scoparium

Little bluestem

x

Sorghastrum nutans

Indian grass

xviii+598_Biodiversity_F.indd 275

x x x x x

x

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276 grasslands and savannas  276 in eastern Oregon and Washington. Shortgrass prairie also grew on the foothills of the Sierra Nevada in California. The topsoil and plant roots are much shallower in the shortgrass than in the tallgrass prairie. The grasses such as the grama grasses (see table on page 275) may be only a foot (⅓ m) tall; some, such as buffalo grass (Buchloë dactyloides) may be only four inches (10 cm) tall. It is the lack of moisture that keeps trees from growing in the shortgrass prairie; where water is available, as along rivers, trees (mostly cottonwood, Populus deltoides) can grow. Fire is essential to maintaining the shortgrass prairie also, not by killing tree seedlings but by killing cool desert shrubs such as sagebrush in the Great Basin and warm desert shrubs such as creosote bush in the southern Great Plains. A band of grasslands intermediate between tall and shortgrass prairies dominate the landscape across central North and South Dakota, Nebraska, Kansas, and Oklahoma, making up the mixed-grass prairies, dominated by grasses that grow about three feet (one m) tall (see table on page 275). The grasses and forbs of the tallgrass, mixedgrass, and shortgrass prairies of North America are often different species of the same genus that have different abilities to tolerate drought. For example,

first entry the prairie dock, Silphium terebintinaceum, has enormous leaves without lobes, while the compass plant (S. laciniatum) has smaller leaves that are lobed. Smaller leaves and lobes allow a leaf to disseminate its heat load without transpiring as much water. In addition, the compass plant tends to orient its leaf blades to face east and west (hence its name), thus avoiding direct sunlight at noon. The forbs of the tallgrass prairie, like the grasses, have deep roots. In the shortgrass prairies, however, the root sod is formed mostly by the grasses; the forbs grow mostly in areas disturbed by animals and erosion. Grasslands around the world contain or once contained large grazing mammals and other mammals such as rodents that act as keystone species that determine the structure of the entire ecological community. Grasses and grazing mammals have coevolved: The mammals have complex digestive systems with symbiotic bacteria that allow them to digest coarse grass, while the grasses grow from buds that are near or below the surface, allowing them to grow back after grazing as well as after fire. Grasslands and savannas are found in California, Australia, South America (especially the ­pampas of Argentina), the steppes of Central Asia, and the

The savannas of Africa support many large mammals, such as elephants.  (Fogstock)

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grasslands and savannas  277

Selected Grasses and Large Animals of Grasslands North American Prairie

Californian Grassland

Argentine Pampas

Central Asian Steppe

African Savanna

Dominant grasses x

Aristida congesta Aristida purpurea

x

x x

Bromus brevis x

Bromus carinatus

x

Bromus japonicus Bromus kalmii

x x

Bromus tectorum x

Eragrostis diffusa Eragrostis intermedia

x x

Eragrostis pilosa

x

Eragrostis superba Koeleria cristata

x

x x

Koeleria permollis

x

Panicum maximum Panicum virgatum

x x

Schizachyrium condensatum Schizachyrium scoparium

x x

Sporobolus africanus x

Sporobolus cryptandrus Sporobolus heterolepis

x

Stipa breviflora

x

Stipa capillata

x

Stipa grandis

x x

Stipa ichu x

Stipa occidentalis (Achnatherum)

x

Stipa papposa x

Stipa pulchra (Nassella)

x

Stipa sibirica Stipa spartea (Heterostipa)

x

Large animals Acinonyx jubatus (cheetah)

x

Antilocapra americana (pronghorn)

x

Bison bison (bison)

x

Cervus elaphus (Tule elk) Chlamydotus undulata (jerboa)

x x (continues)

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278 grasslands and savannas  278

first entry

Selected Grasses and Large Animals of Grasslands (continued) North American Prairie

Californian Grassland

Argentine Pampas

Central Asian Steppe

African Savanna

Large animals Connochaetes taurinus (wildebeest) Cynomys ludovicianus (prairie dog)

x x

Equus grevyi (Grévy’s zebra)

x

Equus hemionus (wild ass)

x

Eudorcas thomsoni (gazelle)

x

Gazella subgutturosa (gazelle)

x

Giraffa camelopardalis (giraffe)

x

Lagidium viscacia (viscacha)

x

Lama guanicoe (guanaco)

x

Lama glauca (vicuña)

x

Leptailurus serval (serval)

x

Loxodonta africana (elephant)

x

Mustela nigripes (black-footed ferret)

x

Oryx gazella (gemsbok)

x

Panthera leo (lion)

x

Rhea americana (rhea) Struthio camelus (ostrich)

savannas of Africa as well as central North America. Each of these grasslands has unique native species of dominant plants and keystone mammals not found in the others (see table on pages 277 and 278). Grasslands of the Middle East still contain grass species that were the ancestors of domesticated wheat, oats, and rye. Some genera of grasses grow only in one geographical area, as Andropogon and Bouteloua in central North America. Other grass genera grow in more than one region, such as species of Stipa that grow in many Northern Hemisphere grasslands. Before European settlement, native grass species dominated the grasslands of California. Since the coming of the Spaniards, however, European livestock created conditions that allowed European grasses to be superior competitors. The native grasslands are largely gone, and the native grasses nearly extinct, in California. Invasive grasses have filled large areas of western North America as well. Introduced European and Asian grasses are abundant, especially cheatgrass (Bromus tectorum) throughout the western United States, Japanese brome (Bromus japonicus) in the shortgrass prairie regions, and wild oats (Avena fatua) in California.

xviii+598_Biodiversity_F.indd 278

x x

Cheatgrass and brome also grow in disturbed areas of what was once tallgrass prairie, where they grow quickly early in the season before larger grasses become active. Savannas are grasslands with widely spaced trees, such as Acacia tortilis in Africa, sandpaper trees (Curatella americana) in South America, post oaks (Quercus stellata) in central North America, and blue oaks (Quercus douglasii) in California. The trees utilize water from deep in the soil, while the grasses and forbs utilize water in the shallow part of the soil. The savannas of Africa teem with wildlife: huge herds of grazing mammals such as wildebeests and elephants (see figure on page 276) and many predators such as lions. Humans evolved under savanna conditions. The grasslands of North America and Australia also teemed with wildlife, but many species of large mammals became extinct coincident with the first arrival of humans: about 50,000 years ago in Australia and at the end of the most recent ice age in North America. Many scientists conclude that massive extinctions of large mammals occurred when technologically advanced humans (for example, with spears) encountered them for the first time,

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greenhouse effect  279 but such extinctions did not occur in places such as Africa in which the large mammals and humans had evolved together for millions of years. The most famous large mammal of the North American prairie is the bison. When white Americans were traveling and homesteading across the Great Plains, they saw herds of millions of bison, and Native Americans hunting them. They assumed that this is the way it had always been—then proceeded to attempt the extermination of the bison in order to undermine the economy of the Native tribes. Recent scholarship has suggested, however, that hunting by Native Americans had kept the bison populations under control for thousands of years, and the bison population exploded only after diseases such as smallpox reduced Native populations by as much as 90 percent. A similar explanation has been offered for why there were so many billions of passenger pigeons in the forests of eastern North America just prior to white American expansion. According to the earliest explorers, who visited Native tribes prior to their decimation by smallpox, Native Americans extensively transformed the landscape by agriculture and fire. If this is true, then much of the “original” distribution of the North American prairies, immediately before white settlement, may have been as much due to Native American land management as to natural processes. See also communities, ecological; deserts, cool; deserts, warm; disturbances, ecological; invasive species; keystone species; marshes and swamps.

Kirt, Russell R. Prairie Plants of the Midwest: Identification and Ecology. Champaign, Ill: Stipes Publishing, 1998. Kurtz, Carl. A Practical Guide to Prairie Reconstruction. Iowa City: University of Iowa Press, 2001. McNaughton, S. J. “Serengeti grassland ecology: The role of composite environmental factors and contingency in community organization.” Ecological Monographs 53 (1983): 291–320. Manning, Richard. Grassland: The History, Biology, Politics, and Promise of the American Prairie. New York: Penguin, 1997. Menke, John W. “Grazing and fire management for native perennial grass restoration in California grasslands.” Fremontia 20 (1992): 22–25. Moul, Francis, and Georg Joutras. The National Grasslands: A Guide to America’s Undiscovered Treasures. Lincoln: University of Nebraska Press, 2006. O’Connor, T. G., et al. “Influence of precipitation and species composition on phytomass of a semi-arid African grassland.” Journal of Ecology 89 (2002): 850–860. Seabloom, Eric W., et al. “Invasion, competitive dominance, and resource use by exotic and native California grassland species.” Proceedings of the National Academy of Sciences USA 100 (2003): 13,384–13,389. Tilman, David, and John A. Downing. “Biodiversity and stability in grasslands.” Nature 367 (1994): 363–365. Uys, Roger G., et al. “The effect of different fire regimes on plant diversity in southern African grasslands.” Biological Conservation 118 (2004): 489–499.

Further Reading

greenhouse effect  The Earth is getting warmer

Archer, Steve, et al. “Autogenic succession in a subtropical savanna: Conversion of grassland to thorn woodland.” Ecological Monographs 58 (1988): 111–127. Brown, Lauren. Grasslands. New York: Knopf, 1985. Carlsen, Tina M., et al. “Reducing competitive suppression of a rare annual forb by restoring native California perennial grasslands.” Restoration Ecology 8 (2001): 18–29. Hamilton, J. G., et al. “Coexistence and interference between a native perennial grass and nonnative annual grasses in California.” Oecologia 121 (1999): 518–526. Hayes, Grey F., and Karen D. Holl. “Cattle grazing impacts on annual forbs and vegetation composition of mesic grasslands in California.” Conservation Biology 17 (2003): 1,694–1,702. Hector, A., et al. “Plant diversity and productivity experiments in European grasslands.” Science 286 (1999): 1,123–1,127. Huenneke, Laura Foster, et al. “Effects of soil resources on plant invasion and community structure in Californian serpentine grassland.” Ecology 71 (1990): 478–491.

xviii+598_Biodiversity_F.indd 279

and humans are the principal cause. Humans have increased the amount of carbon dioxide (CO2) gas in the atmosphere, and this gas retains heat in the atmosphere, in a manner suggestive of the way a glass roof holds sunlight heat in a greenhouse. Along with global warming have come many other changes in climate. Consensus of scientists on these points, and about the importance that they have for the future of natural ecosystems and human society, has grown over recent decades and is now as strong as any scientific consensus can be.

The Earth Is Getting Warmer In order to determine whether global climate is becoming warmer, it is necessary to determine temperature patterns over extended periods of time and over the whole Earth. Climate can be thought of as a long-term average of weather conditions. One hot year does not prove that global climate is becoming warmer. However, scientific evidence shows that the climate of the entire Earth has gotten abruptly warmer in the last couple of centuries.

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280 greenhouse effect  280

first entry

Direct temperature readings since 1860.  Since scientists began recording temperatures in many parts of the world about 1860, global average temperatures have significantly increased (see figure below). According to the National Oceanic and Atmospheric Administration (NOAA), the warmest years on record for Earth as a whole were 2005 and 2010. The average temperatures in 2009 were virtually the same as 1998, 2002, 2003, 2006, and 2007, tying for second place. A La Niña weather pattern caused 2008 to be cooler, but this pattern did not persist. The year 2009 was the warmest on record for the Southern Hemisphere. The first decade of the 21st century was the warmest since worldwide thermometer readings have been made. Moreover, North Atlantic Ocean temperatures also show a pattern of recent warming. This is the sort of evidence that is required to show that global climate has become warmer since the beginning of the Industrial Revolution and particularly in the past half century—and the evidence has been found. The Earth has not only become warmer, but abruptly warmer. Abrupt warming occurred between 1980 and 2000. Although the first decade of the 21st century was the warmest on record, the warming trend did not make the end of the decade significantly warmer than its beginning. According to Earth scientist Susan Solomon at NOAA, the reason for this might be water vapor in the stratosphere. Higher than normal atmospheric humidity from 1980 to 2000 enhanced global warming, while lower than normal humidity has repressed global warming since that time. Even though weather is not climate, it is possible to assign a probability that global warming has contributed to particular weather events. Climate scientists can use their computer models to calculate the probability that certain climatic events

would have happened without the extra carbon dioxide that has been released into the atmosphere since the beginning of the Industrial Revolution. These models take into account natural factors, such as the movement of the Earth and the El Niño Southern Oscillation of ocean currents. This approach allows scientists to state that about half of the 2006 North American heat wave could be attributed to global warming and half to natural variability. It is therefore possible to say in retrospect that global warming has contributed to the overall pattern of weather events. A few scientists deny either that global temperatures are increasing or that human activities are an important cause. They have not, however, verified their claims in the scientific literature. Their claims are largely limited to their own Web sites or to books published by organizations that have received funding from corporations that have a vested interest in the continued burning of fossil fuels. Even though few scientists and no published data call global warming into question, journalists and the public have tended to perceive the claims of “global warming skeptics” as potentially valid. Science historian Naomi Oreskes surveyed 928 scientific articles that dealt in some way with global climate change. None of these articles denied that global warming was occurring. However, when she surveyed 636 articles published in popular media, 53 percent of them gave credibility to the claims of those who deny global warming. Apparently the public has been misled about the scientific consensus on global warming. Oreskes, along with atmospheric technologist Erik Conway, documented that the leading deniers of global warming are not climatologists but nuclear engineers who have specialized in attacking a whole range of scientific issues, including the link between smoking and cancer and the effects of pollution on the natural environment. Proxy methods for temperatures in recent centuries.  But a century is not a very long time. The important question is not whether the climate is getting warmer, but whether this increase in global temperature is the result of human activity. If humans are partly or largely responsible for global warming, it must have occurred since the beginning of the Industrial Revolution and accelerated as industrial pollution During the past century and a half, global temperatures have increased. has spread throughout the world. The increase has not been uniform; it was especially rapid after particulate If this is the case, the recent air pollution was brought under control after about 1960.  (Based on the National Climatic Data Center) increase in temperature must be

xviii+598_Biodiversity_F.indd 280

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greenhouse effect  281 greater than any that occurred in the past one or two millennia. Therefore scientists have investigated temperature patterns farther into the past than is possible with just the “instrumental” (thermometer) data. Scientists must use other methods to estimate temperatures before that time. Several of these “proxy” methods have been developed. One example of a proxy method is the measurement of tree rings. Each year, trees add another layer of wood just underneath the bark. The layer is visible as a ring because the wood produced in the spring is more porous, therefore lighter in color, than wood produced in late summer. The age of the tree can be accurately determined by counting the rings all the way to the center of the trunk. During years with favorable weather conditions, trees produce a thick ring of wood; when the weather is poor, the ring is thinner. Good and bad weather result from temperature and moisture conditions. For trees in the north, good years are warm and bad years are cool; for trees in the south, good years are wet and bad years are dry. The barcode pattern of thick and thin layers of wood represents a record of good and bad years, extending back into the past, as long as the tree has been alive. Some trees, such as the bristlecone pines of California, have been alive and accumulating layers of wood for more than 4,000 years (see figure). Dendrochronologists, scientists who study tree rings, do not limit themselves to the study of trees that are alive right now. If they find a well-preserved log, they can line up the barcode pattern of thick and thin rings in the log with those in a living tree, allowing them to determine what year the tree died. They can then extend the tree ring record back to the year the dead tree had begun growing. By this method, forest scientist Edward Schulman was able to determine that a certain bristlecone pine log at the Ancient Bristlecone Pine Reserve in California, now called the Schulman Log, began growing about 1530 b.c.e. and died in 1676 c.e. at the age of 3,206 years. Tree rings in very long-lived trees are more difficult to interpret than those in trees that grow faster and have shorter life spans. But the climate record from tree rings is fairly reliable for the past thousand years, especially when verified by other proxy methods such as the chemistry of the annual layers of sediment on continental shelves. The conclusion of these proxy methods is that the global climate today is hotter than it has been at any time in the past thousand years, and the current warming trend is faster than any warming trend during that period. Several different proxy reconstructions of past temperatures have been published by scientists, and all are in close agreement with this major conclusion. The most famous of these graphs

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Bristlecone pine trees (Pinus longeava) grow very slowly for thousands of years and produce very thin layers of wood. Each layer is about a hundredth of an inch (less than a third of a millimeter) wide. Some are thicker than others, however, and scientists use this information to reconstruct the history of climate change.  (Stanley A. Rice)

is climate scientist Michael Mann’s “hockey stick model,” so called because a long period of relatively stable temperature (the hockey handle) has given way to a sudden warming as brief and abrupt as the end of a hockey stick. Other researchers have independently compiled similar data (see figure on page 282). Since its publication in 1998, Mann’s graph has withstood criticisms, one of which involves the so-called Medieval Warm Period and Little Ice Age. Over the past millennium in Europe, the average temperature has fluctuated. Temperatures were higher during the Medieval Warm Period in the 14th century and thereafter became cooler, producing what has been named the Little Ice Age. Some observers noted that Mann’s graph does not show these two events. It turns out, however, that these phenomena may have been limited to the Northern Hemisphere, rather than global in extent. One reason for the fame of this graph is that it so angered a member of Congress (Joe Barton, a Republican from Texas) that he began an investigation into Mann’s competence, a move that was widely recognized as an attempt to suppress the evidence for global warming. In 2006, a panel of the National Academy of Sciences confirmed Mann’s data, although it noted that the estimates of temperatures of the past four centuries are more reliable than the estimates of the older dates. The Intergovernmental Panel on Climate Change (IPCC) is a group of scientists and government representatives from more than 100 nations, including the United States, brought together by the United Nations Environment Programme (UNEP) and the World Meteorological Organization. Their reports

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This reconstruction of global temperatures, based on proxy measures, shows estimated temperatures warmer than the average in orange and cooler than the average in blue, with light orange and blue error ranges. Global temperatures have been higher, and cool temperatures less frequent, during the last century than at any time in the past millennium.  (Based on fi gures from the National Climatic Data Center)

represent as close to an international consensus on global warming as we can hope to expect. a 2007 report from the iPcc contained a figure that shows essentially the same pattern as the original graph by Mann. Temperature estimates from ice cores. But even a millennium is not very long in terms of human existence, not to mention that of the planet. climate change has been occurring throughout earth’s history. among the most dramatic changes have been the ice ages. For about the past 2 million years (since the beginning of the Pleistocene epoch), the northern Hemisphere has undergone a series of glacial cycles. During each one, cold temperatures have caused glaciers to accumulate and spread southward from the arctic Ocean (glaciation), and warm temperatures have caused them to melt and retreat (interglacial periods). each cycle has lasted about 100,000 years; therefore, since the beginning of the Pleistocene 2 million years ago, about 20 glacial cycles have occurred. each glacial advance effaces much of the evidence of earlier cycles, but direct evidence, such as grooves scratched in rocks and piles of rubble left by melting glaciers, can be found for at least four. the most recent glaciation ended about 14,000 years ago, and the glaciers began to melt rapidly, ushering in the most recent interglacial period, which is still going on. about 7,000 years ago, peak interglacial temperatures occurred, producing warm and dry conditions across much of north america. after that time, temperatures decreased, as the northern Hemisphere headed toward the next glaciation. this raises the question of whether the recent global warming is merely part of a natural cycle of warming. there are at least three reasons why this is not the case.

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First, global temperatures were decreasing after the interglacial temperature maximum about 7,000 years ago; recent warming represents a departure from this trend. Second, global warming since 1850 has occurred faster than previous periods of global warming. Finally, global temperatures appear to be as high as, if not higher than, at any time during any of the most recent glacial cycles.

the evidence for these three claims comes primarily from the study of ice cores. in some parts of the world, snow has accumulated for many thousands of years. as new snow piles up, the old snow underneath it is compressed into ice. For example, ice has amassed in glaciers in the andes Mountains of South america and on Mount Kilimanjaro in africa. the longest accumulation of snow has occurred in the thick ice caps of Greenland and antarctica. the antarctic ice can be two miles thick and heavy enough to press the mountainous continent of antarctica down below sea level. Scientists can (with considerable difficulty) drill down into this ice, and remove cylinders that (in the case of the Vostok ice core from antarctica) date back more than 400,000 years. like tree rings, ice builds up in easily visible layers, caused by annual cycles of snow. the age of a layer of ice, therefore, can be determined by counting the layers downward from the top (see photograph on page 263). as with tree rings, the layers reveal much more than just the age of the ring. First, scientists can determine whether the year that the ice layer formed was relatively warm or cool. each water molecule contains one oxygen atom. Most oxygen atoms have an atomic weight of 16, resulting in a molecule of H 216O. a relatively small number of oxygen atoms, however, are heavier isotopes, with an atomic weight of 18, producing H 218O molecules. the lighter water molecules evaporate from the ocean surface more readily than the heavier molecules and accumulate in the ice on land. a greater proportion of light water in the ice layer indicates a cool year in which a greater amount of ice built up. Scientists also measure the ratio of deuterium (2H) to hydrogen (1H) as a temperature proxy. Second, there are bubbles of air trapped in the ice (also visible in the figure). Scientists can remove the gas from the ice layer and measure the amounts of each kind of gas that was

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Scientists remove cylinders of ice from places such as Greenland and Antarctica, where snow accumulated for hundreds of thousands of years and was then compressed into ice. Each layer represents one year of accumulation. The chemistry of each layer indicates the global climate during that year. Air bubbles in the ice are actual air samples from that year.  (American Museum of Natural History; Stanley A. Rice)

in the atmosphere at the time the layer was formed. The importance of this procedure will become obvious a little later in this entry. Using this information, scientists can reconstruct a record of global average temperatures reaching back as far in the past as the ice layers will allow. An analysis of the changes in global temperature derived from the Vostok ice core from Antarctica clearly reveals the four most recent glacial cycles, each with glacial and interglacial periods (see figure). Global temperatures have not yet increased beyond those of previous interglacial periods, but, as previous graphs have shown, that increase is now occurring rapidly. Global warming is nothing new in Earth’s history; but the current rate of global warming is 10 times as rapid as the warming that occurred at the end of the most recent glaciation. There is other evidence that global temperatures have been increasing during the recent centuries and millennia. The most famous evidence is that,

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all around the world, ice that has accumulated for thousands of years is beginning to melt. In Antarctica, shelves of sea ice have been breaking off and forming icebergs. Because Antarctica is the coldest place on Earth, and because it has so much ice, scientists had expected that global warming would melt Antarctic ice slowly and gradually. Much to their surprise, they found that it is melting more rapidly than they could have imagined. The Larsen B ice shelf in Antarctica, the size of Rhode Island, rather than gradually melting, collapsed over the course of two months in 2002, most of the cavein occurring during two eventful days. A portion of the Wilkins ice shelf collapsed in March 2008. Meanwhile, in Greenland, sheets of land ice are melting and retreating. As in Antarctica, Greenland ice is thick, and scientists expected it to melt slowly. They were surprised to discover in 2006 that water from glacial melt leaks down to the bottom of the glacier and lubricates it, allowing local ice masses

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discrete current. Part of this system is the Gulf Stream, in which warm surface water moves from the tropical Atlantic up toward western Europe. This warm water makes the air warmer in western Europe than at the same latitudes in Canada. From there, the warm water descends abruptly to the bottom of the north Atlantic and moves down the east coast of South America. It flows eastward over Antarctica. The water, now cool, flows northward to the Tropics, becomScientists use ice core information to reconstruct global climate and ing warmer as it moves north global atmospheric carbon dioxide concentration for the last four glacial toward Japan and turns east, cycles. Changes in global temperature (blue line) and of atmospheric bringing warm weather to the carbon dioxide (red line) closely match each other. They cause each other: Warmer temperatures stimulate decomposers to release carbon vicinity of British Columbia from soils, and carbon dioxide enhances global temperatures. In the past, and Washington. The water global temperatures changed before carbon dioxide, but at the present moves back toward Australia, time, carbon dioxide changes are causing global warming.  (Based on south of Asia and Africa, and figures from the National Climatic Data Center) back to the tropical Atlantic Ocean where it replenishes to move relatively rapidly toward the ocean. In addithe Gulf Stream. ●● When warm water flows from tropical Asia tion, historical records and comparisons of photoward South America, surface waters are tographs prove that glaciers all over the world are warm and El Niño storms are strong and melting away. The glaciers in the Andes and on Kilifrequent in South America. When cooler manjaro may be gone in just a few decades. Finally, water, drawn from the ocean depths off the extent and thickness of the sea ice in the Arctic of South America, flows toward tropical Ocean are decreasing. Just in the past half-century, Asia, drier La Niña conditions prevail in the Arctic ice cap has become 20 percent smaller South America. Nobody knows how these and several yards thinner. Given that some of this ocean currents interact. Is the global conice has built up (and left a virtually uninterrupted veyor current a cause, or an effect, of clirecord of ice layers) over hundreds of millennia, the mate change—or both? The shifting effects conclusion is unavoidable that global temperatures of ocean currents on global temperature are heating up faster than at any time in the past patterns are one of the reasons that global 400,000 years, and perhaps more than at any time warming has not occurred uniformly dursince the beginning of the Pleistocene. In 2009, for ing the past century. the first time in recorded history, ships were able to sail across the top of Canada (the fabled NorthThe fact that ocean currents make a tremenwest Passage). Two vessels owned by Beluga Shipdous difference in global temperature patterns is ping, based in Bremen, Germany, sailed from South demonstrated by something that happened about Korea to Siberia to the Netherlands. 3 million years ago. Before the isthmus of Panama Effects of ocean currents.  One of the most arose at that time, ocean water moved unimpeded important factors in global climate patterns is the through the gap between North and South America movement of ocean currents. They redistribute heat on its way to the Arctic Ocean. This strong curfrom tropical zones to the high latitudes throughout rent delivered enough warmth to the arctic regions the world. Two important patterns of ocean currents that broad-leaved deciduous trees were able to grow are the global conveyor current and the El Niño nearly to the North Pole. The formation of the isthSouthern Oscillation (ENSO). mus of Panama considerably weakened this current, so that deciduous trees now form extensive forests ●● The “global conveyor” current is a general only about halfway to the North Pole. Scientists pattern of water movement rather than a

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greenhouse effect  285 have concluded that this cannot be the entire reason that the North Pole was much warmer in the past than it is today, but the decrease in ocean currents was probably an important factor. If anything slowed or stopped the Gulf Stream, the weather in northern Europe could become much colder. This apparently happened about 12,800 years ago, right when the glaciers of the most recent ice age were melting and the Earth was becoming warmer. Very quickly, the warming trend reversed, and temperatures as cold as those of the glacial period returned. This massive cold snap is called the “Younger Dryas.” Dryas is the name of an arctic wildflower, whose range had retreated northward as the glaciers melted, but which quickly returned to Europe and North America when the temperatures became frigid again. The cold snap was apparently caused by a flood of freshwater that entered the North Atlantic. The collapse of a glacier released a huge amount of cold water through the St. Lawrence Seaway into the North Atlantic Ocean. The cold freshwater was lighter than the salt water of the ocean and remained near the surface of the North Atlantic. Then the warm Gulf Stream waters apparently sank long before they reached Europe. Europe, no longer receiving Gulf Stream warmth, experienced a rapid chilling. Nobody knows what caused this sudden glacial melt. Could the North Atlantic again be flooded with cold freshwater? The melting of Greenland ice could cause something like this to occur. Therefore the effects of global warming may, paradoxically, include a temporary, sudden cooling in Europe. This is, however, one of the predictions that has the least support among climate scientists. Sunspots also appear to affect global temperature. For example, there was very little sunspot activity during the Little Ice Age. As is the case with ocean currents, variations in sunspot activity appear to superimpose global temperature variations upon an overall warming trend.

Effects of Global Warming on the Earth It is clear that the Earth is becoming warmer. How much warmer will it become in the future? In order to predict future temperatures, scientists run complex “general circulation models” on some of the world’s most powerful computers. These models make, and integrate, predictions for each of many grid squares into which the Earth’s surface is divided. Different computer models are used at the Goddard Institute for Space Studies in New York, Lawrence Livermore Laboratories in California, the Hadley Centre at the University of East Anglia in England, and the Max Planck Institute in Germany. Although they are all different models, they yield very similar results. And

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there has been at least one opportunity to test the models for reliability. When the volcano Pinatubo erupted in the Philippines in 1991, it spewed particulate matter into the upper atmosphere. Using the Goddard Institute program, NASA climatologist James Hansen predicted that global temperature would decrease by about a half a degree F as a result. His prediction turned out to be very accurate. Global warming is raising the sea level.  During the most recent glaciation, the sea level was almost 300 feet (100 m) lower than it is today, because enormous amounts of water were locked up in glaciers. Then the glaciers melted and the ocean levels rose. Scientific measurements indicate that ocean levels are rising by about a quarter of an inch per year. The sea level appears to be rising at a faster rate than in the past, as a result of global warming. There are two reasons for this. First, when sea ice melts, the additional water does not alter the ocean level. But when global warming causes ice on land to melt, the water drains into the ocean and raises its level. Water from melting glaciers, especially in Antarctica and Greenland, is already causing the sea level to rise. If all of the ice melted, which may occur in a few centuries, the ocean levels would rise several feet. Second, as global temperature increases, the oceans become warmer, causing the water to expand. If the Greenland ice cap melted or just fragmented and fell into the ocean as icebergs, the ocean level would rise by almost 20 feet (about six m). The West Antarctic ice sheet, if it slid into the ocean, would cause the oceans to rise by a similar amount. (The East Antarctic ice sheet is much larger but is more stable and unlikely to collapse.) This rise would be enough to flood the major coastal cities of the world, such as New York, Boston, Washington, Los Angeles, San Francisco, Seattle, Shanghai, Tokyo, Bangkok, Bombay, London, and Marseilles. The ocean levels would rise slowly enough that people would have time to move, but the expense of moving and rebuilding—or, alternatively, of building sea walls—is nearly incalculable. The map of the world would be redrawn, including a Pacific Ocean in which several island nations have vanished and a United States with most of Florida missing. The sudden influx of glacial meltwater into the North Atlantic at the start of the Younger Dryas raised ocean levels by more than 30 feet. Global warming is causing more rainfall in coastal areas and droughts inland.  Warm air can hold more moisture than cool air. As a result, when temperatures rise, more water evaporates from the oceans, most of which falls in coastal areas. The average amount of rainfall in the world has already increased by 20 percent in coastal areas. But warm air can also cause more water to evaporate from

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286 greenhouse effect  286 plants and soil. Therefore, away from the oceans, in continental areas, rainfall could decrease. These continental areas include most of the agricultural region of the United States, where droughts are becoming more frequent. A study released in 2007 predicts that in the American Southwest droughts will become the norm rather than the exception. This region depends on water from snowmelt, and if snowfall decreases, large areas may experience droughts severe enough that crops cannot be irrigated. Meanwhile in the middle of Africa, droughts may become more frequent and intense. Moreover, the year 2010 was the ninth year of one of Australia’s worst droughts. This drought was followed, in 2011, by devastating floods. The drier conditions will undoubtedly cause more frequent, and more severe, wildfires. Fires burned large areas of forest worldwide in the summer of 2005, not only in the Tropics, but in Alaska as well. Another way in which global warming can contribute to continental drought is by causing glaciers to disappear. Millions of people depend on glacial meltwater in mountainous areas of South America and Asia. Glaciers are melting in the Andes and on Kilimanjaro. Global warming is causing stronger storms.  Even though 2005 had more hurricanes in the Atlantic and more typhoons and cyclones in the Pacific than any previously recorded year, the historical record of storms indicates that the frequency of hurricanes is not increasing. Every few decades, a period of either more or fewer hurricanes begins. However, recent hurricanes and other storms have been more severe than those in the past. In India, for example, there has been an increase in heavy storms, but not in the total number of storms, over the past half century. The intensity of storms is influenced by the warmth of the surface waters in the North Atlantic Ocean; warmer surface waters cause more evaporation and stronger wind, both of which contribute to creating intense storms. Hurricanes Katrina (in 2005) and Dean (in 2007) may therefore provide a very realistic glimpse into the kind of damage that will become commonplace in future decades, as global warming continues. In a warmer world, strong storms can also form in places where they have not previously occurred. The first recorded South Atlantic hurricane occurred in 2004. All of these processes can occur simultaneously. The last week of July 2010 saw not only the most severe flooding in Pakistan’s history but also a prolonged heat wave and drought in Russia that resulted in the worst forest fires in a century. Inevitable surprises.  With more sunlight energy being trapped in the climate systems of the Earth, the result will almost certainly not be a uni-

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first entry form warming of the planet. Instead, scientists expect that climate fluctuations will become more extreme. In effect, global warming is stirring the climate pot more vigorously. The exact results will be impossible to predict. In summer 2007, for example, Arctic sea ice melted at a much greater rate than had been predicted. The summer Arctic ice minimum had been declining at 8.6 percent per decade until 2005, then it declined almost 20 percent in 2007. This rapid rate of melting has not continued. One reason that the detailed patterns of climate change are unpredictable is that they occur by means of “tipping points” or “thresholds.” A complex system may be in a relatively stable state for long periods of time, then suddenly change to another stable state when a threshold is reached. Historical and sociological examples abound, such as revolutions and the Reformation. Engineering examples are also well known, in which a building or bridge suddenly collapses. Everyone knows about the proverbial “straw that broke the camel’s back.” Many scientific processes occur by means of threshold events. Rocks move along geological faults, not gradually, but suddenly: A major earthquake may occur after a buildup of pressure crosses a threshold. Chemical reactions may not occur at all until threshold conditions are reached. Climate change may occur slowly until some threshold incident catalyzes a cascade of events that feed on one another. Here are some examples: ●●

●●

The Arctic ice cap reflects a great deal of sunlight back into outer space; this reflected light, called albedo, does not cause the Earth to become warmer. But as the Arctic ice melts, the ocean that the ice formerly covered now absorbs more sunlight and retains the heat. Global warming causes the ice to melt, but the melting of the ice also causes more global warming. Decomposition of organic matter in peat bogs and soils around the world, especially in the far north, releases greenhouse gases such as carbon dioxide and methane (see next section) into the atmosphere. Huge areas of Siberia, including a continental shelf that today is under the sea but was exposed land surface during the most recent ice age, are producing huge amounts of methane. Some of these organic deposits are more than 150 feet (about 50 m) thick. Global warming causes more decomposition, and decomposition causes more global warming in the cold peat bogs; some bog lakes in Siberia no longer freeze in the winter because of the warmth created by decom-

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●●

position. In tropical areas such as Indonesia, global warming dries out peat bogs and encourages them to catch fire. Global warming also causes drier conditions in the interiors of continents. These drier conditions allow more wildfires to occur— which is what happened in thousands of square miles of tropical forests in 2005. The fires put greenhouse gases into the air and, at least temporarily, destroy the forests that could remove the greenhouse gases from the air. The exposed soils become warmer, which causes them to release more carbon dioxide.

Therefore, greenhouse gases cause global warming that causes the release of more greenhouse gases, resulting in more global warming. Because of the complex interactions in the natural world, the effects of global warming on wild species are difficult to predict. Humans may notice most of all the impact of global warming on the spread of organisms, such as mosquitoes, that carry diseases. In 2007, the World Health Organization announced that global warming threatened the livelihoods and health of millions of people, particularly in those countries that put the least carbon dioxide into the air. Therefore even the most sophisticated computer models of what will happen in the future can be erroneous. Leading climate scientists announced in 2007 that this is already proving to be the case. In an earlier 2001 report, the IPCC predicted future increases in atmospheric carbon dioxide, global temperature, and sea level. With each prediction, the IPCC scientists specified an error range, which means the increases might be less, or might be greater, than they had predicted. Since 2001, all three factors have been increasing even more rapidly than the IPCC predicted—and the increases have been right at the very top of the range of predicted possibilities. The climate predictions, as frightening as they have been, have already proven to be underestimates.

Atmospheric Carbon Dioxide Is a Cause of Global Warming The greenhouse effect makes the Earth warmer than it would otherwise be. In a greenhouse, sunlight shines in through the glass roof and heats up the plants and benches, which conduct heat to the air. The glass roof holds in a lot of the heat from this warm air and therefore acts as a largely oneway portal for heat to enter the greenhouse. Greenhouse gases (GHG) perform an analogous service for the Earth’s atmosphere. Light shines through the atmosphere and warms the Earth’s surface, which

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then emits infrared radiation. Infrared radiation is low-energy wavelengths of light that are invisible to humans. The Earth’s atmosphere consists mostly of nitrogen and oxygen gases. In an atmosphere that consisted only of nitrogen and oxygen gases, all of the infrared radiation would be lost into outer space. GHG molecules, however, absorb the infrared radiation, which makes them warm. They conduct some of their energy with the other gases in the atmosphere, making the whole atmosphere warmer. The more GHG molecules there are in the atmosphere, the warmer that atmosphere and the planet will be. Carbon dioxide (CO2) is the most famous greenhouse gas. The atmosphere contains only about 380 parts per million (ppm), or 0.038 percent, CO2 , by volume, fewer than four molecules out of every 10,000 in the atmosphere. But without this CO2 , the Earth would be uninhabitably cold. There are other GHG in the atmosphere, including water vapor and methane (the major component of natural gas). Methane is about a thousand times less common than CO2 in the atmosphere but at least 20 times as potent at retaining heat. However, of these three gases, only CO2 can accumulate indefinitely. Water vapor in the lower atmosphere can build up until it condenses as clouds and falls as rain. Methane reacts with oxygen gas, producing CO2 . Other GHG, such as nitrogen oxides and ozone, are even more potent and (in the case of ozone) persistent, but are rare compared to CO2 . Even though methane is rare and persists only about a decade in the atmosphere, scientists estimate that it is responsible for about 40 percent of the global temperature increase. Nitrous oxide is also a greenhouse gas. Although it is normally rare in the atmosphere, its concentration has been increasing because of China’s overuse of nitrogen fertilizer. The greenhouse effect is, to a certain extent, a good thing. Without it, the Earth would be about as cold as Mars now is. Mars itself has an atmosphere consisting mostly of CO2 , but its greenhouse effect is minor because its atmosphere is so thin. The atmosphere of Venus contains huge amounts of CO2 , which is the reason that Venus is hotter than Mercury even though it is farther from the Sun. But it is possible to have too much of a good thing. Too much CO2 can cause the Earth to become too warm for the life-forms that are now living on it. This is a major reason that scientists view the increasing concentration of GHG in Earth’s atmosphere with some alarm. Atmospheric carbon dioxide levels are increasing.  The longest-running measurement of atmospheric CO2 began in 1958 at the U.S. National Oceanic and Atmospheric Administration (NOAA) observatory near the top of Mauna Loa. The top of a volcanic

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mountain in the middle of the Pacific Ocean is the ideal place to take samples of the atmosphere. The prevailing winds come eastward across the Pacific, over thousands of miles of largely uninhabited water, bringing air that is as close as you can get to an average sample of the global atmosphere. In 1958, the late atmospheric scientist Charles Keeling of the Scripps Institute of Oceanography began measuring CO2 concentration in those atmospheric samples. The measurements continue today, a half-century later (see figure). Three facts became obvious to Keeling after the first few years of measurement, and they have been confirmed every year since the measurements began. First, atmospheric CO2 levels are increasing. The atmosphere contains only about 380 ppm of CO2 . But each year, the concentration has increased by a little more than 1 ppm. This does not sound like much, but when Keeling began collecting data, the atmosphere contained only about 316 ppm of CO2 . Scientists estimate that before the Industrial Revolution, it contained only 280 ppm. Carbon dioxide levels have increased 20 percent just since the measurements began and 36 percent since before widespread industrialization. Therefore atmospheric CO2 levels have been rapidly increasing for the past halfcentury and probably for the past two centuries. At current rates, the atmosphere will have 500 ppm of CO2 by 2050 and 750 ppm by 2100.

Second, atmospheric CO2 levels fluctuate by about 5 ppm each year, increasing in the Northern Hemisphere winter, decreasing in the Northern Hemisphere summer. This is overwhelmingly the effect of land plants in the Northern Hemisphere, such as those in forests and grasslands. Plants remove carbon dioxide from the air through the process of photosynthesis. Some aquatic microbes do this also, but land plants show a strong seasonal pattern: a lot of photosynthesis during the summer and much less during the winter. Aquatic microbes and tropical forests remove carbon dioxide more or less uniformly all year, unlike temperate forests. It is the Northern Hemisphere summer that is important in the annual decline in carbon dioxide, because the Southern Hemisphere is mostly water. Five ppm, therefore, represents the approximate amount of carbon dioxide that temperate land plants can remove from the global atmosphere in a growing season. Third, CO2 is accumulating faster and faster. The curve is becoming steeper. When Keeling began his measures, about 1 ppm of CO2 accumulation occurred each year; now, it is closer to 2 ppm. Both CO2 and temperature have been increasing during the past half-century. This strongly implicates CO2 as a major cause of global warming. But to demonstrate that the parallel changes are no mere coincidence, it is necessary to look farther back into the past. In order to estimate global temperatures of the past, scientists have had to use proxy methods. One of these methods is oxygen isotopes in the layers of ice from Greenland and Antarctica, as explained in the previous section. But for atmospheric CO2 , it is possible to make direct measurements instead of relying on proxies. Within each layer of ice, bubbles of air have been trapped, many visible to the unaided eye. The atmospheric gas contained in a layer of ice can be released in a confined laboratory container, and its CO2 concentration can be measured. Therefore, scientists can make a temperature estimate and a CO2 measurement for each layer of ice for the past several hundred thousand years. The graphs of global temSince measurements began in the late 1950s, global atmospheric carbon perature and CO2 line up almost dioxide has steadily increased by almost 30 percent. Each summer, phoexactly (refer back to earlier figure tosynthesis in the Northern Hemisphere removes about 5 ppm of carbon on page 284). Whenever the air dioxide from the atmosphere. The slope has also increased; changes in atmospheric carbon dioxide are more rapid now than they were in 1960. had a lot of CO2 in it, the tem-

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greenhouse effect  289 perature was greater than at times when there was less CO2 in the atmosphere. This is a striking and convincing proof of the correlation of carbon dioxide with global warming. Correlation, however, is not the same as causation. Not only could an increase in CO2 cause global warming, but global warming could cause an increase in CO2 . Warmer temperatures stimulate decomposition by bacteria and fungi in the soils of the world; decomposition releases CO2 into the air. Increases in CO2 and global warming therefore cause each other. This accounts for the correlation. In the past, ice ages came and went, largely because processes such as the rotation and revolution of the Earth initiated cycles of warming and cooling. A warming trend would stimulate the release of CO2 , which would accentuate the warming trend. Before civilization, global temperatures appear to have increased prior to the increase in CO2 . Today, however, it is the other way around. Atmospheric CO2 has increased to its highest level in almost a half million years, and global temperatures have yet to catch up. For this reason, even if humans stopped putting CO2 into the atmosphere right now, global warming would still occur. The difference between what happened before civilization, in which global warming caused increases in CO2 , and what is happening today, in which CO2 is causing global warming, is that billions of humans are producing vast amounts of CO2 . Increased carbon dioxide levels are largely responsible for global warming. CO2 is not the only factor that may contribute to global warming. As mentioned previously, natural climatic variability can be caused by the movement of the Earth and changes in the intensity of sunlight. The advance and retreat of glaciers across North America and Europe appear to be caused by changes in the movements of the Earth relative to the Sun, which produce an approximately 100,000-year cycle of cold (glaciation) and warm (interglacial) periods. However, the changes in solar intensity are very small. By themselves, they seem unable to explain the ice ages. Apparently these variations in solar intensity have stimulated a series of processes that, working together, have produced ice ages during the past 2 million years. Although the ice ages have followed the pattern imposed by cycles of solar illumination, recent global warming cannot be attributed to it. Other human activities may counteract global warming but at a cost. The destruction of forests, and their replacement by barren land reflect more sunlight back into outer space but also reduce photosynthesis. Particulate air pollution (such as smoke and sulfur dioxide) reflects sunlight back into outer

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space but creates environmental and health problems. In fact, the reduction of particulate air pollution in recent decades, allowing more sunlight to reach the surface of the Earth, may be the reason that global temperatures have risen sharply in recent decades, even though CO2 has been steadily accumulating for a century and a half. None of these other processes has anywhere near the effect that carbon dioxide has had on recent global warming. Human activities have increased the amount of energy at the Earth’s surface by 1.9 watts per square yard (1.6 watts per square meter). This is the equivalent of having an additional heat load of 200 30-watt lightbulbs burning continuously on each acre of the Earth’s land and ocean surface. This is approximately equal to the amount of heating that is attributable to the buildup of CO2 in the air. Carbon dioxide and other GHG have also been a major influence in the Earth’s long-term history, during the past 2 million years, during the climate change that occurred about 30 million years ago, and during the sudden warming that occurred about 55 million years ago. At only one time, about 300 million years ago, has a period of ice ages given way to a prolonged warm period, and this event was apparently caused by an increase in atmospheric carbon dioxide.

What Is Causing the Increase in Carbon Dioxide? Although in previous millennia the changes in temperature and CO2 were related to the ice ages, the present-day increase in CO2 is undoubtedly the result of human activities. The main sources of CO2 emissions are from transportation and manufacturing. The burning of fuels such as coal, oil, and natural gas for transportation and industry releases huge amounts of CO2 into the air. Since the beginning of the Industrial Revolution, humans have burned more and more of these fossil fuels (socalled because they were formed millions of years ago primarily from dead plants and microbes) each year. Of these three fuels, coal (often used in power plants and factories) emits the most CO2 per unit of energy produced, because it already contains so much carbon. Oil, including oil refined into gasoline, also produces a lot of CO2 from the tailpipes of the billion cars and trucks in the world. Another large source of carbon emissions is the burning of firewood. Firewood produces about 30 percent of the CO2 that enters the atmosphere. This is the principal or only source of energy for billions of poor people. Another reason for the prodigious increase in carbon emissions is that humans are destroying plants. The destruction of forests and other plant

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290 greenhouse effect  290 habitats puts CO2 into the air in two major ways. First, when the trees are burned or decompose, they release CO2 into the air. Second, dead plants can no longer carry out the photosynthetic process that removes CO2 from the air. In many instances, the natural habitats do not recover. In such cases, the loss of plant cover represents a permanent release of carbon dioxide and reduction in the ability of plants to cleanse the air of excess CO2 . Humans are not only destroying plants, but causing CO2 to be released from dead plant materials. Conversion of forests to agricultural lands causes the soil to become warmer, which enhances the decomposition of humus—while at the same time reducing the amount of new humus that is created. About 2 billion tons (metric tons) of carbon have entered the air as a result of draining and burning peatlands in Indonesia for oil palm plantations. (This also caused fruit bats to roost outside of the forest, in closer contact with humans. Their feces contain viruses that could infect people.) The sheer volume of these processes—all of them caused by humans—accounts for almost all of the increase in atmospheric CO2 . It is ludicrous to assert that scientists cannot know why its level is rising. One U.S. Republican congressman, Dana Rohrabacher of California, speculated in 2007 that a global warming event 55 million years ago was caused by unknown and unknowable processes—his guess was that it might have been dinosaur flatulence. This suggestion is as irrelevant as it is ridiculous. Even if the causes of global warming in the past were not fairly well understood, the cause today is not in doubt. Nearly all scientists agree that human activities are the main cause of the global warming that is now occurring. The agreement of scientists is perhaps best indicated by the strong conclusions issued by the IPCC. In February 2007, the IPCC stated that global warming from carbon dioxide was a certainty and that the human contribution to this warming was 90 percent certain. In April 2007, the panel released a second report that predicted droughts in some areas, flooding in others, and the spread of disease and insect pests as consequences of global warming. In May 2007, it released a third report that proposed possible solutions. In November 2007, it produced a synthesis report that summarized all of the organization’s conclusions. When this international panel of scientists issues a consensus statement, it is as close to a scientific fact as we can get about climate change. The panel’s statements are reviewed by representatives of many governments and therefore represent something as close to world consensus as can be reasonably expected. The IPCC is now assembling data for their 2013 report.

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first entry Atmospheric CO2 levels have been much higher in the distant past than they are now. And global warming is nothing new on this planet. Before 25 million years ago, Antarctica was fully forested. Then CO2 fell below 500 ppm and ice sheets began to expand in Antarctica. No competent scientist claims that global warming or the accumulation of atmospheric CO2 will prove directly lethal to life on this planet. In fact, the Earth was greener when there was more carbon dioxide in the air millions of years ago. But the consequences of global warming, as outlined above, may be disastrous to the habitats and ecological relationships of plants and animals, as well as to the human economy and to global politics. Never before has the Earth had to support 7 billion humans. The entire system of agriculture and commerce is based on the assumption that global climate patterns and ocean levels will remain as they are except for occasional droughts or storms. This comfortable belief will almost certainly be shaken. It will not be necessary for global warming to make humans fall over dead in order to wreak havoc on global civilization. Human activity is pushing temperatures and CO2 levels outside of the range that they have occupied for the past 2 million to 3 million years, at which time continents and global ocean circulation assumed their present patterns. There is thus no comparable situation in the past to which scientists can look that will allow them to predict what will happen next. The economic consequences, from higher sea levels, from storms, from disease, and from agricultural losses, are unpredictable and will probably be massive.

Can the Greenhouse Effect Be Controlled? For the future security of the human and natural world, it is essential that the greenhouse effect be brought under control. Some scientists have made wildly speculative proposals to do this by reflecting sunlight back into outer space by launching giant mirrors into orbit or by spewing massive amounts of sulfate particles into the upper atmosphere. Most scientists are convinced that the greenhouse effect can be reduced only by managing the amount of GHG in the atmosphere. The two general ways to do this are to release fewer GHG into the atmosphere and to remove them from the atmosphere. Some scientists have proposed to reduce carbon emissions through “carbon sequestration,” or chemical removal of carbon dioxide from effluent gases before they enter the air, for example by removing CO2 from the smokestacks of power plants. The technology to do this on any meaningful scale is currently experimental and expensive. A few other scientists have championed the chemical removal of carbon dioxide from the air. This method would be even

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greenhouse effect  291 more uncertain and expensive. Thus most scientists say that humans should produce less CO2 in the first place and remove it from the air by enhancing natural processes such as plant photosynthesis. Photosynthesis is not the only natural process that removes CO2 from the air. Over a very long period of time, the weathering of some kinds of rocks removes CO2 from the air. Carbon dioxide reacts with silicates in the Earth’s crust, forming carbonates (limestone) that are washed away and accumulate as sediments on the ocean floor. The cycle is completed when continental drift thrusts the sediments into the crust and the carbon is released as CO2 from volcanoes. This process acts as a regulatory mechanism, because a greater abundance of atmospheric CO2 produces a warmer climate that stimulates the reaction between CO2 and silicate. This process cycles a much greater amount of carbon through the Earth than does photosynthesis. However, it requires millions of years and cannot rescue the Earth from an excessive greenhouse effect on any timescale meaningful to humans. Photosynthesis is the only natural process that can quickly remove CO2 from the air. If humans promote the growth of plants, they may not only stimulate photosynthesis but even the formation of limestone: Plants speed up the process of silicate weathering by acidifying the soil with their leaf litter. At least one “think tank” of American antienvironmentalists, the Competitive Enterprise Institute, has claimed that photosynthesis is the reason that humans do not have to worry about global warming. Humans can pour all the carbon dioxide they want into the air, and plants will clean up the mess. Their advertisements asserted: “Carbon dioxide—we call it life!” Unfortunately, this argument is lethally simplistic. Perhaps the most obvious fact that contradicts this hypothesis is that plants are not, right now, absorbing the excess CO2 in the atmosphere. Also, at the very time that they are most needed, humans are destroying plants. Furthermore, plants carry out photosynthesis only if they have enough nutrients and water. If large continental areas experience droughts, the trees will not remove very much carbon from the air. Researchers at Duke University performed a free-air carbon enhancement (FACE) study in a forested area of North Carolina. In FACE studies, the air is enriched in CO2 , but the plants are not enclosed by any kind of barrier. The researchers increased the CO2 in forest plots by 50 percent over the course of an entire decade. They announced in the summer of 2007 that the extra CO2 had aided tree growth only in those areas that had plenty of water and good soil. Other studies have found that global warming might enhance soil and plant respiration, which releases carbon dioxide, even more

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than it stimulates photosynthesis, which removes it. Finally, there are just not enough plants in the world to counteract all of the carbon that human activities are putting into the air. The world not only needs more plant cover but plants that remove carbon from the air permanently. As stated earlier, each northern summer, plants remove about 5 ppm of carbon dioxide from the air. Most of this is returned, however, through decomposition of leaf litter. This is particularly true of short-lived plants such as crops. Researchers at the University of Illinois used FACE experiments to enhance the growth of soybeans and observed only modest increases, far less than the increases that had been predicted from laboratory experiments. Other recent experiments have shown that extra CO2 in the air may boost the growth of forests, but that these results may be transient—forests do not continue to show year after year of additional growth in the presence of elevated carbon dioxide. If, in contrast, forests are allowed to store carbon in the form of wood, the carbon has been removed from the air for the life of the tree. The trees that remove the most carbon from the air during their lives are also the ones that grow slowly. A huge California redwood may remove 30 tons (about 30 metric tons) of carbon from the air—but may require two millennia to do so. Preserving forests and planting more trees is a necessary but not entirely sufficient part of removing excess CO2 from the atmosphere. Another way in which plants may be able to remove carbon dioxide from the atmosphere for a long period is by the growth of roots. When dead roots decompose, much of the carbon goes into humus rather than directly into the atmosphere. Increased plant growth will store more carbon in the soil. Humus in soils all around the world contains a massive amount of carbon. The cold, soggy soils of Siberia alone may hold 70 billion tons of carbon. However, global warming is causing soils everywhere to release CO2 , which will enhance global warming still further. No matter how many forests and grasslands humans may plant, they will not remove all of the additional carbon that is entering the atmosphere. Plant ecologist Christopher Field and colleagues estimated that the Earth’s natural ecosystems produce 117 billion tons of biomass per year. This biomass either consists of carbohydrates or is derived from carbohydrates, which are produced by photosynthesis. Most of the mass of these carbohydrates comes from CO2 . The burning of fossil fuels produces about 7 billion tons of carbon, which corresponds to about 25 billion tons of carbon dioxide, each year. (Carbon dioxide consists of one carbon and two oxygen atoms; mass of CO2 is 3.7 times the mass of ­carbon.)

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292 greenhouse effect  292

first entry

If plants and aquatic microbes were to absorb the entire 25 billion tons, it would be necessary to increase the growth of plants worldwide by about 21 percent relative to the plant cover that existed before civilization. While this will probably never happen while the human economy is as large as it now is, a 21 percent increase in forest cover is not impossible. Not all plant cover would be equally helpful in reducing the greenhouse effect. Boreal forests (of the far north) absorb much more sunlight than does snow cover. This causes the trees to become warm and release heat into the surrounding air, which would not happen with sun shining on snow. One scientist pointed out that an expansion of boreal forests at the expense of tundra, which is covered by snow except for a couple of months each year, would therefore result in a net warming of the planet. This point is true but may be moot, because with global warming, the snow cover of the tundra will be severely reduced anyway, and scientists predict that the boreal forest will move northward whether trees are planted or not. Moreover, it will do no good to plant trees under conditions in which they cannot survive. Millions of trees have been planted in arid, dusty regions of China, but many of these have died. The restoration of grasslands would have been a more effective way of stabilizing the soil and of removing carbon from the air. Grasses have massive root systems and are particularly good at putting carbon into the soil. The oceans also absorb CO2 . Many aquatic microbes carry out photosynthesis just as land plants do. Many small aquatic organisms, and some

Comparisons of the Ecological Footprints (Per Person) of   Selected Countries* Country

Hectares**

United States

10

Canada

8

United Kingdom

6

Japan

4

Germany

2

China

2

World

2

India

1

Kenya

1

*Rounded to the nearest hectare. From Global Footprint Network **1 hectare = 2.5 acres

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that are not so small, produce shells of calcium carbonate. When these organisms die, their shells, and the carbon they contain, settle to the bottom of the sea, forming organic limestone. In addition, ocean water itself absorbs CO2 , producing carbonic acid. Currently, by these processes, the oceans remove about 2 billion tons of carbon from the atmosphere—about one-fourth of what is added to the atmosphere—each year. However, absorption of carbon by the oceans may not continue indefinitely at its current rate. Carbonic acid in the oceans may reduce the growth of the organisms that now make organic limestone, and warmer oceans will absorb less carbon dioxide. Arctic Ocean waters near Canada were measurably depleted of calcium carbonate in 2008. Natural processes (photosynthesis on land and in oceans, absorption by ocean water, reaction with silicates) cannot compensate for the amount of CO2 humans are adding to the atmosphere. This simple conclusion is obvious when we consider that they are not now doing so; atmospheric CO2 increases measurably every year. About 45 percent of the CO2 added to the atmosphere stays there. Because about half of the CO2 that humans put into the atmosphere stays there during any given year, there is no way around imposing limits on carbon emissions and increasing the efficiency of energy use in power plants and vehicles. Timed to coincide with the start of the United Nations Climate Summit in Copenhagen on December 7, 2009, the Environmental Protection Agency announced that it would regulate CO2 as a substance that is dangerous to human health. On that same day, congressional Republicans issued a statement criticizing President Barack Obama for generating carbon emissions (which, they claimed, were not responsible for global warming anyway) by flying in Air Force One to Oslo to accept the Nobel Peace Prize. Caps on carbon emissions appear to be both necessary and impossible in the United States, to which the rest of the world is looking for leadership. Each person leaves an “ecological footprint” on the world. This refers to the acreage of productive land and water (such as forests and agricultural fields) that would be required to remove the carbon dioxide from the air that a person is responsible for releasing and to provide the raw materials for that person’s activities on a continuing basis. This includes the absorption of the CO2 not only from what each person directly releases, such as from an automobile tailpipe, but the CO2 released by power plants and factories that provide the person with what he or she consumes. The average American has an ecological footprint of about 23 acres (10 hect-

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greenhouse effect  293 ares), almost five times the world average, and much higher than other industrialized nations (see table). A “carbon footprint” is the amount of CO2 that a person directly or indirectly releases into the air. The average citizen of India has an ecological footprint more than 10 times smaller than that of an average American and produces almost 30 times less CO2 . If all 7 billion people in the world had the ecological footprint of an American, four worlds of plant growth would be required to compensate for it. The United States is the leading producer of carbon emissions on a per capita basis (see table at bottom of page). Even though planting trees cannot, by itself, save the world from an excessive greenhouse effect, it is hardly possible to succeed without saving the trees that now exist and by planting more. Green plants are essential allies in the effort to prevent a disastrous greenhouse future. Furthermore, tree plantations remove much less carbon from the air than wild forests. Therefore the preservation of biodiversity depends on preventing global warming—

but preventing global warming also depends on the preservation of biodiversity. See also greenhouse effect and biodiversity; ice ages. Further Reading Alley, Richard B. “Abrupt climate change.” Scientific American, November 2004, 62–69. Barnett, Tim P., et al. “Human-induced changes in the hydrology of the western United States.” Science 319 (2008): 1,080–1,083. ———, et al. “Penetration of human-induced warming into the world’s oceans.” Science 309 (2005): 284–287. Bender, Morris A., et al. “Modeled impact of anthropogenic warming on the frequency of intense Atlantic hurricanes.” Science 327 (2010): 454–458. Summarized by Kerr, Richard A. “Models foresee more-intense hurricanes in the greenhouse.” Science 327 (2010): 399. Brumfiel, Geoff. “Academy affirms hockey-stick graph.” Nature 441 (2006): 1,032–1,033.

Comparisons of Carbon Emissions from the Burning of   Fossil Fuels in Countries and Regions of the World* Region and Selected Countries North America United States Canada

Contribution to World Carbon Emissions

Metric Tons of Carbon Dioxide Produced per Person**

25.5%

16.0

21.8%

20.2

2.2%

18.1

Europe

17.2%

8.0

Eurasia

9.4%

8.9

Russia East and Southeast Asia

6.2% 35.5%

11.7 2.7

Japan

4.7%

9.9

China

17.4%

3.9

India

4.1%

1.0

Australia

1.4%

19.4

Central and South America

3.8%

2.4

Middle East

4.9%

7.2

Africa

3.6%

1.1

World

4.2

*2004 data from Energy Information Administration **1 metric ton = 1.1 English tons

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294 greenhouse effect  294 Chen, J. L., et al. “Satellite gravity measurements confirm accelerated melting of Greenland ice sheet.” Science 313 (2006): 1,958–1,960. Collins, William, et al. “The physical science behind climate change.” Scientific American, August 2007, 64–73. Energy Information Administration. “Environment: Energy-related emissions data and environmental analyses.” Available online. URL: http://www.eia.doe. gov/environment.html. Accessed August 1, 2010. Field, Christopher B., et al. “Primary production of the biosphere: Integrating terrestrial and oceanic components.” Science 281 (1998): 237–240. Froese, Duane G., et al. “Ancient permafrost and a future, warmer arctic.” Science 321 (2008): 1,648. Fu, Qiang, et al. “Enhanced mid-latitude tropospheric warming in satellite measurements.” Science 312 (2006): 1,179. Global Footprint Network. “National footprints.” Available online. URL: http://www.footprintnetwork.org/ gfn_sub.php?content=national_footprints. Accessed August 1, 2010. This Web site compares the ecological footprints of all nations. Goswami, B. N., et al. “Increasing trend of extreme rain events over India in a warming environment.” Science 314 (2006): 1,442–1,445. Heath, James, et al. “Rising atmospheric CO2 reduces sequestration of root-derived soil carbon.” Science 309 (2005): 1,711–1,713. Heimann, Martin. “How stable is the methane cycle?” Science 327 (2010): 1,211–1,212. Howat, Ian M., et al. “Rapid changes in ice discharge from Greenland outlet glaciers.” Science 315 (2007): 1,559–1,561. Kerr, Richard A. “Record U.S. warmth of 2006 was part natural, part greenhouse.” Science 317 (2007): 182–183. King, Anthony W. “Plant respiration in a warmer world.” Science 312 (2006): 536–537. Körner, Christian, et al. “Carbon flux and growth in mature deciduous forest trees exposed to elevated CO2.” Science 309 (2005): 1,360–1,362. Kunzig, Robert. “Drying of the West.” National Geographic, (February 2008): 90–113. Long, Stephen P., et al. “Food for thought: Lower-thanexpected crop yield stimulation with rising CO2 concentrations.” Science 312 (2006): 1,918–1,921. Luo, Yiqi. “Terrestrial carbon cycle feedback to climate warming.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 683–712. Luthcke, S. B., et al. “Recent Greenland ice mass loss by drainage system from satellite gravity observations.” Science 314 (2006): 1,286–1,289. Mann, Michael E., et al. “Global-scale temperature patterns and climate forcing over the past six centuries.” Nature 392 (1998): 779–787.

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first entry ———. “Global signatures and dynamical origins of the Little Ice Age and the Medieval Climate Anomaly.” Science 326 (2009): 1,256–1,260. Meehl, Gerald A., et al. “Amplifying the Pacific climate system response to a small 11-year solar cycle forcing.” Science 325 (2009): 1,114–1,118. Meier, Mark F., et al. “Glaciers dominate eustatic sealevel rise in the 21st century.” Science 317 (2007): 1,064–1,067. Mishchenko, Michael I., et al. “Long-term satellite record reveals likely recent aerosol trend.” Science 315 (2007): 1,543. National Academies, Committee on Stabilization Targets for Atmospheric Greenhouse Gas Concentrations. “Climate Stabilization Targets: Emissions, Concentrations, and Impacts over Decades to Millennia.” Released July 16, 2010. Available online. URL: http:// www.nationalacademies.org/includes/Stabilization TargetsFinal.pdf. Accessed July 16, 2010. National Oceanic and Atmospheric Administration. “NOAA: 2010 tied for warmest year on record.” Available online. URL: http://www.noaanews.noaa. gov/stories2011/20110112_globalstats.html. Accessed August 8, 2011. ———. “A Paleo Perspective on Global Warming: The Instrumental Data of Past Global Temperatures.” Available online. URL: http://www.ncdc.noaa.gov/ paleo/globalwarming/instrumental.html. Accessed August 1, 2010. ———. “A Paleo Perspective on Global Warming: Paleoclimatic Data for the Last 2000 Years.” Available online. URL: http://www.ncdc.noaa.gov/paleo/globalwarm ing/paleolast.html. Accessed August 1, 2010. ———. “Trends in carbon dioxide.” Available online. URL: http://www.esrl.noaa.gov/gmd/ccgg/trends/co2_data_ mlo.html. Accessed August 1, 2010. Oreskes, Naomi. “The scientific consensus on climate change.” Science 306 (2004): 1,686. ———, and Erik M. Conway. Merchants of Doubt: How a Handful of Scientists Obscured the Truth on Issues from Tobacco Smoke to Global Warming. New York: Bloomsbury, 2010. Osborn, Timothy J., and Keith R. Briffa. “The spatial extent of 20th-century warmth in the context of the past 1200 years.” Science 311 (2006): 841–844. Overpeck, Jonathan T., et al. “Paleoclimatic evidence for future ice-sheet instability and rapid sea-level rise.” Science 311 (2006): 1,747–1,750. Pagani, Mark, et al. “An ancient carbon mystery.” Science 314 (2006): 1,556–1,557. ———. “Marked decline in atmospheric carbon dioxide concentrations during the Paleogene.” Science 309 (2005): 600–603. Pearce, Fred. With Speed and Violence: Why Scientists Fear Tipping Points in Climate Change. Boston: Beacon, 2007.

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greenhouse effect and biodiversity  295 Petit, J. R., et al. “Climate and atmospheric history of the past 420,000 years from the Vostok ice core, Antarctica.” Nature 399 (1999): 429–436. Rahmstorf, Stefan, et al. “Recent climate observations compared to projections.” Science 316 (2007): 709. RealClimate. “RealClimate: Climate science from climate scientists.” Available online. URL: http://www.realcli mate.org. Accessed August 8, 2011. Retallack, Gregory J. “A 300-million-year record of atmospheric carbon dioxide from fossil cuticles.” Nature 411 (2001): 287–290. Seager, Richard, et al. “Model projections of an imminent transition to a more arid climate in southwestern North America.” Science 316 (2007): 1,181–1,184. Shakhova, Natalia, et al. “Extensive methane venting to the atmosphere from sediments of the East Siberian Arctic Shelf.” Science 327 (2010): 1,246–1,250. Shepherd, Andrew, and Duncan Wingham. “Recent sealevel contributions of the Antarctic and Greenland ice sheets.” Science 315 (2007): 1,529–1,532. Siegenthaler, Urs, et al. “Stable carbon cycle-climate relationship during the late Pleistocene.” Science 310 (2005): 1,313–1,317. Solomon, Susan, and the Intergovernmental Panel on Climate Change. “Climate Change 2007: The Physical Science Basis.” Available online. URL: http://www. ipcc.ch/publications_and_data/ar4/wg1/en/contents. html. Accessed August 8, 2011. ———, et al. “Contributions of stratospheric water vapor to decadal changes in the rate of global warming.” Science 327 (2010): 1,219–1,223. Spahni, Renato, et al. “Atmospheric methane and nitrous oxide of the late Pleistocene from Antarctic ice cores.” Science 310 (2005): 1,317–1,321. Sutton, Rowan T., and Daniel L. R. Hodson. “Atlantic Ocean forcing of North American and European summer climate.” Science 309 (2005): 115–118. Trenberth, Kevin E. “Warmer oceans, stronger storms.” Scientific American, July 2007, 44–47. Tripati, Aradhna K., et al. “Coupling of CO2 and ice sheet stability over major climate transitions of the last 20 million years.” Science 326 (2009): 1,394–1,397. Velicogna, Isabella, and John Wahr. “Measurements of time-variable gravity show mass loss in Antarctica.” Science 311 (2006): 1,754–1,756. Walter, Katey M., et al. “Methane bubbling from Siberian thaw lakes as a positive feedback to climate warming.” Nature 443 (2006): 71–75. Weart, Spencer R. The Discovery of Global Warming. Cambridge, Mass.: Harvard University Press, 2003. Webster, P. J., et al. “Changes in tropical cyclone number, duration, and intensity in a warming environment.” Science 309 (2005): 1,844–1,846. Summarized by Richard A. Kerr, “Is Katrina a harbinger of still more powerful hurricanes?” Science 309 (2005): 1,807.

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Westerling, A. L., et al. “Warming and earlier spring increase western U.S. forest wildfire activity.” Science 313 (2006): 940–943. Summary by Running, Steven W. “Is global warming causing more, larger wildfires?” Science 313 (2006): 927–928. Yamamoto-Kawai, Michiyo, et al. “Aragonite undersaturation in the Arctic Ocean: Effects of ocean acidification and sea ice melt.” Science 326 (2009): 1,098–1,100.

greenhouse effect and biodiversity  The climate of the Earth is becoming warmer. Global warming will have major impacts on natural ecosystems and the species of organisms that inhabit them. Global warming is nothing new in the history of the Earth; in fact it happened once before during the recent history of the modern human species, Homo sapiens. As skeptics of global warming tirelessly point out, the Earth was warmer millions of years ago, such as the middle of the Paleozoic era and of the Mesozoic era. At those times, life flourished on the Earth. Wetland forests were extensive enough during the Paleozoic era that their remains form today’s coal deposits, and the Earth had enough plant growth to support large populations of massive dinosaurs during the Mesozoic era. Clearly, a warmer Earth, per se, is not incompatible with ecosystem productivity and species diversity. A period of global warming also occurred at the end of the most recent ice age, during which Stone Age humans lived nearly everywhere on the Earth. There are two main reasons that global warming is a bigger threat to biodiversity than it was in the past: ●●

●●

The rate of temperature increase. Climatic shifts in the past were generally much slower than the shifts occurring today. Despite temporary (and catastrophic) changes such as the Younger Dryas (a sudden reversal of the warming trend), the global warming that occurred at the end of the most recent ice age was 10 times slower than the global warming that is occurring today. The ability of organisms to disperse. In the Holocene, the northern continents were largely free of obstructions to the migration of animals and the dispersal of plants. Today, cities and farms and roads block their migration. Species that live on the shore may be trapped there as sea levels rise, and animals and the seeds of plants will find few suitable places to live while they migrate northward. Humans, who did not have national boundaries or own property, were also free to migrate.

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296 greenhouse effect and biodiversity  296 For these two reasons, global warming (and associated changes such as droughts and wildfires in continental areas) presents a major threat to biodiversity.

Global Warming and Plants Global warming is already having measurable effects on plants. Plant species are growing closer to the poles and farther up on mountains as a result of global warming. Antarctica has only two native species of higher plants, one of which is the grass Deschampsia antarctica. It used to form only widely spaced tussocks in protected crevices along the coast, but Antarctica now has its first grass meadows. A major indicator of global warming is that buds of deciduous trees in the northern continents are opening sooner now than even a few decades ago— spring is coming earlier. A few isolated instances stand out. Perhaps the most famous example and most noticed by the United States federal government in Washington, D.C. was when the cherry trees bloomed along the Potomac in January 2007, far sooner than their usual budburst time. But scientists do not rely on isolated examples. Botanist A. J. Miller-Rushing and associates compared pressed plant specimens and photographs from the 19th and early 20th centuries with recent specimens and photographs. Their analysis shows that trees are leafing earlier and herbaceous plants emerging earlier in the very same locations—about 11 days earlier per century. Miller-Rushing and colleagues used 285 photographs and numerous preserved specimens. This pattern is confirmed by satellite imagery, which indicates that deciduous forests are becoming green earlier in the spring than in previous decades. Another study, published by climatologist Xiaoyang Zhang and associates, shows that lilacs planted all over North America have been flowering earlier in the spring. Interestingly, some of the southern lilacs have been blooming later rather than earlier, because in those southern locations the winters have not been cold enough to allow the biochemical breakdown of budburst inhibitors. In addition to changing the seasonal patterns of plant growth, global warming is also causing changes in where the plants live. Ecologist Camille Parmesan has reported the results of a survey of 1,700 plant species. On average, these plant species migrated northward about four miles (almost 6 km) per decade and migrated higher up in the mountains by about 24 feet (about 8 m) per decade. She also found that, on average, spring budburst occurred about two days earlier per decade. Daniel W. ­McKenney of the Canadian Forest Service and

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first entry associates studied 130 tree species. They have estimated that most of the trees will experience severe reductions in geographical range even if they manage to migrate hundreds of miles northward. In Britain, 385 species of plants flowered an average of four and a half days earlier over the course of a decade. In Spain, high-altitude grasslands are being replaced by lower-altitude shrublands. One reason that these shifts in range and seasonality are important is that they may result in extinctions. The plants that already live at the tops of mountains, such as in the alpine tundra of the Rocky Mountains and Sierra Nevada and in the cloud forests of Central America, have no place to go if conditions become warmer or drier. The alpine tundra, which consists of small grasses, sedges, and wildflowers, survives only because conditions are too cold for trees to grow over them and shade them. Once the subalpine spruce and pine forests begin to grow to the very tops of the mountains, the tundra plants and animals will face extinction. The cloud forests of Central America persist because they are inside of clouds and receive abundant water from mists. Warmer temperatures are already causing the cloud levels to rise, leaving the cloud forests high and dry. One of the richest biodiversity hot spots is the Cape region of South Africa, which is at the southern tip of the African continent. The endemic plants of this area have no place to go when temperature and moisture conditions change. Emerging from dormancy earlier in the spring may even cause direct harm to plants. This could occur if an extended warm period in the winter awakened buds or animals, which may then be killed by the return of winter. Buds of post oak trees (Quercus stellata) in Oklahoma open on warm days in winter and then die when cold weather returns. Later, when temperatures become and remain warmer, another set of buds open in place of the damaged buds. As global warming progresses, such events will become more common. Whether this loss of some of the buds may have long-term effects on the growth of the oaks is not known. Coniferous forest trees in the western United States—even in forests that appear to be otherwise healthy—are currently experiencing a higher death rate than they were four decades ago. According to forest scientist Phillip van Mantgem and associates, death rate of trees per year has increased from 0.3 percent to 1.3 percent in the Pacific Northwest, from 1.0 percent to 1.7 percent in the mountains of California, and from 0.2 percent to 0.6 percent in the interior forests. This pattern held true at all 76 locations and at all sizes, elevations, species, and ages of trees. The researchers attribute the increased death to higher temperatures and less precipitation, both

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greenhouse effect and biodiversity  297 of which are associated with global warming that has occurred during that period.

Global Warming and Terrestrial Animals Animals are also responding to climatic changes. Armadillos have been expanding from their native habitats in the South, as far north as Illinois. Several bird species have moved their breeding ranges northward. Over the course of 20 years, British birds have shifted their ranges about 12 miles (15 km) northward, and British birds are laying their eggs sooner. Camille Parmesan studied not only plants but also nonmigratory European butterflies, most of which shifted their range northward between 22 to 148 miles (28 to 185 km) during the 20th century. Over the course of 100 years, mammals that live at lower elevations in mountains have moved to higher elevations, and the mammals that live at high elevations have experienced range restrictions. Global warming has caused changes in migration patterns of some birds. The European blackcap breeds in Germany and has traditionally migrated to Spain and Portugal to overwinter. Recently, some flocks of blackcaps have spent the winter in England instead. The flocks return from England earlier than the flocks from Portugal, with the result that the England-wintering birds mate earlier and leave more offspring. Scientists estimate that climate-induced changes in the migration patterns of this species will result in evolutionary changes in their migration instinct. Animal species are already facing extinction from the climatic changes in their habitat. The golden toad has already become extinct at least in part because of the drier conditions in the cloud forests. This is only the beginning. Ornithologist Çag˘an S¸ekerciog˘lu and associates have predicted the extinction of between 100 and 500 bird species for each 1°F increase in global temperature.

Global Warming and Marine Organisms As the oceans become warmer, the extinction of some marine creatures appears to be inevitable. In particular, warmer waters and higher salt concentrations have already caused many coral reefs to experience bleaching. When the corals die, the entire food chain collapses and is replaced by one that is based upon algae. Living corals prevent algae from growing on the reefs, but the algae grow abundantly on dead coral structures. The result is a striking decrease in the diversity of species at all levels of the food chain. Scientists have also given much attention to the effects of ocean acidification. Oceans absorb CO2 , too slowly to prevent CO2 buildup in the atmosphere, but quickly enough to have already caused a measurable increase in the acidity of the water.

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Acidic waters dissolve calcium carbonate. This contributes to the death of animals that use calcium for their structure, including corals, molluscs, and zooplankton. The death of these organisms has a feedback effect on the ocean’s ability to absorb CO2 . Fishes excrete a lot of carbonate and also make a substantial contribution to the removal of carbon from surface waters. Organisms use carbon as well as calcium to make their shells, then when they die they sink to the bottom of the sea, taking the carbon away from the surface and thus from the atmosphere. If there are fewer shelled organisms, the ocean will remove less carbon from the atmosphere. Ocean acidification has already reduced the rate of calcium deposition in reefs.

Global Warming and Ecological Interactions Global warming can also disrupt ecological relationships between species. Warmer temperatures may give insects a longer reproductive season and allow them to spread rapidly on their host plants. (This includes the insect pests of crop plants.) Warmer temperatures are already allowing outbreaks of spruce bark beetles (Dendroctonus rufipennis) and pine bark beetles (D. ponderosae) to destroy millions of spruces in Alaska and Canada, as well as Englemann spruces and lodgepole and piñon pines in the Rocky Mountains. The beetles transmit a fungus (Conartium ribicola).Warmer temperatures allow beetle populations to explode because they can complete their life cycle in one year rather than the normal two. Reduced sap production in the trees, associated with warmer, drier conditions, also encourages the survival of the beetles, since sap blocks the burrows created by the beetle larvae. D. ponderosae is spreading the same fungus among whitebark pines (Pinus albicaulis) in the subalpine forests of California. Because diseases are spreading through the boreal and subalpine forests, global warming is causing these forests to turn brown at the same time that it is causing the tundra adjacent to them to turn greener. Global warming can also have ecological effects via drought. In one example, salt marsh blue crabs (Callinectes sapidus) normally kept periwinkle snail (Littoraria irrorata) populations in check. The snails would damage the salt marsh cordgrass (Spartina alterniflora) by puncturing the grass leaf cuticle, allowing a Fusarium fungus to invade the leaves. During droughts, the cordgrass is stressed by higher concentrations of salt as well as acid and toxic chemicals in the water. But in addition, the drought reduces the crab population, allowing an outbreak of snails. Other disrupted ecological relationships result when global warming causes some organisms to

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298 greenhouse effect and biodiversity  298 become active earlier in the spring than do others. One example is the relationship between flowering plants and their insect pollinators. Most wild plant species, other than conifers, grasses, and sedges, depend on insects for pollination. If warmer temperatures change the seasonal life cycles of the plants and the pollinators in different ways, the flowers may open when the pollinators are not present. As a result, the pollinators may find no food, and the flowers will not be pollinated. Another example is the disruption of the food chain. Herbivorous animals may respond more quickly to the warming climate than do the plants that they eat, with the result that the animals may hatch and find little or nothing to eat. Or, if warmer springs cause caterpillars to hatch before the baby birds that eat them, the nestlings may not have enough to eat. Within bird populations, those individuals that could best adjust the timing of their reproduction have been more successful than those that could not alter their reproduction to adjust to the earlier arrival of spring. An experiment in a California grassland indicates that increased precipitation during the normally rainy winter would have little effect on the growth of plants or the dominant species of plants and invertebrate animals, but rainfall that extended the spring rains into summer would have a profound effect. What that effect would be is also unclear. In this experiment, there was an initial burst of growth in some plant species, followed by a decline in both plant growth and number of plant and invertebrate species in the later years of the experiment.

Global Warming and Evolution There is some evidence that global warming may have already begun to induce evolutionary changes. Researchers have observed genetic alteration within species. Genetic changes have occurred in wild populations of fruit flies similar to those that occur in hot and dry conditions. Researchers have also observed what might be the beginning of the evolution of one species into two or more as a result of global warming. In the European blackcap example mentioned above, the birds that overwinter in England mate mostly with one another rather than with the birds that overwinter in Spain and Portugal; that is, they are reproductively isolated from the birds that migrate from Spain and Portugal. This may eventually allow one bird species to diverge into two. These evolutionary changes are not necessarily bad. In fact, they should allow species to adjust to the changes associated with global warming—except that the changes are occurring too fast for evolution

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first entry to help them. They illustrate the very broad impact of global warming on the natural world.

Global Warming, Wild Species, and Humans Shifts in the geographical ranges of plants and animals and other biological changes may have direct impact on humans. Studies led by Fakhri Bazzaz suggest that global climate change may enhance the growth and the pollen production of ragweeds. Warm weather causes poison ivy to produce more irritant. And tropical mosquitoes, which spread numerous diseases such as malaria and dengue fever, may spread northward and introduce these diseases, which Americans have been privileged to ignore, to the United States. Government agencies and private landowners have set aside “nature preserves” for wild plants and animals, but as the climate becomes warmer, wild species will be trapped in preserves no longer suitable for them. Ecologists are beginning to design preserves that are connected by corridors, which will allow plants and animals to move northward from one preserve to another in response to global warming. But such designs are still far from widespread implementation and will probably prove to be too little too late for the wild species. Some ecologists are even suggesting that humans need to intervene to assist the migration of species to new locations where they can survive. These are just the effects of global warming that scientists have already begun to observe. If global warming disrupts human civilization (for example, by creating environmental refugees and by causing droughts in agricultural areas), humans may turn in desperation to even more harmful exploitation of natural resources than they already are. At the present time, Africans are eating the meat of wild apes partly because of the collapse of ocean fish populations. Will global warming cause such impacts to become more severe and widespread? See also greenhouse effect; ice ages. Further Reading Aronson, Richard B., et al. “Climate change and the invasibility of the Antarctic benthos.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 129–154. Bearhop, Stuart, et al. “Assortative mating as a mechanism for rapid evolution of a migratory divide.” Science 310 (2005): 502–504. Berteaux, D., et al. “Keeping pace with fast climate change: Can arctic life count on evolution?” Integrative and Comparative Biology 44 (2004): 140–151. Bradshaw, W. E., and C. M. Holzapfel. “Genetic shift in photoperiodic response correlated with global warm-

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greenhouse effect and biodiversity  299 ing.” Proceedings of the National Academy of Sciences USA 98 (2001): 14,509–14,511. Charmantier, Anne, et al. “Adaptive phenotypic plasticity in response to climate change in a wild bird population.” Science 320 (2008): 800–803. Colwell, Rita R. “Global climate and infectious disease: The cholera paradigm.” Science 274 (1996): 2,025–2,031. Colwell, Robert K., et al. “Global warming, elevational range shifts, and lowland biotic attrition in the wet tropics.” Science 322 (2008): 258–261. Crick, H. Q. P., et al. “UK birds are laying eggs earlier.” Nature 388 (1997): 526. De’ath, Glenn. “Declining coral calcification on the Great Barrier Reef.” Science 323 (2009): 116–119. Summarized by Pennisi, Elizabeth. “Calcification rates drop in Australian reefs.” Science 323 (2009): 27. Fitter, A. H., and R. S. R. Fitter. “Rapid changes in flowering time in British plants.” Science 296 (2002): 1,689–1,691. Grabherr, G., et al. “Climate effects on mountain plants.” Nature 369 (1994): 448. Hoegh-Guldberg, O., et al. “Assisted colonization and rapid climate change.” Science 321 (2008): 345–346. ———, et al. “Coral reefs under rapid climate change and ocean acidification.” Science 318 (2007): 1,737– 1,742. Lenoir, J., et al. “A significant upward shift in plant species optimum elevation during the 20th century.” Science 320 (2008): 1,768–1,771. Lindgren, E., and R. Gustafson. “Tick-borne encephalitis in Sweden and climate change.” Lancet 358 (2001): 16–18. Lovejoy, Thomas, and L. Hannah, eds. Climate Change and Biodiversity. New Haven, Conn.: Yale University Press, 2005. Lyon, Bruce E., et al. “A matter of timing.” Science 321 (2008): 1,051–1,052. McKenney, Daniel W., et al. “Potential impacts of climate change on the distribution of North American trees.” BioScience 57 (2007): 939–948. Miller-Rushing, Abraham J., et al. “Photographs and herbarium specimens as tools to document phenological changes in response to global warming.” American Journal of Botany 93 (2006): 1,667–1,674. Moritz, Craig, et al. “Impact of a century of climate change on small-mammal communities in Yosemite National Park, USA.” Science 322 (2008): 261–264. Myneni, R. B., et al. “Increased plant growth in the northern high latitudes from 1981 to 1991. Nature 386 (1997): 698–702. Nussey, Daniel H., et al. “Selection on heritable phenotypic plasticity in a wild bird population.” Science 310 (2005): 304–306. Parmesan, Camille, and Gary Yohe. “A globally coherent fingerprint of climate change impacts across natural systems.” Nature 421 (2003): 37–42.

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———, et al. “Poleward shifts in geographical ranges of butterfly species associated with regional warming.” Nature 399 (1999): 579–583. Patz, J. A., et al. “Impact of regional climate change on human health.” Nature 438 (2005): 310–317. Pounds, J. A., et al. “Biological response to climate change on a tropical mountain.” Nature 398 (1999): 611–615. ———, et al. “Widespread amphibian extinctions from epidemic disease driven by global warming.” Nature 439 (2006): 161–167. Powell, J., and J. Logan. “Ghost forests, global warming and the mountain pine beetle.” American Entomologist 47 (2001): 160–172. Pulido, Francisco, and Peter Berthold. “Current selection for lower migratory activity will drive the evolution of residency in a migratory bird population.” Proceedings of the National Academy of Sciences 107 (2010): 7,341–7,346. Rice, Stanley A. “Plants help to keep the Earth from overheating.” Chap. 3 in Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Rogers, Christine A., et al., “Interaction of the onset of spring and elevated atmospheric CO2 on ragweed (Ambrosia artemesiifolia L.) pollen production.” Environmental Health Perspectives 114 (2006): 865–869. Sanz-Elorza, Mario, et al. “Changes in the high-mountain vegetation of the Central Iberian Peninsula as a probable sign of global warming.” Annals of Botany 92 (2003): 273–280. Schneider, Steven H., and T. L. Root. “Ecological implications of climate change will include surprises.” Biodiversity and Conservation 5 (1996): 1,109–1,119. S¸ekerciog˘lu, Çag˘an H., et al. “Climate change, elevational range shifts, and bird extinctions.” Conservation Biology 22 (2008): 149–150. Silliman, B. R., et al. “Drought, snails, and large-scale dieoff of southern US salt marshes.” Science 310 (2005): 1,803–1,806. Sturm, Matthew. “Arctic plants feel the heat.” Scientific American, May 2010, 66–73. Thomas, Chris D., and Jack J. Lennon. “Birds extend their ranges northward.” Nature 399 (1999): 213. Umina, P. A., et al. “A rapid shift in a classic clinal pattern Drosophila reflecting climate change.” Science 308 (2005): 691–693. van Mantgem, Phillip J., et al. “Widespread increase of tree mortality rates in the western United States.” Science 323 (2009): 521–524. Summarized by Pennisi, Elizabeth. “Western U.S. forests suffer death by degrees.” Science 323 (2009): 447. Visser, Marcel E., and Leonard J. M. Holleman. “Warmer springs disrupt the synchrony of oak and winter moth

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300 gymnosperms  300 phenology.” Proceedings of the Royal Society of London B (Biology) 286 (2001): 289–294. ———, ———, and Phillip Gienapp. “Shifts in caterpillar biomass phenology due to climate change and its impact on the breeding biology of an insectivorous bird.” Oecologia 147 (2006): 164–172. Willis, Kathy J., and Shonil A. Bhagwat. “Biodiversity and climate change.” Science 326 (2009): 806–807.

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first entry Wilson, R. W., et al. “Contribution of fish to the marine inorganic carbon cycle.” Science 323 (2009): 359–362. Zeebe, Richard E., et al. “Carbon emissions and acidification.” Science 321 (2008): 51–52.

gymnosperms  See conifers; seed plants.

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H habitat  fragmentation  Habitat fragmentation occurs when a large habitat, with large populations of many of its species, becomes divided into numerous smaller habitats. Fragmentation can occur as a result of natural processes. as the climate became drier over much of north america during the late neogene period, moist habitats became smaller and isolated from one another. Some species that were once widespread, such as the california fan palm Washingtonia filifera, may survive only as endemic species in desert springs. the isolated populations may diversify into different species or subspecies. For example, pupfishes were common in rivers and streams of what is now the Mojave and Sonora Deserts of southwestern north america. as desert conditions spread, the fishes were isolated into separate desert springs, where they evolved into separate species. today, Cyprinodon diabolis lives only in Devil’s Hole, and C. nevadensis nevadensis lives only in Saratoga Springs, both in Death Valley. today, human activity is causing more habitat fragmentation than has probably ever occurred during the history of the earth. Humans have altered most of the surface of the earth. they sometimes set aside wildlife preserves, which are only tiny fragments of the original habitat range, in which they permit wild species to survive. even these few remaining habitats are divided by roads, even the smallest of which may represent a barrier to the movement of some species. Habitat fragmentation has numerous significant effects on wild species, including the following: ●





enced by the environment outside, may not be suitable for the survival of many of the habitat’s species. in particular, many large animals stay away from the edges, where they would frequently come in contact with people. Breaking larger populations into smaller ones. each species has populations in each fragment that are effectively isolated from the populations in other fragments. each population therefore has a reduced amount of genetic variation upon which natural selection can act. the populations may be small enough that genetic drift may cause random genetic changes. Blocked migration. the species in each fragment are unable to migrate to other fragments. if corridors of migration were open, individuals could migrate from one fragment to another in the event that one of the fragments becomes uninhabitable. it is particularly important that organisms have corridors of migration over long distances, which will allow them to migrate (as they did after the most recent ice age) in response to global warming.

the only solution to the edge effect problem would be to establish larger protected areas. this is extremely unlikely to occur, since most unprotected areas are privately owned. in the western United States, the federal government owns a lot of land, some of which is protected as wilderness areas or national parks, while much of the national forest and national grassland area is leased to private timber

Edge effect. the edges of a habitat, the climatic conditions of which are strongly influ301

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302 herbivory  302 and ranching interests. The federal government could consolidate protected areas, removing some of the leased areas from private use. However, the leaseholders have strongly voiced their opinions that the land is effectively theirs, even if they do not own it. In what has been dubbed the “Sagebrush Rebellion,” some Bureau of Land Management officials have been intimidated by ranchers. A possible solution to the problem of migration may be to establish corridors of suitable habitat between the isolated fragments. This would also help to reduce the genetic problems of the isolated populations. This is now an important component of conservation planning. The Yellowstone to Yukon Conservation Initiative is intended to connect 2,000 miles (3,200 km) of protected mountain areas. The Mesoamerican Biological Corridor is intended to protect 80,000 square miles (208,000 square km), which is 27 percent of the land area in Central America. These corridors, however, have an even more pronounced edge effect than the fragments they connect. It remains to be seen whether these corridors can be established and, if so, whether they will have the desired effect of saving biodiversity. See also communities, ecological; endemic species; federal government role in conservation (United States). Further Reading Artis, Scott. “Combating habitat fragmentation with garden corridors.” Available online. URL: http://www. ecosystemgardening.com/gardens-as-wildlife-corri dors.html. Accessed August 1, 2010. Cawley, R. McGreggor. Federal Lands, Western Anger: The Sagebrush Rebellion and Federal Politics. Lawrence: University Press of Kansas, 1993. Clark, Rulon W., et al. “Roads, interrupted dispersal, and genetic diversity in timber rattlesnakes.” Conservation Biology 24 (2010): 1,059–1,069. Cole, David N. Beyond Naturalness: Rethinking Park and Wilderness Stewardship in an Era of Rapid Change. Washington, D.C.: Island Press, 2010. Collinge, Sharon K. Ecology of Fragmented Landscapes. Baltimore, Md.: Johns Hopkins, 2009. Damschen, Ellen I., et al. “Corridors increase plant species richness at large scales.” Science 313 (2006): 1,284–1,286. Fahrig, Lenore. “Effects of habitat fragmentation on biodiversity.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 587–516. Ferraz, Gonçalo, et al. “A large-scale deforestation experiment: Effects of patch area and isolation on Amazon birds.” Science 315 (2007): 238–241. Forman, Richard T. T., and Lauren E. Alexander. “Roads and their major ecological effects.” Annual Review of Ecology and Systematics 29 (1998): 207–231.

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first entry Gu, Weidong, et al. “Estimating the consequences of habitat fragmentation on extinction risk in dynamic landscapes.” Landscape Ecology 17 (2002): 699–710. Hilty, Jodi, et al. Corridor Ecology: The Science and Practice of Linking Landscapes for Biodiversity Conservation. Washington, D.C.: Island Press, 2006. Johnson, Douglas H. “Habitat fragmentation effects on birds in grasslands and wetlands: A critique of our knowledge.” Great Plains Research 11 (2001): 211–231. Letcher, Benjamin H., et al. “Population response to habitat fragmentation in a stream-dwelling brook trout population.” Public Library of Science One 2 (2007): e1139. Lindenmayer, David, and Joern Fischer. Habitat Fragmentation and Landscape Change: An Ecological and Conservation Synthesis. Washington, D.C.: Island Press, 2006. López, Alexander, and Alicia Jiménez. “Environmental conflict and cooperation: The Mesoamerican Biological Corridor as a Mechanism for Transborder Environmental Cooperation.” United Nations Environmental Programme. Available online. URL: http://www.unep.org/ dewa/eccreports/ECPI_Latin_America_Assessment_ Final_Report_Feb21. pdf. Accessed August 14, 2010. Opdam, Paul, and Dirk Wascher. “Climate change meets habitat fragmentation: linking landscape and biogeographical scale levels in research and conservation.” Biological Conservation 117 (2004): 285–297. Peterkin, George. “Reversing the habitat fragmentation of British woodlands.” Available online. URL: http:// assets.panda.org/downloads/ukforestsfragmentation. pdf. Accessed August 1, 2010. Ribeiro, M. C., et al. “The Brazilian Atlantic Forest: How much is left, and how is the remaining forest distributed? Implications for conservation.” Biological Conservation 142 (2009): 1,141–1,153. Tallmon, David A., et al. “Of mice and men and Trillium: Cascading effects of forest fragmentation.” Ecological Applications 13 (2003): 1,193–1,203. Turner, Monica G. “Landscape ecology: What is the state of the science?” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 319–344. Worboys, Graeme L. Connectivity Conservation: A Management Guide. London: Earthscan Publications, 2010.

herbivory  The term herbivore usually refers to an animal that eats leaves, stems, roots, or fruits. If an animal consumes and destroys a whole plant (for example, a seed that contains an embryonic plant), it is considered to be a predator. Herbivorous insects may lay hundreds of eggs and produce several generations of offspring in a single summer, building up huge populations. Popu-

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herbivory  303 lations of herbivores could quickly consume every green sprig on the planet. What prevents them from doing this? Why is the world green? The answer is that plants have many defenses that have evolved against herbivores. Plants derive no benefit from having their leaves eaten; natural selection has produced characteristics that protect the leaves from herbivores. Herbivory is necessary to the global ecosystem, but plants do everything they can to avoid it. Plants have numerous characteristics that make them difficult to eat, for example: ●●

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●● ●●

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Many plants have physical defenses such as spines and hairs. A cactus in the desert stores water in its stem; its spines protect it from thirsty animals. Hairs can be as effective against tiny insects as spines are against larger animals. All plant parts contain large amounts of cellulose, which is the major component of cell walls and which most animals cannot digest. Many stems are woody, and most animals cannot eat them. Grass stems and leaves are very rough because they contain silicon compounds. Deer will not browse pine needles in winter because the needles are very tough, waxy, and full of sticky resin. Plants that store large quantities of starch, such as potatoes, generally do so in places not accessible to most herbivores, such as in underground tubers or the cortex in the middle of the stem.

In addition, most plants contain chemical compounds that are harmful to herbivores, especially in their leaves. Some of these chemicals inhibit the efficiency of digestion; others are mildly, or strongly, poisonous. Examples include: ●●

●●

Mildly toxic alkaloids, such as caffeine, nicotine, cocaine, morphine, and theobromine (an ingredient in chocolate), are widespread in the plant kingdom. Various other chemicals, such as mustard oils and menthol (which gives mint its distinctive smell), also make some leaves unpalatable to herbivores. Some plants produce extremely toxic compounds. The ricin that is found in the seeds of the castor bean (Ricinus communis) is the third most toxic biological compound known, following the bacterial toxins of botulism and tetanus. Many of these very toxic compounds, however, may not be as toxic to specific herbivores that have evolved the ability to consume the plant.

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●●

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Some plants absorb toxic metal ions from the soil and accumulate them in their leaves. Locoweeds (genera Astragalus and Oxytropis) accumulate selenium. Milkweeds contain chemicals that interfere with heart muscle contractions. Some chemicals, such as those found in members of the nightshade family and the ricin found in castor bean plants, are among the deadliest chemicals known. The pesticide rotenone is extracted from South American and Asian leguminous plants.

These chemicals may be toxic not only to herbivores but also to bacteria and fungi. Therefore many chemicals found in leaves and bark have antibiotic and other pharmaceutical properties. Plants must use a great deal of energy and material to manufacture defensive structures and chemicals. If a plant makes no such compounds and escapes the herbivores, it can afford to grow larger and produce more seeds. In some cases, plants that grow rapidly and live for only a short period and that live only temporarily in one place do not produce many defensive chemicals. If herbivores find these plants they can eat them easily, but frequently these plants complete their life cycles before the herbivores find them. In contrast, slow-growing, longlived plants may benefit from producing defensive compounds. For example, botanist Stanley Rice and his students found that leaves of long-lived bur oak trees (Quercus macrocarpa) were more toxic than those of short-lived chokecherry leaves (Prunus virginiana) in the Black Hills. Plant defense against herbivores can also vary with the seasons. The leaves of trees in climates with cold winters may produce few defensive chemicals in the spring when insects are not yet abundant; during the summer, however, when insect populations increase, the leaves produce defensive chemicals. The tree can grow rapidly during the spring because it is not spending its energy on making defensive chemicals. This was the pattern observed by ecologist Paul Feeny in the English oak (Quercus robur). In climates with milder winters, however, herbivorous insects are abundant in early spring, and the trees may produce leaves that are toxic when they are young. Several researchers have found that oak leaves produce more tannins in the spring than in the summer. For example, botanist Stanley Rice and associates have found that the post oak (Quercus stellata) in the dry, warm forests of Oklahoma produce more tannins in the spring than in the summer (see figure on page 304). Ecologist Juha-Pekka Salminen and associates found the same pattern in Quercus robur (the same species studied by Feeny)

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304 herbivory  304

first entry

sequester the poisons in the cell vacuoles, where the poisons do not come in contact with the cell’s metabolic activities. However, the toxins are released when the mandibles or teeth of herbivores rupture the vacuoles. Many herbivores die during the winter or during dry seasons. In this way, seasonal changes help to protect plants from animals. But in tropical rain forests, herbivores are active all year. Rain forest plants protect themselves by poisonous chemicals. Since many of these chemicals have pharmaceutical properties, many significant drugs were first discovered in rain forest plants. Many more potential drugs are being lost as undiscovered tropical species are being driven into extinction before they can be studied. Humans who live by gathering wild plants concentrate on starchy storage organs such Oak leaves contain tannins, which inhibit the ability of herbivores to digest the leaves. Post oaks (Quercus stellata) in the dry, warm forests of Oklaas roots or on fruits and seeds. homa produce more tannins during the spring, when herbivorous insects Humans have bred crop plants are abundant, than during the summer. Vertical bars are 95 percent confithat have few physical or chemidence limits.  (Based on unpublished measurements by Stanley A. Rice and cal defenses against herbivores. Erica A. Corbett) This makes the plants very palatable to humans but also to insect in Finland, despite the very great difference between pests. The lack of physical and chemical defenses the seasonal temperature patterns of Oklahoma and against pests is one of the reasons that crop plants Finland. Both seasonal patterns—seasonal increases do not long survive “in the wild.” Because farms are or seasonal decreases in leaf toxicity—occur because dense concentrations of tender plants, populations plants cannot afford to defend all of their leaves all of insect pests explode. In response, modern agriculof the time. They produce defensive compounds just ture has grown dangerously dependent on pesticides. during the season when they might experience the Because plants are so well defended against most herbivore damage. them, herbivores cannot simply go out and eat any In some cases, plants economize their producplant they encounter. The world is not a gigantic tion of toxins by having inducible defenses. The salad bowl. The herbivores have evolved specialized leaves produce few toxins until the herbivores strategies for avoiding, or tolerating, the toxic or actually begin chewing on them. Herbivore attack tough portions of plants: induces the plant to produce the toxins. In some cases, a compound known as jasmonic acid is trans●● Avoidance. Although many caterpillars ported throughout the plant, causing leaves distant and some large animals eat whole leaves, from the attack to produce defensive compounds. In some tiny insects such as leaf miners eat other cases, herbivore attack causes a plant to proonly the tender mesophyll layers inside the duce volatile compounds that can travel through the leaf or the soft tissues of the inner bark. air and induce defensive responses in other leaves of Some insects feed only on the sap, which is the same plant or in other plants of the same speusually not toxic. cies. This response is common in birch and alder ●● Tolerance.  Ruminant mammals, such as trees. cows, can eat grass leaves, which contain How does a plant, whose leaves contain poisons, much cellulose, because their stomachs conkeep from poisoning itself? In most cases, plants tain bacteria that digest the cellulose. Simi-

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herbivory  305 larly, koalas can eat unpalatable eucalyptus leaves because of their complex intestines. This is an example of mutualism. Many caterpillars, mammals such as sloths, and birds such as the hoatzin consume massive quantities of leaves and excrete most of what they eat, including the poisons. In many cases, the herbivores can use the plant defenses for their own benefit. The caterpillars of monarch butterflies are poisonous. Inexperienced birds may eat them and then vomit, thereby learning to avoid them. But the caterpillars do not produce the poison themselves. It comes from the milkweeds that they eat. The caterpillars confine the poisons in specialized structures within their bodies, where the poison does not affect them but will harm a predator that, in the process of eating the caterpillar, breaks open the poison sacs. Another example involves chimpanzees, which, like humans, can be infected with malaria. The chimps eat the antimalarial leaves of a plant Trichilia rubescens, and they eat clay with the leaves, which enhances antimalarial activity of the leaves. Birds may include sprigs of aromatic plants in their nests which, according to some researchers, reduces the number of parasites on their nestlings. In many spice plants, chemicals deter herbivores from eating the leaves. The spice compounds in the leaves make them unsuitable as a staple food source for humans, but humans find these chemicals pleasant in small quantities. Many human cultures have made use of poisonous plant compounds such as caffeine as stimulants, but only in small quantities. Some plant species have intricate defenses against herbivores. Certain butterflies lay their eggs on leaves of passionflower vines. To prevent overcrowding of their larvae, the butterflies avoid laying eggs on leaves upon which eggs have already been laid. Some species of passionflower vine have evolved yellowish spots or bumps on the leaves, which look (to the eye of the butterfly) like eggs. Natural selection proceeded to modify these spots and bumps into structures that convincingly resemble insect eggs, because the butterflies most frequently avoided the plants that had the most egglike spots upon them. Despite all their defenses, most plants suffer at least some loss to herbivores. However, they have evolved methods of making the best of their losses. Consider a plant, for example, that is experiencing a mild drought or is growing in poor soil. If a herbivore consumes some of the leaves but does not harm the roots, the remaining leaves now have access to all of the water and minerals that the roots can provide. The additional water and minerals may therefore stimulate photosynthesis in the remaining leaves. This may allow compensatory regrowth, in

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which the plant grows back and becomes as large as it would have been if the herbivores had not attacked it. Plants defend their leaves, stems, and roots from herbivores. Fruits, in contrast, may attract animals rather than driving them away. The function of a fruit is to get the seeds transported to a new location, away from the parent plant. That is, animals (especially birds and mammals) and plants have coevolved a dispersal relationship that benefits both of them. This is why many fruits attract, rather than repel, animals. The effects of herbivory are not limited to the plant and the herbivore. They can produce a cascade of effects on ecological communities. For example, when herbivores eat the flowers, they affect the number of flowers available to pollinators. But in addition, the plant releases volatile chemicals, which may themselves affect the behavior of the pollinators. Plant toxins may affect not only the herbivores but the parasites that live upon the herbivores. When a plant species migrates or is transported by humans to a new location, it often becomes an invasive species. One of the reasons that it may successfully invade its new habitat is that it has left behind the herbivores that previously kept its populations under control. The plant populations may then evolve a different defensive chemistry suitable to their new biological environment. If the herbivore is subsequently introduced into the invasive plant population, which is sometimes done in an attempt to control the plants, the coevolution of plant and herbivore resumes in an altered form. Global warming may alter relationships between plants and insect herbivores. Higher temperatures may de-synchronize the germination or leafing of the plants and the hatching of the insects. The carbon dioxide itself may influence herbivory. Carbon dioxide stimulates photosynthesis and the production of organic compounds but does not enhance the amount of nitrogen fertilizer available to the plants. Some plant defensive compounds contain nitrogen atoms. Therefore, high levels of atmospheric carbon dioxide might cause the plants to produce tissues that are more palatable to herbivores. However, when the herbivores eat more and grow larger, they may attract parasites or predators that actually reduce their populations. Herbivory is an ecological interaction that can be readily adapted to classroom studies. Expertise, chemicals, and equipment are often necessary to directly measure the toxic compounds in plants—or even to know which compounds should be measured. However, there are indirect methods of measuring plant toxicity that students have found to be understandable and interesting. Brine shrimp (Artemia

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306 herbivory  306 salina) are tiny crustaceans that are often used to determine toxicity. Thousands of eggs can be cheaply purchased at pet supply stores. The student needs only to add freshly hatched brine shrimp to brackish water that contains a plant extract, wait a day, and count how many of the shrimp have survived. From this, the LD50 can be calculated. This is the “lethal dose” concentration that kills 50 percent of the animals and is a standard measurement in toxicity studies. A more toxic extract will have a lower LD50. Similarly, the extract can be mixed into a standardized chow which is fed to tobacco hornworm caterpillars (Manduca sexta). Both the chow and the caterpillars are available from biological supply companies. Each caterpillar can be weighed every few days. A more toxic compound will cause the caterpillars to grow more slowly than a less toxic compound. Evolution has produced a prodigious variety of adaptations by which plants, as much as possible, keep animals from eating their leaves, stems, and roots and an equally prodigious variety of adaptations by which animals can eat the plants anyway. Evolutionary innovation in plant defense stimulates evolutionary innovation in the ability of animals to get around these defenses. See also biodiversity, resources for medicine; coevolution; seed dispersal. Further Reading Anderson, D. “Below-ground herbivory in natural communities: A review emphasizing fossorial animals.” Quarterly Review of Biology 62 (1987): 261–286. Berenbaum, May, Arthur Zangerl, and James Nitao. “Constraints on chemical coevolution: Wild parsnips Pastinaca sativa and the parsnip webworm Depressaria pastinacella.” Evolution 40 (1986): 1,215–1,228. Choat, J. H., and K. D. Clements. “Vertebrate herbivores in marine and terrestrial environments: A nutritional ecology perspective.” Annual Review of Ecology and Systematics 29 (1998): 375–403. Creelman, Robert A., and J. E. Mullet. “Jasmonic acid distribution and action in plants: Regulation during development and response to biotic and abiotic stress.” Proceedings of the National Academy of Sciences USA 92 (1995): 4,114–4,119. Dearing, M. Denise, et al. “The influence of plant secondary metabolites on the nutritional ecology of herbivorous terrestrial vertebrates.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 169–189. Donaldson, J. R., and Richard L. Lindroth. “Genetics, environment, and their interaction determine efficacy of chemical defense in trembling aspen.” Ecology 88 (2007): 729–739. Feeny, Paul. “Seasonal changes in oak leaf tannins and nutrients as a cause of spring feeding by winter moth caterpillars.” Ecology 51 (1970): 565–581.

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first entry Hanhimäki, Sinikka. “Induced resistance in mountain birch: Defense against leaf-chewing insect guild and herbivore competition.” Oecologia 81 (1989): 242–248. Knepp, R. G., et al. “Elevated CO2 reduces leaf damage by insect herbivores in a forest community.” New Phytologist 167 (2005): 207–218. Lambert, E. C., et al. “Tritrophic effects of xanthotoxin on the polyembryonic parasitoid Copidosoma sosares (Hymenoptera: Encyrtidae). Journal of Chemical Ecology 34 (2008): 783–789. Lewinsohn, Thomas M., et al. “Insects on plants: Diversity of herbivore assemblages revisited.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 597–620. Núñez-Farfán, Juan, et al. “The evolution of resistance and tolerance in herbivores.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 541–566. Ohgushi, Takayuki. “Indirect interaction webs: Herbivoreinduced effects through trait change in plants.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 81–105. Peacock, L., and S. Herrick. “Responses of the willow beetle Phratora vulgatissima to genetically and spatially diverse Salix spp. plantations.” Journal of Applied Ecology 37 (2000): 821–831. Rice, Stanley A., and Ian B. Maness. “Brine shrimp bioassays: A useful technique in biological investigations.” American Biology Teacher 66 (2004): 208–215. ———, and Jennifer R. Griffin. “The hornworm assay: Useful in mathematically-based biological investigations.” American Biology Teacher 66 (2004): 487–491. Salminen, Juha-Pekka, et al. “Seasonal variation in the content of hydrolyzable tannins, flavonoid glycosides, and proanthocyanidins in oak leaves.” Journal of Chemical Ecology 30 (2004): 1,693–1,711. Schultz, Jack C. “Seasonal and individual variation in leaf quality of two northern hardwoods tree species, sugar maple (Acer saccharum) and yellow birch (Betula allegheniensis). American Journal of Botany 69 (1982): 753–759. Seldal, Tarald, et al. “Wound-induced proteinase inhibitors in gray alder (Alnus incana): A defense mechanism against attacking insects.” Oikos 71 (1994): 239–245. Stiling, Peter, et al. “Elevated CO2 lowers relative and absolute herbivore density across all species of a scrub-oak forest.” Oecologia 134 (2003): 82–87. ———, and Tatiana Cornelissen. “How does elevated carbon dioxide (CO2) affect plant-herbivore interactions? A field experiment and meta-analysis of CO2mediated changes on plant chemistry and herbivore performance.” Global Change Biology 13 (2007): 1,823–1,842. Tscharntke, Teja, et al. “Herbivory, induced resistance, and interplant signal transfer in Alnus glutinosa.” Biochemical Systematics and Ecology 29 (2001): 1,025–1,047.

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hybridization  307 Zangerl, Arthur R., and May R. Berenbaum. “Effects of florivory on floral volatile emissions and pollination success in the wild parsnip.” Arthropod-Plant Interactions 3 (2009): 181–191. ——— and ———. “Parsnip webworms and host plants at home and abroad: Trophic complexity in a geographic mosaic.” Ecology 87 (2006): 3,070–3,081. ———, et al. “Selection for chemical trait remixing in an invasive weed after reassociation with a coevolved specialist.” Proceedings of the National Academy of Sciences USA 105 (2008): 4,547–4,552.

Holocene epoch  See Neogene period, bio-

diversity in.

Humboldt, Alexander

von  (1769–1859)  ­ erman  Naturalist and explorer  Born SeptemG ber 14, 1769, in Berlin, Baron Friedrich Wilhelm Heinrich Alexander Freierr von Humboldt was one of the most important scientists of the late 18th and early 19th centuries. He began the modern study of biogeography. At an early age, he had a passion for studying plants and animals. At the University of Frankfurt, he studied subjects from commerce to politics to geology. Though he rose to a high position as a geologist as a government assessor of mines, he resigned in order to travel and conduct scientific investigation. In 1799, he began a scientific journey through Latin America, including Mexico, the Caribbean, and western South America, with French botanist Aimé Bonpland. He traveled 1,725 miles (2,776 km) in the Amazon Basin, where he was the first European to (painfully) discover the electric eel. He climbed mountains in the Andes, nearly reaching the top of the 20,565-foot (6,268-m) Chimborazo volcano in Ecuador. He collected plants and, with Bonpland, was the first scientist to realize that temperature patterns (due both to latitude and to elevation) largely determined the distribution of plant species. Throughout this expedition he made detailed measurements of temperature and magnetic fields with the finest scientific equipment available at the time, one of the first scientists to insist on such precision. Such measurements allowed him to discover new ocean currents, including one now called the Humboldt Current (off the west coast of South America), and that Earth’s magnetic field was stronger at the poles and weaker near the equator. After meeting President Thomas Jefferson, Humboldt returned to Germany in 1804. Humboldt analyzed his data and published many books about his journey over the next 21 years. As he did so, he proposed that South Amer-

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ica and Africa had once been joined into a single continent, a theory not fully vindicated until continental drift was accepted a century and a half later. Then he turned his thought to the unification of all branches of scientific knowledge in his five-volume Kosmos, which he began to publish in 1845. His thought was strongly influenced by the romantic movement, which idealized nature as being perfect apart from human interference. Because of Humboldt’s enormous influence in science, scientists until recently tended to ignore the important role that native peoples have had in determining natural ecological communities. While writing his books, Humboldt traveled little, until he took a 9,614-mile (15,472-km) journey through Russia in 1829. Humboldt’s insights and his bold adventures inspired many scientists, most notably Charles Darwin, who saw himself as retracing Humboldt’s journey when he visited South America. Darwin said of Humboldt, “I have always admired him. Now I worship him.” Humboldt died in Berlin on May 6, 1859. See also biogeography; Darwin, Charles. Further Reading Humboldt, Alexander von. Personal Narrative of a Journey to the Equinoctial Regions of the New Continent. Abridged Edition by Jason Wilson. New York: Penguin, 1996. ———, and Aimé Bonpland. Essay on the Geography of Plants. Stephen T. Jackson, ed., and Sylvie Romanowski, transl. Chicago: University of Chicago, 2010. Lack, H. Walter. Alexander von Humboldt: The Botanical Exploration of the Americas. New York: Prestel, 2009. Rupke, Nicolaas A. Alexander von Humboldt: A Metabiography. Chicago: University of Chicago, 2008. Walls, Laura Dassow. The Passage to Cosmos: Alexander von Humboldt and the Shaping of America. Chicago: University of Chicago, 2009.

Hutchinson, G. Evelyn  See competition,

ecological.

hybridization  Hybridization is the crossbreeding of different species of organisms. The term hybrid has also been used for crosses between varieties within a species (as in hybrid corn within the species Zea mays). The offspring with many heterozygous traits produced by intraspecific crosses may produce hybrid vigor. However, conservation and evolutionary biologists generally restrict the term hybrid to crosses between species. According to the biological species concept, distinct species do not normally produce fertile

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308 hybridization  308

first entry

offspring. This is most obviously the case with crosses between donkeys and horses, resulting in mules, which are very strong but are sterile. Crosses between lions and tigers (such as ligers and tigons) have also occurred in zoos (see table). Many other hybrids are possible between feline species. While even fertile hybrids may be produced between different feline species, they are rare in the wild, which suggests that either the species nearly always avoid one another when mating and/or the hybrid offspring have reduced health or fertility. Hybrids also occur among canine species. For example, black coat color in forest wolves (Canis lupus) has been traced to hybridization with domesticated dogs (Canis familiaris), a species that recently evolved from wolves. Hybrids have also been reported between species of fishes. The bluegill (Lepomis macrochirus) can cross with the green sunfish (L. cyanellis). Intergeneric hybrids, such as between pumas and leopards and between dromedaries and llamas, have also been reported (see table on page 309). When a scientific name is assigned to a hybrid species, an x often precedes the specific name.

Hybrids between plant species in the same genus occur more often than hybrids between animal species. Hybridization in plants is not usually successful, for at least two reasons: ●●

The two species may pollinate at different times of the year. Among the oaks of North America, hybridization can occur among species of white oaks and among species of red and black oaks (genus Quercus). However, all of the white oaks have acorns that mature during the same year, while most of the red and black oaks have acorns that mature the following year, after pollination. Because of these differences in reproductive pattern, hybrids between the two groups of oaks cannot occur. Hybridization between species of pine (the bishop pine Pinus muricata and the Monterey pine P. radiata) and between species of alders (the seaside alder Alnus maritima and the hazel alder A. serrulata) cannot occur, as pollination occurs at different times of the year.

Interspecific Crosses in Animals and Plants (Within Genera) Parent

Parent

Hybrid

Jackass (Equus asinus)

Mare (E. caballus)

Mule

Jenny (Equus asinus)

Stallion (E. caballus)

Hinny

Male tiger (Panthera tigris)

Lioness (P. leo)

Tigon

Tigress (Panthera tigris)

Male lion (P. leo)

Liger

Leopard (Panthera pardus)

Lion (P. leo)

Leopon

Bluegill (Lepomis macrochirus)

Green sunfish (L. cyanellis)

Hybrid sunfish

Larkspur (Delphinium hesperium)

Larkspur (D. recurvatum)

D. gypsophilium

Penstemon (Penstemon centrantifolius)

Penstemon (P. grinnellii)

P. spectabilis

Japanese larch (Larix kaempferi)

European larch (L. decidua)

Dunkeld larch

Magnolia (Magnolia denudata)

Magnolia (M. liliiflora)

M. soulangeana

American sycamore (Platanus occidentalis)

European (P. orientalis)

London plane

Elm (Ulmus glabra)

Elm (U. minor)

U. x hollandica

Wingnut (Pterocarya fraxinifolia)

Wingnut (P. stenoptera)

P. x rehderiana

Linden (Tilia cordata)

Linden (T. platyphyllos)

T. x europaea

White poplar (Populus alba)

Aspen (P. tremula)

Gray poplar

Arbutus (Arbutus unedo)

Arbutus (A. andrachne)

A. x andrachnoides

Horse chestnut (Aesculus hippocastanum)

Horse chestnut (A. pavia)

A. x carnea

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hybridization  309 Intergeneric Crosses Reported from Animals and Plants Parent

Parent

Leopard (Panthera pardus)

Puma (Felis concolor)

Dromedary (Camelus dromedarius)

Guanaco (Lama guanicoe)

Platygyra coral

Leptoria coral

Wild wheat (Triticum boeoticum)

Goatgrass (Aegilops speltoides)

Durum wheat

Tetraploid wheat (Triticum dicoccum)

Goatgrass (Aegilops squarrosa)

Bread wheat

Bread wheat (Triticum aestivum)

Rye (Secale cereale)

Triticale

Radish (Raphanus)

Mustard (Brassica)

x Raphanobrassica

Cypress (Cupressus)

Cypress (Chamaecyparis)

x Cupressocyparis

Heuchera sanguinea

Tiarella cordifolia

x Heucherella

Purshia tridentata

Cowania stansburiana

P. glandulosa

Mandarin (Citrus reticulata)

Kumquat (Fortunella)

Calamondin

Cattleya intermedia orchid

Laelia lobata orchid

x Laeliocattleya

Laelia milleri orchid

Brassavola nodosa orchid

x Brassolaelia

Cattleya orchid

Broughtonia orchid

x Cattleytonia

●●

The two species may specialize on different habitats. Hybrids can and do occur within the white oak and within the black-red oak groups. Hybridization usually produces solitary unusual trees or scattered clusters with characteristics intermediate between the species. Occasionally there will be a widespread zone of hybridization between oak species. The oak species remain distinct probably because the hybrids are not adapted to either of the habitats of the parents. For example, even though post oak (Q. stellata) and bur oak (Q. macrocarpa) are both white oaks, hybrids between them would probably not grow well under natural conditions, since post oaks specialize on relatively dry and bur oaks on relatively moist habitats. Natural hybrids (Q. x guadalupensis) have been reported but have not become widespread. The California black oak (Q. kelloggii), a tall, deciduous tree, can cross with the interior live oak (Q. wislizenii var. frutescens), an evergreen shrub, to produce the oracle oak (Q. x morehus), which is a small, partly deciduous tree with leaf shape and other characteristics intermediate between those of its parents. All three species occur in the mountains of southern California, but the

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Hybrid

hybrid is rare. While most hybrids become extinct, recurrent origin maintains small populations of them. If the hybridization event produces a plant with an odd number of chromosomes, the resulting plant is sterile. There are two ways in which this sterile hybrid can produce seeds. ●●

●●

First, mutations may allow the plant to go ahead and produce seeds even without sexual reproduction. This process of apomixis produces seeds that are exact genetic copies of the sterile parent. The result may be a new species that never has sexual reproduction. Examples include the common dandelion (Taraxacum oficinale) and a South African oxalis (Oxalis pes-caprae). Second, if the reproductive cells undergo a spontaneous chromosome doubling, the resulting tetraploid plant (with chromosomes in groups of four) is no longer sterile: Each chromosome can match up with a copy of itself during meiosis. The fertile hybrid plant can now produce seeds and perhaps a small population of tetraploids. The hybrid tetraploid plants, though now fertile, have a different number of chromosomes than does

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310 hybridization  310 either parent species. Therefore it cannot crossbreed with either of its parent species; it can only cross-pollinate with other members of the tetraploid population. The tetraploid population, reproductively isolated from the parental species, now functions as a new species. Examples of spontaneous chromosome doubling that has restored the fertility of the reproductive cells of the sterile plant are salt grasses, tobaccos, mustards, and sunflowers: ●●

●●

●● ●●

Cross-pollination between Spartina maritima (native to Europe) and S. alterniflora (native to California), two species of saltmarsh grasses, occurred when S. alterniflora was introduced into England. The hybrid, S. x townsendii, was sterile. Chromosome doubling in the sterile hybrid resulted in S. anglia, which now grows vigorously in English salt marshes. The common tobacco Nicotiana tabacum (with 48 chromosomes) can cross with another tobacco species, N. glutinosa. However, N. glutinosa has only 24 chromosomes. A sterile hybrid, with 36 chromosomes, results. Spontaneous chromosome doubling can occur in this sterile hybrid, resulting in seeds with 72 chromosomes. The result is the hybrid species N. digluta. Hybridization among three mustard species in the wild has produced three new species. The sunflowers Helianthus deserticola and H. anomalus have been shown to have hybrid origins. Botanist Loren Rieseberg has experimentally replicated the hybrid origin of H. anomalus in the greenhouse. By crossing H. annuus with H. petiolaris, Rieseberg produced three independent hybrid lines. Only four generations were required to select vigorous hybrids. The genetic markers of the greenhouse hybrids closely resemble those in the wild populations of H. anomalus.

In plants, intergeneric hybrids (while still rare) are more common than in animals. Russian botanist Georgi Karpechenko crossed the radish Raphanus sativus with the cabbage Brassica oleracea, producing a Raphanobrassica hybrid in 1927. Unfortunately, the hybrid had the leaves of radish and the roots of cabbage. Wild Raphanobrassica hybrids have been reported from California. Triticale, a hybrid of wheat and rye, is reported to have the high yield of wheat and the hardiness of rye but is rarely

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first entry grown on a commercial scale. Hybrids between plant genera are known from orchids and cypresses as well (see table on page 309). Among orchids, hybrids are possible among three or even more genera, although this almost always occurs under artificial conditions. In natural habitats, pollinator specificity usually prevents extensive crossings among orchids. For example, Brassolaeliocattleya is a cross among the genera Brassavola, Laelia, and Cattleya. When a scientific name is assigned to an intergeneric hybrid, the x may precede the generic name. Natural hybrids tend to be rare, but hybrid plants produced for horticultural purposes can be vigorous. The reduced reproductive capacity of the horticultural hybrid is not a drawback because artificial propagation is available. Perhaps the plant hybridizations that are most famous in the history of the world are the crosses that produced modern wheat. The wild wheat Triticum boeoticum had chromosomes in pairs (diploid, 14 chromosomes) and was bred by ancient farmers into the cultivated einkorn wheat Triticum monococcum. However, T. boeoticum accidentally cross-pollinated with the wild goatgrass Aegilops speltoides. The chromosomes from the two parents were incompatible, but chromosome doubling produced a fertile hybrid with chromosomes in groups of four (tetraploid, with 28 chromosomes), the wild T. dicoccoides. This was bred by ancient farmers into the emmer wheat T. dicoccum and into durum (T. durum) and other wheats. T. dicoccum also accidentally cross-pollinated with a wild goatgrass, this time A. squarrosa. Chromosome doubling turned a sterile hybrid into a species of wheat with chromosomes in groups of six (hexaploid, 42 chromosomes) that are today’s major wheat species T. spelta (spelt) and T. aestivum (bread wheat) (see table on page 309). One of the distinguishing features of modern bread wheat is the gluten protein, which makes the flour sticky, allowing it to hold in bubbles of carbon dioxide during leavening. The gene for gluten apparently came not from the Triticum ancestor but from the Aegilops squarrosa weed with which emmer wheat accidentally hybridized. Hybridization, aside from producing new plant species, can also facilitate the transfer of genes from one species of plant to another. Consider two plant species that hybridize and produce a new hybrid species. The two original plant species seldom hybridize with one another but may be able to crossbreed more often with the intermediate hybrid species. Genes from the first plant species can enter into the hybrid population by cross-pollination and can then enter into the population of the second plant species, also by cross-pollination. The hybrid species has thus acted as a bridge over which genes have crossed, or

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hydrological cycle  311 introgressed, from one species into another. This concept of introgressive hybridization or introgression was first suggested by Edgar Anderson, an early 20th-century expert on the genetic history of crop species. The relative rarity of hybridization between species suggests that a new species, once it evolves, has a coordinated team of genes that would be disrupted by mixing with a different set of genes. This may explain why evolutionary changes may occur so rapidly when a species first forms, followed by a period of relative stability. Hybridization raises particularly interesting questions about the conservation status of endangered species. Are the hybrids, one or both of whose parents may be endangered, also protected? While artificial hybrids are not a concern for conservation biologists, hybrids that occur in nature as a result of human activity, such as global warming, may deserve protection. For example, what about the grolar bear? First reported in northern Canada in 2006, this hybrid between a grizzly bear and a polar bear may have come about because global warming has encouraged grizzly bears to migrate northward into polar bear territory. The man who shot the grolar bear was worried that he had violated the terms of his hunting license, which permitted him to hunt only one of the parental species. See also speciation. Further Reading Anderson, Tovi M., et al. “Molecular and evolutionary history of melanism in North American gray wolves.” Science 323 (2009): 1,339–1,343. Gompert, Zachariah, et al. “Homoploid hybrid speciation in an extreme habitat.” Science 314 (2006): 1,923–1,925. Kadereit, J. W., et al. “Reciprocal hybridization at different times between Senecio flavus and Senecio glaucus gave rise to two polyploid species in north Africa and south-west Asia.” New Phytologist 169 (2006): 431–441. Miller, Howard, and Samuel Lamb. Oaks of North America. Happy Camp, Calif.: Naturegraph Publishers, 1985. Pfennig, Karin S. “Facultative mate choice drives adaptive hybridization.” Science 318 (2007): 965–967. Schwarzbach, Andrea, Lisa A. Donovan, and Loren H. Rieseberg. “Transgressive character expression in a hybrid sunflower species.” American Journal of Botany 88 (2001): 270–277.

hydrological cycle  Also known as the water

cycle, the hydrological cycle is the movement of water molecules through the ecosystems of the Earth. The

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details of this cycle have an overwhelming impact on which ecological communities live in which locations and on the effects of global warming. Oceans. About 98 percent of the water on Earth is oceanic salt water. Another 1.6 percent is ice, with the remaining 0.4 percent freshwater on land surfaces. The volume of water in the oceans does not remain constant. During periods of global warming, ocean levels rise for two reasons. First, the water expands. Second, ice on land surfaces melts. These two processes contribute about equally to sea-level rise during warm periods. During the most recent ice age, ocean levels were more than 300 feet (about 100 m) lower than they are today. The oceans also have a profound effect on global temperatures. Oceans absorb heat during warm periods and release it during cold periods of history, although this process is too slow to counteract the current crisis of global warming. Land areas near oceans have much less temperature fluctuation during the year than do land areas far from oceans. This is the reason that the winters are warmer and the summers cooler in Seattle than in Minneapolis, despite their similar latitude and amount of heat they receive from the Sun. Ocean currents redistribute heat around the world. One important example is the Gulf Stream, part of a larger “global conveyor” system of ocean currents. The warm Gulf Stream waters carry heat from the Caribbean toward Europe. This is the reason that the climate is warmer in England than in Labrador, even though both are at similar latitudes. Evaporation and condensation. Evaporation from the ocean surfaces is the major source of water vapor in the atmosphere. Water vapor and clouds also have a profound effect on global temperatures. Water vapor is a greenhouse gas. When condensation forms clouds, these clouds have two effects on heat. First, the albedo (reflectivity) of clouds sends much solar energy right back into outer space, preventing it from heating the Earth. Second, clouds absorb and emit infrared light, thus preventing the Earth’s surface from emitting infrared light into outer space. Clouds, therefore, both cool and warm the Earth. Different kinds of clouds have different relative amounts of heating and cooling effects on the Earth. Clouds are the principal method by which water that evaporates from oceans is transported over land surfaces. Precipitation. At the tops of clouds, water droplets may be supercooled, that is, remain liquid below the freezing point. When a droplet receives a freezing nucleus (for example, a dust or sulfate particle), it freezes. Frozen water can fall in the form of snow, hail, or sleet. Most raindrops are ice that melted on the way down.

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312 hydrological cycle 312

first entry

Deforestation allows rainwater to rush down the mountain slope and cause floods, rather than percolating down into the soil. Transpiration from forests also puts a great deal of water vapor into the air.

the biodiversity and ecological communities of the earth are primarily influenced by temperature and precipitation. terrestrial ecological communities with more precipitation have greater productivity and more species. thousands of years ago, the Sahara received more rainfall and was home to many more plant and animal species. the annual timing of precipitation is also important. the highest species diversity is in the tropical rain forests, where rainfall is uniform. Snow and ice that accumulate in the winter may melt in the spring, supplying water to environments that would otherwise experience a dry summer. Dry summers would probably cause the mountains of western north america to have less forest growth if it were not for the winter snowpack. Groundwater and runoff. Rain and snow that enter the ground slowly may percolate down into shallow aquifers, which feed creeks and rivers with a relatively uniform flow of water. By intercepting raindrops, vegetation cover allows much more water to percolate into the soil than does bare soil. Runoff

xviii+598_Biodiversity_F.indd 312

water floods quickly into creeks and rivers, often carrying much soil with it and occasionally causing mudslides (see figure). thicker vegetation cover reduces the amount of runoff (see table on page 313). the fact that deforestation increases runoff has been experimentally demonstrated on whole mountainsides, such as the Hubbard Brook watershed in new Hampshire where ecologist Gene likens and associates clear-cut some mountain slopes and left adjacent ones intact. Similar results have been found at the coweeta watershed in the southern appalachians. Reservoirs delay the flow of runoff into rivers and oceans. Reservoirs allow humans to have water for irrigation and hydroelectricity. they do not appear to significantly increase humidity; the mountains near reservoirs in the desert Southwest appear no different from those farther away. the impoundment of runoff in reservoirs has measurably reduced the amount of sea-level rise that would otherwise have occurred with global warming.

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hydrological cycle  313 Effect of Vegetation Cover   on Runoff of Water Plant Cover

Percent of Rainfall Lost as Runoff

Ungrazed thicket

0.4

Grass

1.9

Millet

26.0

Bare ground

50.4

●●

Note: From Redman

Transpiration. The roots of plants remove a tremendous amount of water from the soil and return it to the air as water vapor. Water transpired from plants adds to water evaporated from nonliving surfaces to create total evapotranspiration. Some trees remove so much groundwater that the flow of water in creeks and rivers is significantly reduced. Examples are red cedars (Juniperus virginiana) in the Midwest and tamarisks (genus Tamarix) in the West. In most cases, especially on sloping ground, the amount of water that percolates into the soil as a result of the vegetation cover greatly exceeds the amount removed by transpiration. Water vapor from transpiration can significantly contribute to cloud formation and precipitation. Transpiration accounts for about a half to a third of the precipitation in the world (see table); on a local scale it can be very significant. About half of the rain that falls on the Amazon basin comes from rain forest transpiration and about a quarter of the rain in the Great Smoky Mountains of the eastern United States comes from transpiration. Much of the haze in these mountains is transpired water; the rest of it is photochemical smog from isoprene compounds produced by the trees, particularly by oaks. Although it is difficult to prove, there are several instances in which deforestation has led to reduced rainfall. In each case, it is impossible to clearly separate the effects of natural climate change from the effects of deforestation, but deforestation appears to have had a significant impact: ●●

●●

The Mediterranean basin and the Anatolian peninsula used to have extensive forests. Humans cut down these forests several times during ancient history. Today there is not enough rainfall for extensive forests. The islands of the eastern Atlantic were extensively forested until the Spaniards and Portuguese cut down the trees. “Verde” is Spanish for “green” and “madeira” Portuguese for “wood,” both of which better described Cape Verde and Madeira prior to European contact than after. Christopher

xviii+598_Biodiversity_F.indd 313

●●

Columbus commented that deforestation in the Azores and Canary Islands appeared to have made the climate less misty and rainy. Rapa Nui (Easter Island) used to have extensive forests, which included Elaeocarpus raratongensis and Alphitonia zizyphoides, as well as Jubaea chilensis, the world’s largest palm trees. Within a few centuries of settling there, the inhabitants had cut down all of the trees and introduced rats that ate many of the palm seeds. The climate of the island is now too dry to permit the growth of forests. In 1907, Australians built a 2,000-mile (3,200-km) “bunny fence” in an unsuccessful attempt to prevent the spread of introduced rabbits. Natural vegetation dominates one side, while cleared land used for ­agriculture and ranching dominates the other side. Rainfall is 20 percent lower on the cleared side of the fence.

Movement of Water Through   Global Ecosystems Compartment or Process

Movement (1,000 km3 per year)

Evaporation from sea

436.5

Precipitation into sea

391

Precipitation onto: Forests

54

Grassland

31

Irrigated cropland

11.6

Wetlands, lakes Other Total

2.7 11.7 111

Evapotranspiration from: Forests

29

Grassland

21

Irrigated cropland

7.6

Wetlands, lakes

1.5

Other

6.4

Total

65.5

Surface runoff

15.3

Subsurface runoff

30.2

Used and released by humans Returned to sea in rivers

2.8 45.5

Note: From Oki and Kanae

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314 hydrological cycle  314 It is clear that ecological communities not only depend upon precipitation but that they influence it. By destroying vegetation cover, humans may be significantly altering the amount of precipitation in some areas. Global warming will have yet further effects on the hydrological cycle. See also communities, ecological; ecosystems. Further Reading Barnett, Tim P., et al. “Human-induced changes in the hydrology of the western United States.” Science 319 (2008): 1,080–1,083. Bosch, J. M., and J. D. Hewlett. “A review of catchment experiments to determine the effect of vegetation changes on water yield and evapotranspiration.” Journal of Hydrology 103 (1982): 232–333. Chao, B. F., et al. “Impact of artificial reservoir water impoundment on global sea level.” Science 320 (2008): 212–214. Costa, Marcos Heil, et al. “Effects of large-scale changes in land cover on the discharge of the Tocantins River, southeastern Amazonia.” Journal of Hydrology 283 (2003): 206–217. Coweeta Long Term Ecological Research. “Coweeta Long Term Ecological Research.” Available online. URL: http://coweeta.ecology.uga.edu. Accessed June 25, 2010.

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first entry Dransfield, J., et al. “A recently extinct palm from Easter Island.” Nature 312 (1984): 750–752. Gordon, Line J., et al. “Human modification of global water vapor flows from the land surface.” Proceedings of the National Academy of Sciences 102 (2005): 7,612–7,617. Hubbard Brook Research Foundation. “Hubbard Brook ecosystem study.” Available online. URL: http://www. hubbardbrook.org. Accessed February 27, 2011. Kerr, Richard A. “Another side to the climate-cloud conundrum finally revealed.” Science 319 (2008): 889. Kröpelin, S., et al. “Climate-driven ecosystem succession in the Sahara: The past 6000 years.” Science 320 (2008): 765–768. Likens, Gene E., et al. “Effects of forest cutting and herbicide treatment on nutrient budgets in the Hubbard Brook watershed-ecosystem.” Ecological Monographs 40 (1970): 23–47. Noticewala, Sonal. “At Australia’s bunny fence, variable cloudiness prompts climate study.” New York Times, August 14, 2007. Available online. URL: http://www. nytimes.com/2007/08/14/science/earth/14fenc.html. Accessed August 8, 2011. Oki, Taikan, and Shinjiro Kanae. “Global hydrological cycles and world water resources.” Science 313 (2006): 1,068–1,072. Redman, Charles L. Human Impact on Ancient Environments. Tucson: University of Arizona Press, 2001.

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I ice  ages  the ice ages are recurring periods of

lations were oversimplified but provided a major insight that turned out to be correct. croll was not a professor, but a janitor who spent a lot of time in the library. the details of how the variations in the earth’s orbit—a combination of changes in the distance from the Sun and the tilt of the earth— caused the ice ages were worked out by the Serbian mathematician Milutin Milankovi´c. the dates that emerged from Milankovi´c’s calculations for when ice ages were most likely to have occurred did not correspond to what was then believed to be the times of glaciation. therefore by the time Milankovi´c died he did not have the satisfaction of seeing his theory vindicated. now that scientists have radiometric dates of several of the glaciations, they see that Milankovi´c was largely correct. Variations in earth’s angle and orbit affect the ice ages because they shift the balance of solar energy going into and out of the planet. Short, cool summers resulting from less solar energy—because of a combination of distance from the Sun and angle of the sunlight—reduce snowmelt. the increased area covered with snow reflects more light into outer space, increasing the albedo (reflected light) of the planet. this further shifts the balance of climate toward an ice age. the accumulation of ice and snow in the northern latitudes eventually pushes the ice southward in great rivers of snow (glaciers). if the summers in the latitudes farther south are cool enough that the ice does not melt as much as it advances, then the result is glaciation. the rate of advance was variable but has seldom exceeded three feet (one meter) a year. the return of warmer summers results in glaciers melting more than they advance. the relatively slight differences in solar radiation seem inadequate to explain the drastic changes

glaciation that began during the Pleistocene epoch of the Quaternary period. During each ice age, glaciers advanced from the north across north america and eurasia. an interglacial period followed each glaciation, in which the glaciers melted and retreated. each ice age glaciation plus its subsequent interglacial period lasted about 100,000 years. therefore, during the approximately 2 million years of the Pleistocene, about 20 ice ages occurred, with the Holocene epoch consisting of the time since the peak of the most recent glaciation. in many cases, a more recent glaciation has obliterated the geological evidences of an earlier one. Several of the more extensive glaciations can be directly studied from geological deposits. the Quaternary period has been one of the coldest in all of earth’s history, but glaciations also occurred many times in the past. For example, glaciations occurred in the southern continent of Gondwana 355 to 280 million years ago and in antarctica beginning 33 million years ago. Perhaps the most extensive ice ages occurred during the Precambrian time. three times, the earth nearly froze into a permanent ball of ice popularly called Snowball earth. this entry focuses upon the recurring northern Hemisphere ice ages of the Quaternary period. By the middle of the 19th century, scientists (led by geologist louis agassiz) had determined that there had been at least one ice age in the northern Hemisphere. But nobody understood what caused them. During the 1860s, scientific journals received papers about physics from a certain James croll of anderson’s University in Glasgow. One of these papers suggested that variations in the orbit of the earth caused ice ages to come and go. the calcu315

xviii+598_Biodiversity_F.indd 315

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316 ice ages  316 in temperature that characterize the coming and going of ice ages. But these slight changes in temperature set in motion a cascade of effects that amplify glaciation and then amplify the melting of glaciers. As snow begins to accumulate in the north, more sunlight is reflected back into outer space (albedo), which creates even colder conditions, speeding up glaciation. Cooler temperatures also reduce the decomposition of dead biomass, reducing the greenhouse effect. Once the glaciers begin to melt, both albedo and greenhouse effect amplify the onset of the interglacial period. The most recent maximum glacial extent ended about 14,000 years ago. The Arctic Ocean was relatively ice-free during the glaciations and was the source of evaporated water for much of the snow that caused them. Extensive glaciations did not occur in the Southern Hemisphere, because it contains mostly ocean, which does not change temperature as readily as land. Glaciers covered and still cover Antarctica, but there is very little land surface between Antarctica and the tip of South America. Therefore Antarctica produced, and produces, separate icebergs rather than advancing glaciers. The Milankovi´c cycle explains why cyclical glaciations occur today but does not explain why they did not occur prior to the Pleistocene. The land that is now North and South America had not been connected since the breakup of Pangaea during the Mesozoic era. A gap of ocean between them allowed a vast worldwide circulation of ocean water to flow into the Atlantic Ocean, forcing warm water into the Arctic Ocean. Water holds more heat than air, and this movement of heat from Tropics to the Arctic caused temperatures to be sufficiently warm that trees grew right up to the North Pole, even though they were in darkness half of the year. However, the Isthmus of Panama gradually arose, first as islands that slowed the flow of water, then as a land bridge that stopped it. Today, the Gulf Stream carries warm Caribbean water to the North Atlantic, causing the climate of Europe to be much warmer than the land at the same latitudes in North America (compare Labrador and England, for example). But the Gulf Stream is not big enough to warm up the Arctic Ocean. The planetary movements that produce the Milankovi´c cycle occurred long before the Pleistocene, but until then they had not produced cyclical glaciations. As the glaciers advanced, they pushed piles of rubble ahead of them. These piles, after the glaciers began to retreat, formed moraines. Some moraines have resulted in major geographical landmarks, such as Long Island and Cape Cod. Glaciers tore large chunks of rock from some mountains, while going around others. The isolated mountains that rose

xviii+598_Biodiversity_F.indd 316

first entry above the sheet of ice were called nunataks. Sometimes whole mountain systems, such as the Black Hills of South Dakota, remained above the glaciers. The temperatures were sufficiently cold and dry that very few organisms survived on nunataks. Glaciations during the Quaternary ice ages influenced the climate of North America very severely. Most of the same vegetation zones that exist today were present during the glaciation, including tropical rain forests, seasonal forests, and savannas. However, because the glaciers came so far southward, the northern vegetation zones were thinner and compressed toward the equator (see figure on page 317). The tropical areas, though slightly cooler, were still warm. However, since so much of the water was removed from meteorological circulation and stored in glaciers, the global climate was drier. In the dry tropical regions, deserts and grasslands were extensive, while tropical forests consisted of isolated groves. Because so much water was frozen in the glaciers, sea level was almost 300 feet (100 m) lower than it is today. Much of the continental shelf, which today is under shallow water, was dry land. Some “fishing banks” of shallow water in the oceans were exposed islands or peninsulas during the most recent glaciation. Some plant communities that have no counterpart today, such as spruce savannas, existed during the glaciation. The most recent glacial retreat began about 12,000 years ago. Retreat was generally faster than advance, sometimes as much as 30 feet (10 m) a year. Therefore a person would readily notice the retreat of glaciers during a lifetime, and there were modern humans in both Eurasia and in North America to observe this. The return of water to the meteorological cycle resulted in a wetter climate in tropical regions, in some regions even wetter than today. What is now the Sahara Desert, about 9,000 years ago had extensive grasslands and herds of wild animals, which human tribes observed, carving images of them on rocks. The vast amounts of water from melting glaciers had to go somewhere. Many rivers were much larger during the time of glacial melt than they are today. For example, the bluffs along the Missouri River, formed from fine soil blown from land newly exposed by the retreating glaciers, are today more than two miles (over three kilometers) from the current banks of the river, implying that the river was about four miles (seven kilometers) wider as the glaciers were melting upstream. Vast lakes, such as Lake Agassiz in North America, formed from the meltwater. Although the Great Lakes are among the largest lakes in the world and contain about a fifth of the planet’s freshwater, they are much smaller than Lake Agassiz, of which they are remnants. In

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ice ages

317

North American vegetation zones during the most recent ice age

some cases, ice blocked the drainage of the lakes, and when the ice gave way, massive floods occurred downstream. this occurred with lake agassiz and produced a flood of water down the St. lawrence River. So much freshwater drained during this flood that it altered the climate of the entire region for a few hundred years. Since freshwater is lighter than salt water, this cold water remained at the surface of the north atlantic and caused a temporary reversal of the warming trend that had been occurring. a similar flood, in western north america, produced huge ripples and other deposits known as the Scablands. Within about 5,000 years (by 7,000 years before the present), the warming trend had reached a max-

xviii+598_Biodiversity_F.indd 317

imum, known as the hypsithermal. at this time, grasslands covered much of the land that is today forested in north america. this included a new kind of grassland, the tallgrass prairie, consisting of large deep-rooted grasses that grow mostly during warm summers. as conditions began to change once again, leading the northern Hemisphere toward the next ice age, cool moist conditions returned to the north and the forests advanced southward. the tallgrass prairie, however, persisted in regions with a climate capable of supporting trees, because the accumulation of dead grass encouraged fi res. the fi res kill tree seedlings but merely create fertilizer for the grasses and wildflowers that resprout from underground stems and roots.

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318 insects  318 The ice ages continue. During the last glaciation, 30 percent of North America was covered with ice. But 10 percent of it still is and another 14 percent has permafrost, which is a permanent layer of ice beneath the soil. If past conditions occur again, another ice age is on the way. However, the greenhouse effect is causing the opposite trend to occur; glaciers and sea ice in North America, as well as Antarctica, are becoming smaller and thinner. It would be very nice for human civilization if the greenhouse effect precisely balanced the return of the ice ages; however, global temperature is rising (largely due to human production of carbon dioxide) 10 times faster than it did even during the period of rapid glacial retreat. The greenhouse effect is causing much of the permafrost to melt, resulting in soil subsidence and the buckling of highways. The ice ages occurred rapidly enough that very little evolution resulted from them. For the most part, species of plants and animals have dispersed to new locations, rather than evolving into new species, as a result of any single ice age. Sometimes, plant species have gotten trapped in limited locations as they have moved northward. The alpine tundra, at the tops of ranges such as the Rocky, Cascade, and Olympic Mountains and the Sierra Nevada, came into existence when arctic tundra retreated to the tops of mountains rather than northward. Subalpine forests came into existence when boreal forests retreated up the slopes of mountains. Some individual species have gotten trapped in regions to which they may not be well adapted, resulting in a disjunct distribution pattern. One example is the Monterey cypress (Cupressus macrocarpa) of California. During the most recent ice age, it survived in Mexico. As this species dispersed northward during glacial retreat, it migrated westward and ended up confined to a small area near the Monterey Peninsula of California. Had it turned eastward rather than westward, it might have found a much more extensive region in which to live. In some cases, plant species dispersed northward after the last ice age more quickly than can be easily explained by the movements of their seeds. In Europe, the oak Quercus robur can spread rapidly, as jays carry their seeds, but Q. petraea seeds spread much more slowly. Recent research suggests that Q. petraea spread northward not by its seeds but by its pollen. The two oak species can cross-pollinate. Q. robur spread quickly northward as birds carried its seeds, and the wind carried pollen of Q. petraea northward. This pollen fertilized Q. robur individuals once they had matured. The resulting hybrid seeds grew into male-sterile trees, which produced only female flowers. When the hybrid trees matured, they too were pollinated by Q. petraea pol-

xviii+598_Biodiversity_F.indd 318

first entry len, and some of the offspring were completely fertile Q. petraea trees. In this way, Q. petraea dispersed northward at the rapid pace of their windborne pollen, not the slow pace of their acorns. Many extinctions (the Pleistocene extinction) occurred at the end of the last glaciation, far more than at the ends of previous ice ages. In many cases, trees were left without the animals that had previously dispersed their seeds. In some cases, the overall climatic changes of the Pleistocene may have affected evolution, even if the individual glaciations did not. One example has direct relevance to humans. On at least two occasions starting about 5 million years ago, the spread of drier conditions across Africa caused forests to retreat and savannas to spread. These cycles of aridity may have been important stimuli in the evolution of the human lineage. A drying trend in Africa about 5 million years ago may have been an important stimulus in causing australopithecines to evolve the ability to walk on two legs, even though recent evidence indicates that human ancestors still lived in forests even after becoming bipedal. Another drying trend over a million years ago may have stimulated the earliest members of the genus Homo to make tools, eat more meat, and evolve larger brains. Evolutionary shifts in other African mammals, such as antelope, occurred at about the same times. In Europe, during the ice age prior to the most recent, Neanderthals (Homo neanderthalensis) were the only humans. Modern humans (H. sapiens) migrated into Europe and displaced the Neanderthals during the interglacial period. The Neanderthals were extinct by the time the most recent glaciation reached its maximum. See also biogeography; boreal and subalpine forests; disjunct species; greenhouse effect; Pleistocene extinction; tundra. Further Reading Colinvaux, Paul. Amazon Expeditions: My Quest for the Ice Age Equator. New Haven, Conn.: Yale University Press, 2008. Macdougall, Doug. Frozen Earth: The Once and Future Story of Ice Ages. Berkeley: University of California Press, 2006. Petit, Rémy J., et al. “Hybridization as a mechanism of invasion in oaks.” New Phytologist 161 (2003): 151–164. Pielou, E. C. After the Ice Age: The Return of Life to Glaciated North America. Chicago: University of Chicago Press, 1992.

insects  Insects are arthropods with six legs and three body parts. Like other arthropods, they have an external skeleton (exoskeleton) and jointed legs.

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insects  319 This structure is unstable at large body sizes, therefore all arthropods including insects are relatively small. While crustaceans live only in moist environments, most species of arachnids and insects are fully terrestrial for at least part of their life cycle.

Insects are by far the most numerous and diverse arthropods. The world as we know it could not function without its million or more species of insects (see table). At any given moment, there are a billion billion (1018) insects on this planet. As herbivores,

Estimated Number of Species in Each Insect Order Order

Common name

Lower estimate of number of species

Apterygotes Collembola

Springtails

6,000

Diplura

Bristletails

800

Protura

Proturans

500

Thysanura

Silverfish

840

Exopterygotes Anopleura

Lice

3,100

Dermaptera

Earwigs

1,200

Dictyoptera

Mantids, roaches

6,000

Embioptera

Web spinners

Ephemeroptera

Mayflies

Hemiptera*

Bugs

Isoptera

Termites

2,400

Grylloblattodea

Icebugs

25

Odonata

Dragonflies

Orthoptera

Grasshoppers

Phasmida

Stick insects

2,700

Plecoptera

Stoneflies

2,000

Pscocoptera

Barklice

2,000

Thysanoptera

Thrips

5,000

Zoraptera

Zorapterans

300 2,000 80,000

5,300 20,000

30

Endopterygotes Coleoptera

Beetles

360,000

Diptera

Flies, mosquitoes

130,000

Hymenoptera

Ants, bees, wasps

130,000

Lepidoptera

Butterflies, moths

150,000

Mecoptera

Scorpionflies

Neuroptera

Lacewings

5,400

Siphonaptera

Fleas

2,380

Strepsiptera

Stylops

Trichoptera

Caddisflies

Approximate total (lower estimate)

500

370 7,000 919,000

*Includes Homoptera

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320 insects  320 carnivores, pollinators, and decomposers, they play a greater role in the flow of energy and matter through the Earth’s ecosystem than any other group. About 800 species of insects have become pests of agricultural crops; on the other hand, one-third of all commercial crops depend on bees for pollination. Flight has allowed insects to evolve many different pollination relationships with plants; the evolution of pollination relationships may have been the most important factor contributing to the evolution of insect diversity.

Structure and Function of Insects Insects have an open circulatory system, in which the blood bathes all of the internal organs inside of the exoskeleton. Most of the blood is watery hemolymph, with some blood cells. The blood cells do not have hemoglobin, therefore the circulatory system does not carry oxygen through the body. Insects have a single blood vessel, open at both ends. In it, a heart pumps blood along the dorsal (back or upper) side of the body toward the head. Oxygen is delivered to all parts of the insect body not by the blood but by a series of air tubes called tracheae. Air enters the tracheae through openings (spiracles) in the thorax and abdomen. Muscular activity during movement helps to squeeze fresh air in and out of the insect’s body. In aquatic stages of the life cycle, outgrowths of the tracheal system form gills that absorb oxygen from surrounding water. Insects may also store air bubbles inside or outside of their body. These bubbles serve two functions: first, they allow terrestrial insects to take an air supply with them underwater; secondly, they allow insects that live in dry environments to store an air supply without opening their spiracles, through which they could lose water vapor, very often. Insects have appendages, which are legs or modified legs. Evolution modified the functions of these appendages into specific and diverse forms, such as antennae and mandibles. The evidence for this is genetic. Certain mutations cause appendages to develop into the wrong kind of appendage; for example, the antennapedia mutation of flies causes legs to develop where antennae are supposed to be. Insects have three body parts, each composed of several segments, as follows: The head. An insect head has appendages such as antennae and mandibles. The antennae (which may have many segments) have a sensory function, often by reacting to the presence of specific molecules such as sex pheromones. The mandibles manipulate and process food items. Therefore insect mandibles (modified from legs) have an entirely different developmental origin from vertebrate jaws (modified from gill arches of fishes). Mandibles may

xviii+598_Biodiversity_F.indd 320

first entry chew or (if modified into a long proboscis) suck nectar from a flower or juices from plant and animal tissues. The head also has a pair of compound eyes, which consist of a large number of small lenses or ommatidia (4,000 in the case of the house fly) (see photograph on page 321). Each lens registers a pixel of light intensity and color. Compound eyes do not produce a sharp image but are good at detecting movement. Between the compound eyes there are usually three ocelli, or single-lensed eyes. The thorax. The thorax, which is the middle part of the body, contains three pairs of legs. Each leg has six segments: The coxa anchors the leg to the thorax; the trochanter is a swivel joint where the leg attaches; the femur, tibia, tarsus, and pretarsus make up the long portion of the leg. Most insects have one or two pairs of wings. In some insect lineages, wings did not evolve; other lineages, such as fleas, lost their wings during evolution. The thorax contains a lot of muscles. The abdomen. The abdomen contains the heart, digestive system, and reproductive system. The evolution of wings, unique among arthropods, is one of the insects’ most important terrestrial adaptations. Wings allow some insects to travel at great speeds. The sphinx moth can fly at 1,000 body lengths per second. A jet flying at three times the speed of sound travels only 100 body lengths per second. In addition to speed, wings allow insects to have tremendous maneuverability. The earliest insects lived on land during the Devonian period. Insects remained rare until the Carboniferous period. The earliest insects ate detritus, pollen, or spores; they did not eat leaves until very much later, perhaps as late as the Jurassic period. This is one reason that plant material from Carboniferous swamps built up into large coal deposits: insects did not defoliate them before they died. Insect flight evolved during the Carboniferous period, particularly the large dragonflies. Meganeura monyi had a wingspan of over two feet (75 cm). Such a wingspan seems too large to have allowed flight, and the insect system of respiration through spiracles seems incapable of providing enough oxygen to such a large organism. Some scientists speculate that the atmosphere contained more oxygen at that time, which made respiration easier and also made the atmosphere thicker. As a result, the large dragonflies would have moved their wings slowly, mostly gliding through the thick air. By the Devonian period, other modern insect groups such as orthopterans, coleopterans (beetles), and hemipterans (bugs) had evolved. Numerous orders of insects died during the Permian extinction, but surviving orders (especially flies and beetles) proliferated during the Mesozoic era. By the Cretaceous

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insects  321

Insects, such as this Condylostylus fly, have compound eyes.  (Thomas Shahan)

period, insect life consisted mostly of the orders that dominate the world today. Most modern insects are either amphibious (living first in the water then on land) or entirely terrestrial. The first insects lived partly or wholly on land; a few modern insects have returned to an entirely aquatic existence. Insects undergo metamorphosis, from juvenile to adult, by passing through a series of molts or instars. Some insects such as grasshoppers have relatively small changes during metamorphosis, in which the juvenile insect (nymph) that hatches from the egg closely resembles the adult (hemimetabolous development). Wings usually develop only on the final instar. Other insects undergo complete metamorphosis. They have a larval stage that looks almost completely different from the adult, as “grubs” bear little resemblance to adult beetles or bees, nor caterpillars to butterflies (holometabolous development). The larvae are almost always adapted as “eating machines,” while the adults (which devote themselves to reproduction) eat much less, if anything at all. In amphibious insects, such as the dragonfly, the juvenile stage lives underwater, but the adult lives on land and in the air.

Overview of Insect Diversity The three major lineages of the insects are as follows: (1) The Apterygota are wingless and have not had wings during their evolutionary history. This group includes the springtails (collembolans) and silverfish (thysanurans). They have long antennae that curve backward and long abdomens that end in three bristles. Most of them live in the soil, although some silverfish live in books, which resemble leaf litter. (2) The Exopterygota have hemimetabolous development and wings that develop on the outside of the body. (3) The Endopterygota have holome-

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tabolous development and wings that develop inside of the body. Some scientists classify the Apterygota separately from the insects. The exopterygotes, whose nymphs resemble the adults, include the following: Order Ephemeroptera. The mayflies are the oldest group of winged insects still in existence. They are common in freshwater worldwide. The larvae live underwater, usually eating algae or detritus, for up to two years. They breathe through abdominal gills. After undergoing many instar molts, the mayfly emerges into the atmosphere during its second to last molt. Mayflies are the only insects to have wings before the final molt. They then land on a surface to undergo their final molt. Males swarm over water and females choose males, mate with them, and lay eggs. They are called Ephemeroptera because the adults live very brief (ephemeral) lives. Order Odonata. The dragonflies and damselflies have two pairs of membranous wings. Dragonflies hold their wings horizontally, and damselflies hold them vertically. Unlike other insects, dragonflies and damselflies can move the front and back wings independently of one another. This allows them to have tremendous maneuverability. Because the wings are so large, they can beat only one-tenth as fast as those of bees. Though they have very small antennae, they have very large eyes, each with as many as 30,000 ommatidia. Odonates were among the first flying insects, as noted previously. Dragonflies and damselflies are unique among insects in that the male inseminates the female with a secondary sexual apparatus; before mating, he must transfer sperm to this apparatus from his primary sexual apparatus. Nymphs are aquatic and adults terrestrial. They are predators, and the nymphs can be cannibalistic. Order Orthoptera. The grasshoppers and crickets are easily recognized by enlarged back legs, used primarily for jumping. Grasshoppers have short antennae, while crickets have long antennae. They have chewing mouthparts. Grasshoppers are primarily herbivores, while crickets are omnivorous; a few orthopterans are predatory. They are renowned for the sounds that they produce. Crickets rub their left and right front wings together, while grasshoppers rub their upper hind legs against their front wings. Some orthopterans produce sounds by rubbing their mandibles together or by drumming their legs against wood. Order Phasmida. The stick and leaf insects are either elongated, resembling sticks, or flattened, resembling leaves. They are spectacular examples of mimicry, some species having a remarkable resemblance to their models and all of them a close enough resemblance to fool most predators. Often, they are

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322 insects  322 also animal mimics. Females of Extatosoma tiaratum lay eggs in ant nests. The eggs have a protuberance that the ants like to eat. The ants carry the eggs inside the nests, eat the protuberance, and throw the eggs into the garbage pile. Being in the ant garbage pile protects the eggs from other predators. Order Dictyoptera. This order consists of the mantids and cockroaches. The mantids (such as the praying mantis) have enlarged front legs which they keep against their bodies as they sit still for long periods of time (reminding some observers of prayer). When a prey animal comes within reach (usually a smaller arthropod, though sometimes small vertebrates) the mantids quickly extend their legs and catch the prey with the bristles on the legs and voraciously consume it. In some mantid species, the female eats the male during copulation; even with his head removed, the male can copulate. It is not clear whether this is or is not simply a mistake on the part of the female, who may attack almost any small animal within reach. Roaches are flat, with hind wings hidden underneath strong forewings, and their shape allows them to seek out and fit into crevices (natural or human). Less than 1 percent of cockroach species inhabit buildings and are human pests. They are not disease vectors the way fleas and mosquitoes are, although they may carry germs with them from inaccessible and uncleaned areas in a building. Order Isoptera. Termites are renowned for their societies. They live in groups of up to a million individuals, often in large mounds which can be up to 24 feet (8 m) tall, the temperature conditions of which they can control (see photograph). The less specialized termites eat wood, much of which is inside of human buildings, causing a great deal of economic damage. More specialized termites eat other types of food as well, including leaves, seeds, and lichens, much of it (like wood) containing cellulose. Termites cannot digest wood. They depend upon mutualistic microorganisms living within their digestive systems to perform this task: protists in the less specialized termites and anaerobic bacteria in the more specialized termites. Some of them (like leaf-cutter ants, to which they are not closely related) raise and eat gardens of fungus inside their mounds. All of the reproduction is carried out by a primary female (“queen”) and primary male (“king”), whose hormones suppress reproduction in all the other termites in the mound. The queen becomes an egglaying machine, with a grossly distended abdomen, laying an egg every three seconds—tens of millions over her lifetime. The queen does not eat wood but is fed by the saliva of the workers. Sterile soldiers defend the nest in several ways, depending on the species. Some soldiers have huge heads and man-

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Termites produce large mounds in tropical areas. This mound in Litchfield National Park, Northern Territory, Australia, is about 16 feet (5 m) tall and may be more than 50 years old. The termites live underground; the aboveground mound is a complex chamber in which fungi partially decompose the grass that the Nasutitermes triodiae termites eat.  (J. Brew)

dibles for attacking intruders; other soldiers spit toxic solutions; others have large heads with which they block the entrances to the nest when it is under attack. Termites are so abundant that the methane produced by their colonies makes a measurable contribution to the global carbon cycle. Most termites are wingless, but winged reproductive individuals can swarm to new locations. Upon arrival, they shed their wings. Order Anopleura. Lice are wingless and horizontally flattened parasites of vertebrates, allowing them to lie very close to the skin of the host. Their flatness makes them difficult to remove by scratching or preening. The lice are divided into two groups. The Mallophaga (biting lice) mostly consume skin and feather fragments (and occasionally blood) of birds. The Siphunculata (sucking lice) suck blood from mammals. Two louse species live only on humans: the pubic louse and the body louse (with separate subspecies that live on the head or on the trunk of the body). Order Hemiptera. The true bugs are insects that have pairs of sucking mandibles. Most of them

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insects  323 consume plant fluids (thus often causing economic loss), although some are predatory. Examples include the shield bugs (or stink bugs) with a large shield over the back of the thorax; the water striders, which can walk upon the surface tension of water; the cicadas; and the aphids. ●●

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Cicada nymphs (within order Hemiptera) feed on plant roots; the adults emerge from the ground and produce sounds from tree branches by buckling special membranes on the foremost abdominal segment. The adults reproduce and die. Periodical cicadas emerge en masse every 13 or 17 years. When they emerge, there are too many of them for predators to deplete their populations, and the predator life cycles cannot easily adjust to those of their cicada prey, which emerge on a prime-number schedule. Aphids (within order Hemiptera) are tiny, soft-bodied bugs that insert a proboscis into plant phloem cells, from which they drink sap. Phloem sap is pressurized, therefore aphids do not need to suck or even swallow. The sugary fluid passes through them too fast for efficient digestion; objects underneath a tree infested with aphids become sticky with slightly-altered plant sap called honeydew. Aphids can withdraw so much sap from a plant that it dies. Aphids can also transmit plant diseases (often viruses) by the proboscis. Less than 10 percent of aphid species are agricultural pests. The sap that aphids consume contains little nitrogen. Aphids obtain the nitrogen that they need (such as amino acids) by processing a large amount of sap and from the mutualistic metabolism of bacteria (often genus Buchnera) within their digestive systems. Large aphid populations may consist only of females that reproduce asexually by laying unfertilized eggs, but toward the end of the season sexual forms develop and mate. During their rapid population growth phase, female aphids have live birth, and the little aphids already have eggs developing into embryos inside of them. Many aphids have a mutualistic association with ants, in which the ants live largely or exclusively from honeydew, and the aphids depend upon the ants to transport and protect them. This mutualism has evolved independently many times.

In some schemes of classification, bugs such as cicadas and aphids are placed in their own order, the Homoptera.

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The endopterygotes, which have a larval stage that pupates, include the following: Order Siphonaptera. Adult fleas suck the blood of birds and mammals. The larvae eat detritus from the bodies or nests of their hosts. Among the adaptations that make them successful parasites are the following: ●●

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Fleas are laterally flattened, making them very difficult to remove by scratching or preening. Fleas have strong legs that allow them to escape danger and to leap from one host to another, up to 150 times their body length or 80 times their height. Fleas have backward-pointing bristles that enhance their ability to escape from other animals. Fleas release an anticoagulant when they bite, which not only keeps the blood flowing but also causes the itchy irritation. Fleas respond to the hormones in the blood, allowing them to synchronize their reproduction with that of the host. In this way, a new generation of fleas can infest a new generation of baby mammals or birds.

Fleas are vectors of disease, the most famous of which is the bubonic plague, which has caused numerous plagues including the Black Death in Europe in 1345–47. Bubonic plague is spread by rat fleas, Xenopsylla cheopsis, which carry the plague bacteria from rats to humans, and not by the human flea Pulex irritans. The Black Death, as well as other plagues, has changed the course of human history. Order Diptera  Most flying insects have four wings, but flies and mosquitoes have just two—the front pair. “Diptera” is Greek for “two wings.” The hind pair of wings develops into balancing devices, known as halteres, which greatly enhance their maneuverability. The two main groups of dipterans are the Nematocera (mosquitoes and relatives) and the Brachycera (flies and relatives). Mosquito larvae are the aquatic “wrigglers” with complete heads and mouth bristles, but no legs. They eat smaller algae and bacteria, often in the surface film of still water. Their pupae float, and adult mosquitoes emerge from them into the air. Craneflies look like large mosquitoes. Their larvae consume decaying vegetation in moist soil. Adult mosquitoes and craneflies may not eat or may consume only nectar. Female mosquitoes need a blood meal to provide protein and iron for egg development. The saliva of the female mosquito contains compounds that prevent blood clotting, promote blood flow, and inhibit host immune response. ­Mosquito bites

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324 insects  324 transmit many diseases, such as yellow fever, dengue fever, and viral encephalitis. They do not transmit HIV (the virus that causes AIDS). One of the most common and most severe diseases in the world, malaria, spreads through mosquito bites, mostly by the genus Anopheles. Fly larvae are maggots, with few distinguishable external features, that (depending on the species) live in decaying flesh, fruit, dung, and occasionally in living flesh (as with bot flies in cattle). Adult flies have very large compound eyes. Although there are many thousands of species of flies, one species (Musca domestica, the house fly) has followed humans throughout the world. Adult flies may feed on many different kinds of fermenting liquid food. Adult fruit flies and vinegar flies are attracted to ripe or decaying fruit, as well as to wine. Because their mouthparts form a tube, adult flies cannot ingest solid food. Often their saliva helps to soften the food before they ingest it. Because the adults often visit vertebrate feces, house flies can spread many of the same diseases that otherwise spread by sewage contamination of water and food. Flies, however, almost continually scrape contaminants from their body surfaces. Order Lepidoptera.  Butterfly and moth caterpillars are eating machines, usually consuming large amounts of leaf material, much of it toxic, from which they extract the little bit of nutrition that is available and produce a lot of waste. In most species, with exceptions such as the gypsy moth (Lymantria dispar), the caterpillars eat only one species of plant. In some cases, the species may be flexible, but the individual caterpillars are not. Hornworms (the caterpillars of the sphinx moth or hawkmoth, Manduca sexta) can feed on many different species within the plant family Solanaceae (including tobacco, tomatoes, and jimsonweed) but a caterpillar will reject leaves from all solanaceous species except the one which it first ate. Many caterpillars may eat other insects if they are small enough and are encountered by chance. A carnivorous caterpillar (genus Eupithecia) has evolved in Hawaii. Some moth caterpillars may eat fungi, decaying material, or even feces. Explosions of caterpillar populations may cause severe damage to crops or wild plants; the gypsy moth caterpillar defoliates large acreages of trees in the northeastern United States each summer. Insects have six legs, but caterpillars appear to have more. The only true jointed legs are the six toward the front of the caterpillar; the others are prolegs that are not jointed but end in bristly pads that help them clasp to stems and leaves. Once it has completed its feeding, the caterpillar transforms into a pupa. In moths, the pupa forms a cocoon of silk. In butterflies, the pupa is a chrysa-

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first entry lis with exoskeleton plates. The pupating caterpillar of the sphinx moth (hawkmoth) (Manduca sexta) forms a tube inside of which the adult tongue will develop. Inside the protected chrysalis or cocoon, the pupa undergoes a striking metamorphosis. Caterpillars have “buds” of cells that they do not use but that become active during metamorphosis. Enzymes digest much of the caterpillar’s body from the inside, and the buds form new structures (such as wings). The metamorphosis includes the exchange of chewing mandibles for a long tongue. Pupae are usually immobile, although sphinx moth caterpillars can wriggle if disturbed. It is perhaps this stage of the life of a butterfly or moth that has most fascinated humans, to whom it appears to be a death and rebirth. The adults emerge with four wings covered with scales, some of which refract light into different iridescent colors. Most of them insert their long tongues, like coiled ropes, into long-tubed flowers to drink nectar. Some adult moths do not eat anything. A few will consume animal materials: Lobocraspis griseifusa drinks tears of large mammals, Ophiusa tirhaca pierces the skin of fruits, and Calyptra minuticornis actually pierces the skin of animals to drink blood. The tongue may be longer than the body of the butterfly or moth itself. Butterflies often have delicate wings, while moths have more rigid wings. Sphinx moths beat their rigid wings rapidly and can be mistaken for hummingbirds by casual observers. The antennae (feathery in the case of moths) detect pheromones (aerially dispersed sex hormones) which allow males to find females. Butterflies are usually colorful and active during the day, while moths are often dull in color and nocturnal, although there are many exceptions, such as the luna moth (see photograph on page 325). Coleopterans.  With more than 360,000 recognized species, the beetles are the largest order of insects and perhaps the most diverse group of animals in the world. About one in four species of animals is a beetle. Someone once asked the famous British biologist J. B. S. Haldane what he learned about God from his studies of nature. He answered that God must be “inordinately fond of beetles.” “Coleoptera” means “sheath-winged” because the first pair of wings in the adult form a sheath (the elytra) that covers the flying wings; beetles raise their elytrae when they fly. Their species diversity is matched by their diversity of size: Titanus giganteus (South American long-horned beetle) is the largest, at over six inches (16 cm) in length and a fungus beetle Nanosella fungi may be the smallest insect, at one-hundredth of an inch (0.25 mm). The adults have chewing mouthparts. Some beetles eat plant materials and may be pests of human crops and food. Both the larvae and

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insects  325

Many butterflies and moths, such as this luna moth in Arkansas (Actias luna), have colorful wings.  (Rutgers University)

adults of the Colorado potato beetle (Leptinotarsa decemlineata) feed on potatoes and related crops. Weevils (family Curculionidae) destroy crops and stored foods. But beetles play essential ecological roles. Many are pollinators of flowers and may have pollinated the earliest flowers. Some beetles make a living from the decomposition of vertebrates or their dung. Dung beetle (scarab beetle) adults may live in or bury dung or roll spheres of dung with their hind legs. They lay eggs in the dung, and the grubs develop there. Burying beetles (genus Nicophorus) find a vertebrate corpse, remove the hair or feathers, cover it with secretions that inhibit decomposition, and dig a crypt underneath it, eventually burying it. The female lays eggs near the carcass, and then they eat the carcass and feed regurgitated food to the grubs that hatch. Both larvae and adult ladybird beetles (family Coccinelidae) are predators upon other insects, especially aphids. “Lightning bugs” are actually beetles (family Lampyridae) that use light, produced by a very efficient enzymatic reaction that generates almost no heat, as mating signals. Hymenopterans. Ants, bees, and wasps have legless larvae that develop in cocoons. The adults have chewing mouthparts, sometimes modified for sucking, two pairs of membranous wings (Hymenop-

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tera comes from the Greek for “membrane-winged”), and a very narrow connection of the abdomen to the thorax. The narrow waist allows hymenopterans to bend their abdomens at an acute angle while laying eggs or stinging. Many species of bees and wasps are solitary, but many of them, as well as nearly all ants, form large societies (in some cases of 300 million individuals). In these societies, the females are diploid (have pairs of chromosomes) while the males are haploid (have unpaired chromosomes), a system known as haplodiploidy. Queen females lay all of the eggs; in the workers, the ovipositor (egg tube) develops into a stinger. Most hymenopteran females have the ability to sting. The bee’s stinger has barbs. The worker cannot remove its stinger from the flesh of an intruder. The worker bee dies after pulling free from the intruder. Each worker ant, having a barbless stinger, can sting an intruder several times. The haplodiploid system results in a high genetic relatedness among the workers, which in turn has allowed the evolution of altruism to the extent that workers may die in defense of the colony. When fire ants (Solenopsis invicta) attack intruders, many of them crawl onto the intruder and then synchronize their stinging attack.

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326 insects  326

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The ecological and economic importance of hymenopterans are almost impossible to overstate. Numerous species of wild bees pollinate flowers as they forage for sweet nectar and protein-rich pollen. One species, the European honeybee Apis mellifera, is overwhelmingly important to agriculture; according to one estimate, every third bite of food comes from plants that require bee pollination or comes from cattle whose alfalfa requires pollination. Parasite and disease outbreaks (and possibly pollutants) threaten honeybee populations, especially since the emergence of “colony collapse disorder” in 2007. Some scientists are seeking to cultivate wild bees, which are often more efficient at pollinating specific kinds of agricultural plants. Some wasps are also pollinators, especially of figs. Many wasps lay eggs in caterpillars, which the wasp grubs eat; wasps can therefore be an important biological control of agricultural pests. Ant burrows aerate soils.

Insects and Humans Insect populations are so massive that, next to bacteria and plants, they may be the major players in the ecosystems of the Earth. For example, one-third of the animal biomass of the Amazon rain forest consists of ants and termites. Many insects become pests when their populations get out of control. Massive use of pesticides has not only failed to control them but has resulted in the evolution of super-pests. Modern agricultural researchers now realize that the best, and only permanent, control of insect pests is to release diseases, predators, parasites to kill the pests, or release sterilized adults of the pest species, which mix with the pest population and reduce its reproductive success. In addition, if humans try to spray all of the insect pests, they will also kill the many insects that are not only beneficial but also essential, especially the pollinators. These are some of the reasons that integrated pest management is beginning to replace the heavy use of pesticides in many regions of the world. Insects may provide great medical benefits. Sometimes medicines are ineffective against infected wounds, but doctors can sometimes use maggots— yes, the larvae of flies—to clean out decaying flesh from a person’s wound, a process known as debridement. Furthermore, scientists have wondered why some insects such as ants can live in dense populations without having outbreaks of disease. It appears to be because these insects produce antibiotics that protect them, either directly or by encouraging the growth of beneficial microorganisms. In the continual search for new antibiotics, researchers may have to turn to the insects. Many people do not like insects, even those they will admit are good for the human economy. They

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need someone to popularize them. May Berenbaum, an entomologist at the University of Illinois, has done precisely this. She is famous not only for her research in the coevolution of insects and plants and for leading research into the causes of colony collapse disorder (the deaths of honeybee colonies), but also for her popular science books and for starting the Insect Fear Film Festival at the University of Illinois, an annual event for more than a quarter of a century. See also arthropods; integrated pest management; invasive species; mutualism; pollination. Further Reading Averof, Michalis, and Stephen M. Cohen. “Evolutionary origin of insect wings from ancestral gills.” Nature 385 (1997): 627–630. Bänziger, H. “Skin-piercing blood-sucking moths I: Ecological and ethological studies on Calpe eustrigata (Lepidoptera, Noctuidae).” Acta Tropica 32 (1975): 125–144. Berenbaum, May. Bugs in the System: Insects and Their Impact on Human Affairs. Upper Saddle River, N.J.: Addison-Wesley, 1996. ———. Buzzwords: A Scientist Muses on Sex, Bugs, and Rock ‘n’ Roll. Washington, D.C.: National Academies Press, 2000. ———. “Colony collapse disorder and pollinator decline.” Presented to Committee on Agriculture, U.S. House of Representatives, March 29, 2007.Available online. URL: http://www7.nationalacademies.org/ocga/testimony/ Colony_Collapse_Disorder_and_Pollinator_Decline. asp. Accessed August 10, 2011. ———. The Earwig’s Tail: A Modern Bestiary of MultiLegged Legends. Cambridge, Mass.: Harvard University Press, 2009. ———. Ninety-nine Gnats, Nits, and Nibblers. Urbana, Ill.: University of Illinois Press, 1989. Chernin, E. “Surgical maggots.” Southern Medical Journal 79 (1986): 1,143–1,145. Conner, William E., ed. Tiger Moths and Woolly Bears: Behavior, Ecology, and Evolution of the Arctidae. New York: Oxford University Press, 2008. Eisner, Thomas. For Love of Insects. Cambridge, Mass: Harvard University Press, 2003. Franks, N. R. “Army ants: a collective intelligence.” American Scientist 77 (1989): 139–145. Glausiusz, Josie. Buzz: The Intimate Bond Between Humans and Insects. San Francisco, Calif.: Chronicle Books, 2004. Grimaldi, David, and Michael S. Engel. Evolution of the Insects. New York: Cambridge University Press, 2005. Hölldobler, Bert, and Edward O. Wilson. The Ants. Cambridge, Mass: Harvard University Press, 1990.

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integrated pest management 327 Oldroyd, B. P. “What’s killing American honey bees?” Public Library of Science Biology 5 (2007): e168. Available online. URL: http://www.plosbiology.org/article/ info:doi/10.1371/journal.pbio.0050168. Accessed May 16, 2011. Ramel, Gordon. “The insect orders: An introduction to each of the 32 orders of insects.” Available online. URL: http://www.earthlife.net/insects/orders.html. Accessed May 16, 2011. Waldbauer, Gilbert. What Good Are Bugs: Insects in the Web of Life. Cambridge, Mass: Harvard University Press, 2003. White, Richard E. Beetles: A Field Guide to the Beetles of North America. A Peterson Field Guide. New York: Houghton Mifflin, 1998.

integrated pest management  (IPM)  Inte-

grated pest management (IPM) is a way of controlling pests, principally insects that damage crops and spread diseases, that recognizes the reality of ecology and evolution. It is a viewpoint about how to restrict the growth of pest populations rather than a detailed guide to doing so. The “conventional” view of pest control, promoted by large corporations that sell chemicals, is that large amounts of pesticides are the only effective way to control pests. In contrast, IPM (as its name suggests) integrates many different ways of controlling pests, including the use of pesticides. Here follow some of the guiding principles of integrated pest management: Zero pest population levels are unattainable. No matter how much a farmer may spray on a cotton field to control bollworms or how much a public health official may spray to control mosquitoes, there is no way to kill all of the pests. As the United States Environmental Protection Agency says, “Sighting a single pest does not always mean control is needed.” But it is possible to keep pest populations low enough that they do not cause significant damage to crops or to human health by using a combination of methods. Overuse of pesticides causes pest resurgence. The heavy use of pesticides can, in fact, greatly reduce pest populations. However, the pesticides also reduce the populations of the natural predators, either directly (as when the pesticides kill spiders or parasitic wasps) or indirectly (as when pesticides concentrate in the food chain and kill birds). All of the populations begin to recover after the use of the pesticide. The predator populations grow more slowly than the pest populations. Soon after the pesticide has either degraded or washed away into wetlands and soils, there is a population explosion of pests. In order to prevent this, IPM attempts to keep the wild predator populations intact.

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Overuse of pesticides in rice fields in Indonesia caused an outbreak of the brown plant hopper Nilaparvata lugens in 1974. The powerful central government decreed restrictions on pesticide use, and advertisements encouraged farmers to not kill spiders. Natural predators returned, including the beetles Harmonia octomaculata and Ophionea nigrofasciata and the parasitic insects Tetrastichus schoenobii, Telenomus rowani, and Cotesia angustibasis. Pesticides are still necessary and used, but at much lower levels than in 1974. Overuse of pesticides causes the evolution of resistant pests. Natural selection is inevitable in pest populations, just as in every other population. Pests have physiological mechanisms to either avoid or to detoxify pesticides. These mechanisms are the product of millions of years of natural selection that have given the animals the ability to avoid or resist natural toxins, especially those produced by plants, and they work just as well against synthetic toxins. An environment saturated with pesticides creates an ideal stage for the evolution of pest populations that are largely unaffected by the pesticide. “Natural” pesticides can become ineffective almost as easily as synthetic ones. The problems of pesticide overuse cannot be avoided by simply using natural compounds such as pyrethrin (produced by Chrysanthemum cinerariaefolium flowers, primarily grown in Kenya) or Bt (produced by Bacillus thuringiensis bacteria). These compounds are less toxic than most synthetic pesticides, but their overuse can cause resurgence and the evolution of resistant insects. Some pest insects have already evolved resistance to Bt, including the Bt produced in the leaves of genetically modified crop plants. Some harmless chemicals can be used for pest control.  One such chemical is soap. When soap is sprayed on aphid infestations, the aphid exoskeletons are disrupted, which kills them. Conventional pesticides, when mixed with soap, penetrate insects more effectively, which allows a reduced use of pesticides. Pests can be controlled by reducing host density. In a huge field of corn (a monoculture), every plant is a source of food for corn earworms. In smaller patches of corn, interspersed with patches of other crops such as soybeans, the corn earworm populations cannot grow as rapidly. Pest populations can be controlled in time as well as in space. Crop rotation reduces the growth of pest populations. If earworms infest a cornfield, they may hatch the next year and discover that the field is now a soybean field, and many of them will die. Pests can be controlled by encouraging predator populations. If agricultural fields are surrounded by fencerows of trees or shrubs, predatory insects or birds can live in them and fly out to capture pests

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328 integrated pest management 328 from the fields before returning to safety. It is important that the fields be small; predators will not fly long distances to the middle of a large field. The fencerow trees can also help to prevent wind and water erosion, an added benefit beyond pest management. Natural predators can be important to an agricultural economy. India banned frog exports in 1987 when the profits of selling them became less than the costs of pesticides to make up for insects the frogs ate. Pests can be controlled by manipulating their behavior.  Pest insects are not very smart and can be easily tricked; they often do whatever their airborne hormones (pheromones) tell them to do. Two important uses of synthetic pheromones in insect control are as follow: ●●

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Mass trapping.  Pheromone bait can attract insect pests to box traps. Millions of bark and other beetles have been trapped in this manner in the forests of northwestern North America. Pheromone bait has also been important in controlling codling moths (Cydia pomonella), whose caterpillars are a serious pest of apples and pears. It is estimated that pheromone traps killed 4.5 billion spruce bark beetles (Ips typographus) in Norway during a major infestation in 1980. Pheromone traps have also been used against the tomato pinworm, Keiferia lycopersicella, in Mexico. Mating disruption. A dilute suspension of pheromones, when sprayed in an agricultural field, can confuse male moths, and they cannot find the females.

Pheromones are effective at extremely low concentrations, and synthetic pheromones are not prohibitively expensive. The only way for pesticides to remain effective is to use them sparingly.  Most environmentalists, following the lead of Rachel Carson, did not oppose the frugal use of pesticides. In fact, this is the only way that the pesticides can remain effective: If the pesticides are rarely used, natural selection cannot favor the evolution of pest populations that resist them. No matter how carefully IPM is used, pest outbreaks will happen occasionally; for those times, pesticides are effective because IPM was practiced between pest outbreaks. Carson opposed the blanketing of the entire countryside with mirex, which was a pesticide intended to control invasive fire ants; instead, she called for the use of mirex by workers with backpack sprayers who could deliver the mirex directly to the ant mounds. The mirex concentration on the mound would be high, but the countryside as a whole would have a relatively low concentra-

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first entry tion. DDT, a pesticide notorious for accumulating in the food chain, is used safely in Africa to control mosquitoes that spread malaria, because it is used just around houses (direct human contact with small amounts of it is not harmful) and because the inhabitants of the houses also use mosquito nets when they sleep. IPM is complex. It is not as simple as spraying. It requires the simultaneous use of many different techniques and an understanding of biology. It requires that a farmer think of a farm as an ecological community. It requires that the public health official think of nonchemical ways to prevent the growth of mosquito populations. For example, old junk left out in the open can accumulate pools of water that are perfect breeding places for mosquitoes. That is, there is a connection between the cleanup of old junk and the spread of diseases such as the West Nile virus. However, the scientific principles are not difficult to understand, and many of them are simply common sense. The principles of IPM are not too difficult to implement in any situation. Many insect pests have been imported without their natural parasites or predators. It is tempting to think about importing their parasites or predators as biological control agents. This has worked in the past. The cottony cushion scale Icerya purchasi, from Australia, became a citrus pest in California in the early 20th century. It was brought under control by the vidalia beetle Rodolia cardinalis, also imported from Australia. There are, however, other not so successful examples of invasive species that were introduced for the purpose of biological control of another invasive species, and this practice is now uncommon. IPM does not have a perfect record of success. Its success, however, is comparable to that of reliance on pesticides. Agricultural scientist Matthew Thomas indicates that many IPM programs have been ineffective because they were not integrated enough: They depended too heavily on just one component, usually the chemical one. He wrote, “the single solution, ‘magic bullet’ approach has undermined our basic understanding of how individual components actually work and has oriented IPM toward quick fixes, often underpinned by commercial incentives.” Rare species are particularly vulnerable to the overuse of pesticides. A pesticide application that will decimate the populations of common predatory insects and birds only temporarily and of pest insects even more briefly can eradicate a rare species. IPM is therefore not just a good idea for agriculture and for the control of disease but an essential component of protecting biodiversity. See also biomagnification; Carson, Rachel; invasive species; resistance, evolution of.

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invasive species  329 Further Reading Bianchi, F., et al. “Sustainable pest regulation in agricultural landscapes: A review on landscape composition, biodiversity, and natural pest control.” Proceedings of the Royal Society of London B (Biology) 273 (2006): 1,715–1,727. Bloomers, L. H. M. “Integrated pest management in European apple orchards.” Annual Review of Entomology 39 (1994): 213–241. Cardé, R. T., and A. K. Minks. “Control of moth pests by mating disruption.” Annual Review of Entomology 40 (1995): 559–585. Cuyno, Leah C. M., et al. “Economic analysis of environmental benefits of integrated pest management: A Philippine case study.” Agricultural Economics 25 (2005): 227–233. Donald, P. F., et al. “Agricultural intensification and the collapse of Europe’s farmland bird populations.” Proceedings of the Royal Society of London B (Biology) 268 (2001): 25–29. Environmental Protection Agency. “Integrated pest management (IPM) principles.” Available online. URL: http://www.epa.gov/pesticides/factsheets/ipm.htm. Accessed August 8, 2011. Flint, Hollis M., and Charles C. Doane. “Understanding semiochemicals with emphasis on insect sex pheromones in integrated pest management programs.” Available online. URL: http://ipmworld.umn.edu/ chapters/flint.htm. Accessed August 2, 2010. Hendrix, P. F., et al. “Detritus food webs in conventional and no-tillage agroecosystems.” BioScience 36 (1986): 374–380. Holt, J., et al. “Strategies of insecticide use to avoid resurgence of Nilaparvata lugens (Homoptera: Delphacidae) in tropical rice: A simulation analysis.” Journal of Economic Entomology 85 (1992): 1,979–1,989. Johnson, David R., et al. “Controlling weeds with phytopathogenic bacteria.” Weed Technology 10 (1996): 621–624. Liu, Tong-Xian, and Philip A. Stansly. “Insecticidal activity of surfactants and oils against silverleaf whitefly (Bemisia argentifolii) nymphs (Homoptera: Aleyrodidae) on collards and tomato.” Pest Management Science 56 (2000): 861–866. Nyffeler, M., and K. D. Sutherland. “Composition, abundance, and pest control potential of spider communities in agroecosystems: A comparison of European and US studies.” Agriculture Ecosystems and Environment 95 (2003): 579–612. Ogol, C., et al. “Maize stem borer colonization, establishment, and crop damage levels in a maize-leucaena agroforestry system in Kenya.” Agriculture Ecosystems and Environment 76 (1999): 1–15. Paoletti, Maurizio G., and David Pimentel. “Environmental risks of pesticides vs. genetic engineering for agricultural pest control.” Journal of Agricultural and Environmental Ethics 12 (2000): 279–303.

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Perfecto, Ivette, and R. Snelling. “Biodiversity and the transformation of a tropical agroecosystem—ants in coffee plantations.” Ecological Applications 5 (1995): 1,084–1,097. Pollard, K. A., and J. M. Holland. “Arthropods within the woody elements of hedgerows and their distribution pattern.” Agricultural and Forest Entomology 8 (2006): 203–211. Richards, A. J. “Does low biodiversity resulting from modern agricultural practice affect crop pollination and yield?” Annals of Botany 88 (2001): 165–172. Rutledge, Claire E., et al. “Soybean aphid predators and their use in integrated pest management.” Annals of the Entomological Society of America 97 (2004): 240–248. Salom, S. M., et al. “Effect of an inhibitor-based suppression tactic on abundance and distribution of southern pine beetle (Coleoptera: scolytidae) and its natural enemies.” Journal of Economic Entomology 88 (1995): 1,703–1,716. Settle, W. H., et al. “Managing tropical rice pests through conservation of generalist natural enemies and alternative prey.” Ecology 77 (1996): 1,975–1,988. Smith, N. J. H., et al. “Agroforestry developments and potential in the Brazilian Amazon.” Land Degradation and Rehabilitation 6 (1995): 251–263. Thomas, Matthew B. “Ecological approaches and the development of ‘truly integrated’ pest management.” Proceedings of the National Academy of Sciences USA 96 (1999): 5,955–5,951. Vibe-Petersen, H., et al. “Effects of predation and dispersal on Mastomys natalensis population dynamics in Tanzanian maize fields.” Journal of Animal Ecology 75 (2006): 213–220.

invasive species  Invasive species are species

that proliferate within an ecological community and disrupt it. Usually invasive species are exotic, which means they are not native to the ecological community. In some cases, a native species can become invasive if ecological processes that once kept its populations in check are disrupted. Important examples of invasive native species are two species of cedars in the southern Great Plains of North America. When a species enters into a community from outside, its most likely fate is extinction. The climatic and microclimatic conditions in the new habitat will probably be unsuitable for the introduced species. Even if the new species survives, its populations may grow slowly, and it may be eliminated by competition with the better adapted native species. In some cases, however, an alien species may find the new habitat to be ideal for wild proliferation. The native range of the introduced species may have

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330 invasive species  330 been very small, while its new range can be very extensive. The Monterey pine (Pinus radiata) was native to three small forest patches in California, but upon its introduction to New Zealand it spread over large areas. The rapid spread of introduced species has often been caused by human activities, as in these examples: ●●

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Most of the major American agricultural and urban weeds, including the ubiquitous dandelion (Taraxacum officinale), came from Europe, probably because their seeds mixed with those of crop and garden species. Plants and animals may be brought to a new location as livestock, pets, or ornamentals. Ring-necked pheasants (Phasianus colchicus) were brought from China as game birds. Purple loosestrife (Lythrum salicaria) was an ornamental plant, and starlings were pets, brought to America from Europe. One of the most persistent of American weeds, the velvetleaf Abutilon theophrasti, was brought to America because its beautiful immature fruits could be used to make decorations on slabs of butter, hence its other common names, stampweed and butterprint. In each case, organisms escaped and experienced rapid population growth. Many feral livestock animals now roam free, such as goats and pigs in Hawaii and donkeys in Death Valley (see figure).

first entry ●●

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Aquatic organisms live in bilgewater in ships that cross the ocean and escape when bilgewater is dumped. Eurasian watermilfoil (Myriophyllum spicatum) and the zebra mussel (Dreissena polymorpha), both of which are proliferating in many American waterways, may have been introduced in this way. The Asian tiger mosquito, Aedes albopictus, is a vector of viral diseases. It came to North America in pools of water that had accumulated in tires being shipped from Asia to the United States. New species are sometimes deliberately released because humans want to alter the natural environment. Australian melaleuca trees (Melaleuca quinquenervia) were released into the Everglades in order to dry them up for development, something they continue to successfully do. Deliberate introductions were sometimes intended for recreational purposes. Red foxes (Vulpes vulpes) were introduced into Australia so that white immigrants could hunt them, as they had in England; starlings were brought from Europe and released in New York City because someone wanted to have all of the birds mentioned in Shakespeare in North America. Asian carp were raised in enclosed ponds along the Mississippi River. Floods allowed some of them to escape, and they spread northward. Electrical barriers failed to pre-

Donkeys run wild in Death Valley, California. Their populations grew from animals that were released by borax miners in the early 20th century.  (Stanley A. Rice)

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invasive species  331

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vent their spread, through artificial waterways, into the Great Lakes. Two species of cedars, the eastern red cedar (Juniperus virginiana) and the Ashe juniper (J. ashei) are native to the southern Great Plains but were relatively rare in the grasslands before fire suppression and deforestation began in the late 19th century. Today, eastern red cedar is invading many ranchlands, and the Ashe juniper grows abundantly in mountain areas where native oak forests have been cut down. They are considered invasive species even though they are locally native.

In some cases, species were introduced in a sincere but misguided attempt to control other invasive species. Cane toads (Bufo marinus) were introduced into Australia to control agricultural pests, but they did not do so. Coatimundis (Nasua nasua), relatives of the raccoon, were introduced on some Pacific islands, such as the Juan Fernandez Islands, to control rats, but the coatis preyed mostly upon ground-nesting native birds. The birds had evolved in the absence of native predators. An African land snail (Achatina fulica) was introduced into the Society Islands, near Tahiti. Then a predatory snail (Euglandina rosea) was introduced to control it. The predatory snail instead mostly ate native Parula snails, causing most of them to become extinct. Mosquito fish (genus Gambusia) have been introduced into many freshwater wetlands so that they would eat mosquito larvae; in some cases, this has been successful, while in others, the fish have themselves caused ecological problems by displacing native fishes. The ladybird beetle Harmonia axyridis was introduced into Europe to control aphids; it ate aphids but also ate native ladybird beetles. In some cases, alien species invade new territory by natural means, but those means are enhanced by human activity. Microbes and the spores of fungi that kill agricultural crops can spread with dust in the wind even from one continent to another. Human activity, including global warming, has caused soil erosion and perhaps stronger storms, which has caused more dust, and spores, to travel to new locations. In nearly all cases, the new species was introduced while the predators and parasites that would normally have held its populations in check were not. For example, red imported fire ants (Solenopsis invicta) are native to South America, where native phorid flies are parasitic upon them and limit their population growth. In the southern United States, the fire ants are spreading but the flies have not established permanent populations. Once the exotic

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Major Invasive Species   in the United States* Aquatic plants Alternanthera philoxeroides (alligatorweed) Arundo donax (giant reed) Caulerpa taxifolia (Caulerpa seaweed) Didymosphenia geminata (didymo) Egeria densa (Brazilian waterweed) Eichhornia crassipes (water hyacinth) Hydrilla verticillata (hydrilla) Ipomoea aquatica (water spinach) Lythrum salicaria (purple loosestrife) Melaleuca quinquenervia (melaleuca) Myriophyllum spicatum (watermilfoil) Phragmites communis (common reed) Pistia stratiotes (water lettuce) Salvinia molesta (salvinia) Trapa natans (water chestnut)

Aquatic animals Alosa pseudoharengus (alewife) Carcinus maenas (European green crab) Channa argus (snakehead fish) Didemnum vexillum (sea squirt) Dreissena bugensis (quagga mussel) Dreissena polymorpha (zebra mussel) Eriocheir sinensis (Chinese mitten crab) Gymnocephalus cernuus (Eurasian ruffe) Monopterus albus (Asian swamp eel) Myocastor coypus (nutria) Neogobius melanostomus (round goby) Oronectes rusticus (rusty crawfish) Petromyzon marinus (sea lamprey) Potamypyrgus antipodarum (New Zealand mud snail) Pterois volitans (lionfish) Pylodictus olivaris (flathead catfish) Rapana venosa (veined rapa whelk) Rana catesbeiana (bullfrog)

Terrestrial plants Ailanthus altissima (tree of heaven) Alliaria petiolata (garlic mustard) Bromus tectorum (cheatgrass) Carduus nutans (musk thistle) Celastrus orbiculatus (Oriental bittersweet) Centaurea diffusa (diffuse knapweed) Centaurea calcitrapa (purple star thistle) Centaurea solstitialis (yellow star thistle) Centaurea stoebe (spotted knapweed) Cirsium arvense (Canada thistle) Cynoglossum officinale (hounds-tongue) Cystisus scoparius (Scotch broom) Dipsacus fullonum (common teasel) Elaeagnus umbellata (autumn olive) Elaeagnus angustifolia (Russian olive) Elymus repens (quackgrass) (continues)

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332 invasive species  332 Major Invasive Species   in the United States* (continued) Euphorbia esula (leafy spurge) Fallopia japonica (Japanese knotweed) Heracleum mantegazzianum (giant hogweed) Hypericum perforatum (Saint-John’s-wort) Imperata cylindrica (cogongrass) Lepidium appelianum (giant whitetop) Lepidium draba (whitetop) Linaria dalmatica (Dalmatian toadflax) Linaria vulgaris (common toadflax) Lonicera japonica (Japanese honeysuckle) Lygodium microphyllum (Old world climbing fern) Onopordum acanthium (Scotch thistle) Paulownia tomentosa (princess tree) Persicaria perfoliata (mile-a-minute weed) Pueraria montana var. lobata (kudzu) Rhaponticum repens (Russian knapweed) Rosa multiflora (multiflora rose) Solanum viarum (tropical soda apple) Sorghum halepense (Johnson grass) Striga asiatica (witchweed) Taeniatherum caput-medusae (medusahead) Tamarix spp. (salt cedar) Triadica sebifera (tallow tree) Vitex rotundifolia (beach vitex)

first entry species has arrived, native species may ­accidentally help the invader to spread; for example, muskrats help spread the underground stems of loosestrife. The introduced species have many profound influences on the community they invade. They may displace native species or even drive them to extinction, as in these examples: ●●

Terrestrial invertebrates Achatina fulica (African giant snail) Adelges tsugae (hemlock woolly adelgid) Aedes albopictus (Asian tiger mosquito) Agrilus planipennis (emerald ash borer) Anastrepha ludens (Mexican fruit fly) Apis mellifera scutellata (Africanized honeybee) Anoplophora glabripennis (Asian long-horned beetle) Anoplophora chinensis (Citrus long-horned beetle) Bemisia argentifolii (silverleaf whitefly) Cactoblastis cactorum (cactus moth) Ceratitis capitata (Mediterranean fruit fly) Coptotermes formosanus (Formosan subterranean termite) Diaphorina citri (Asian citrus psyllid) Diuraphis noxia (Russian wheat aphid) Epiphyas postvittana (light brown apple moth) Heterodera glycines (soybean cyst nematode) Homalodisca coagulata (glassy-winged sharpshooter) Ips typographicus (European spruce bark beetle) Lymantria dispar (gypsy moth) Maconellicoccus hirsutus (mealybug) Solenopsis invicta (red imported fire ant)

Terrestrial vertebrates Boiga irregularis (brown tree snake) Bufo marinus (cane toad) Sturnus vulgaris (starling) Sus scrofa (wild boar) *From National Agricultural Library. This table does not include agricultural weeds or species whose potential to spread is limited (e.g., burros in Death Valley).

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Some invasive animals harm native animals. Red imported fire ants (Solenopsis invicta) were introduced into the United States about 1930. They have spread throughout the southern states and have recently entered California as well. They cause painful stings, kill some ground-dwelling wild animals, and damage some equipment and some agricultural crops. Ferocious African honeybees have displaced European honeybees (both varieties of Apis mellifera) from the tropical zones of the Americas, reaching as far north as southern Texas. African “killer bees” have had a longer history of exploitation by humans and other predators, and their evolutionary response has been a tendency to attack potentially dangerous animals. African bee queens were allowed to escape from a breeding experiment in Brazil in the 1960s and have mixed with European honeybee populations. Unable to tolerate cold winters, the African bees will probably not extend beyond the southernmost tier of states. European honeybees are themselves an invasive species in North and South America, displacing many native bee species. A population explosion of a comb jelly from Chesapeake Bay, Mnemiopsis leidyi, has destroyed some fisheries in the Caspian Sea. Toxic cane toads in Australia have nearly driven the native marsupial quoll (Dasyurus hallucatus) to extinction because the marsupial does not recognize the toad as poisonous. Some invasive species reproduce faster and outcompete native species. The Nile perch (Lates niloticus) was introduced into Lake Victoria in Africa, where it has driven many of the native species of fish nearly to extinction. Introduced birds such as the myna bird have driven the native birds of Hawaii away from the coastlands and many into extinction. The few remaining native Hawaiian birds can only be found in the highlands. European grasses, originally spread in the droppings of horses that escaped from the Spaniards, have displaced the native California grasses. Water lettuce and water hyacinth fill the surface waters and crowd out

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invasive species  333

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phytoplankton. Populations of melaleuca and loosestrife outgrow those of native plants because they produce millions of seeds. Introduced African grasses inhibit the germination of native Hawaiian tree seedlings. The American gray squirrel (Sciurus carolinensis) has displaced the native red squirrel (Sciurus vulgaris) in many areas of Europe. Invasive species can alter ecosystems, making them unsuitable for native species. Cedars cast dense shade and compete with other plants for water, which they transpire liberally into the air. Native species cannot compete well with them for light and moisture. Fire destroys cedars. But when a fire gets started in the dense cedar brush, it is hot enough to destroy native forest trees. The leaves of the wax myrtle (Myrica cerifera), which has invaded Florida wetlands, do not decompose well and have literally clogged up the aquatic food chain. The deep litter of casuarina trees (Casuarina equisetifolia) introduced into Hawaii from Southeast Asia inhibits the growth of practically everything under their canopy. Kudzu vine (Puereria montana), introduced from Asia, drapes over and kills many trees in the southeastern United States (see photograph). Salt cedars (species of Tamarix; not related to junipers) were introduced from the Middle East and have spread along rivers throughout the western United States, smothering entire riverbanks and driving out the native plant species.

Invading species may create many disturbances. Feral pigs in Hawaii create disturbances in the rain forest, in which the native plant species cannot grow well. However, introduced plants, such as the strawberry guava, thrive in these disturbances. When grasses are first introduced into a community that previously had none, they can create a fire hazard. Fires deplete the populations of species that are not fire-resistant and further encourage the spread of the grasses, which can grow back after the fires. In places where fires were a common part of the natural ecosystem, fire suppression has encouraged the spread of invasive species. Ellwood Cooper planted 50,000 Eucalyptus seedlings at his ranch near Santa Barbara, California, in 1876. Today eucalyptus groves grow where no trees formerly lived. They draw down the water table and can burn explosively. Their fragrant leaf litter accumulates in deep layers because local decomposers cannot consume them. Gum from their flowers clogs the faces and bills of pollinating birds.

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Invading plant species reduce plant species diversity in the community that they invade, and they do so by enhancing the total amount of productivity. Invasive plants enhance net primary production (total net photosynthetic weight gain) by 80 percent. This may occur in part because the invading plants stimulate microbes to release nitrogen into a form that can be readily absorbed and used and in part because invading plants have thinner leaves—this allows more photosynthesis to occur with a given amount of leaf tissue. Exotic predators have disrupted whole food chains. For instance, the brown tree snake (Boiga irregularis) has severely depleted native bird populations on Guam. Invading species can have severe economic impacts on agriculture and even on public health, as well as on nature preserves. The eastern red cedar and the salt cedar transpire enough water that underground water supplies are affected. The Ashe juniper releases pollen that is particularly allergenic. Zebra mussels can clog water intake systems and interfere with municipal water supplies. Cane toads have poisonous skin. Much money and effort are spent in attempts to control the spread of invasive species. It may be impossible to eradicate any invasive species, but in some cases conservation agencies have limited their spread. Sometimes this requires putting up fences. Fences have limited the spread of feral hogs in Hawaii, allowing native vegetation to grow back on one side of the fence and crowding the hogs onto the other side of the fence where they can be more easily shot from helicopters. In order to control the spread of invasive species, it is necessary to monitor them. By the time the invasive organisms are easily visible, it may be too late to do anything about them. The Asian carp in

Do not park your truck too long in the American state of Georgia, or kudzu (the invasive Puereria montana, a plant from East Asia) will grow all over it.  (Stanley A. Rice)

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334 invasive species  334 Illinois, mentioned previously, were first discovered not by observing carp outside the electric barrier but by detecting carp DNA in the water upstream from the fence. Governments now inspect incoming airplanes, ships, and cargo as closely as time and funds permit. In the United States, the Animal and Plant Health Inspection Service (APHIS) is the agency that carries out these inspections. Often the means of controlling invasive species, such as the use of pesticides and herbicides, are as dangerous as they are ineffective, such as mass hunting campaigns. Australians organize mass citizen hunting campaigns against cane toads, with little visible impact. Scientists have investigated biological controls as a method of bringing escaped exotic species under control. Loosestrife is not a pest in Europe, where its populations are controlled by beetles. Scientists are now attempting to introduce those beetles to North America. Biological controls, unlike pesticides, can be permanent. As noted previously, biological control agents run the risk of becoming pests themselves. Eventually, other species (either native or themselves introduced) will evolve ways of eating the invaders, bringing their populations into check. The time required for this process, however, is likely to make it meaningless to human concerns. See also communities, ecological. Further Reading Agricultural Research Service, United States Department of Agriculture. “Biological control sends scurrying scourge scrambling.” Available online. URL: http:// www.ars.usda.gov/is/AR/archive/may03/biol0503. htm. Accessed August 1, 2010. Burdick, Alan. “The truth about invasive species.” Discover, May 2005, 34–41. Coote, T., and E. Loeve. “From 61 species to five: Endemic tree snails of the Society Islands fall prey to an illjudged biological control programme.” Oryx 37 (2003): 91–96. Cox, William. Alien Species and Evolution: The Evolutionary Ecology of Exotic Plants, Animals, Microbes, and Interacting Native Species. Washington D.C.: Island Press, 2004. Daehler, Curtis C. “Performance comparisons of co-occurring native and alien invasive plants: Implications for conservation and restoration.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 183–212. Davis, Mark A. Invasion Biology. New York: Oxford University Press, 2009. Duncan, Richard P., et al. “The ecology of bird introductions.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 71–98.

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first entry Enserink, Martin. “A mosquito goes global.” Science 320 (2008): 864–867. Forseth, Irwin N., and A. F. Innis. “Kudzu (Puereria montana): History, physiology, and ecology combine to make a major ecosystem threat.” Critical Reviews in Plant Sciences 23 (2004): 401–413. Greenway, Roger. “NOAA solution to lionfish invasion, eat them!” Environmental News Network, August 8, 2010. Available online. URL: http://www.enn. com/wildlife/article/41636. Accessed August 8, 2011. Hendrix, Paul F., et al. “Pandora’s box contained bait: The global problem of introduced earthworms.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 593–613. Hobbs, R. J., and Laura F. Huenneke. “Disturbance, diversity, and invasion—implications for conservation.” Conservation Biology 6 (1992): 324–337. Isard, S. A., et al. “Principles of the atmospheric pathway for invasive species applied to soybean rust.” BioScience 55 (2005): 851–861. Keller, Reuben P., et al., eds. Bioeconomics of Invasive Species: Integrating Ecology, Economics, Policy, and Management. New York: Oxford University Press, 2009. Krajick, Kevin. “Winning the war against island invaders.” Science 310 (2005): 1,410–1,413. Liu, Shu-Sheng, et al. “Asymmetric mating interactions drive widespread invasion and displacement in a whitefly.” Science 318 (2007): 1,769–1,772. Summarized by Reitz, Stuart R., “Invasion of the whiteflies.” Science 318 (2007): 1,733–1,734. Mooney, Harold A., et al., eds. Invasive Alien Species: A New Synthesis. Washington, D.C.: Island Press, 2005. National Agricultural Library. “National invasive species information center.” Available online. URL: http:// www.invasivespeciesinfo.gov. Accessed August 8, 2011. O’Donnell, S., et al. “Conditioned taste aversion enhances the survival of an endangered predator imperiled by a toxic invader.” Journal of Applied Ecology 47 (2010): 558–565. Parker, John D., et al. “Opposing effects of native and exotic herbivores on plant invasions.” Science 311 (2006): 1,459–1,461. Peterson, A. Townsend, et al. “Predicting the potential invasive distributions of four alien plant species in North America.” Weed Science 51 (2003): 863–868. Pyke, Graham H. “Plague minnow or mosquito fish? A review of the biology and impacts of Gambusia species.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 171–191. Romero, Simon. “War in the Pacific: It’s hell, especially if you’re a goat.” New York Times, May 1, 2007. Available online. URL: http://www.nytimes.

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island biogeography  335 com/2007/05/01/world/americas/01galapagos. html?pagewanted=print. Accessed August 8, 2011. Rout, Marnie E., and Ragan M. Callaway. “An invasive plant paradox.” Science 324 (2009): 734–735. Ruesink, Jennifer L., et al. “Introduction of non-native oysters: Ecosystem effects and restoration implications.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 643–689. Sax, Dov F., John J. Stachowicz, and Steven D. Gaines, eds. Species Invasions: Insights into Ecology, Evolution, and Biogeography. Sunderland, Mass.: Sinauer Associates, 2005. Snyder, William E., and Edward W. Evans. “Ecological effects of invasive arthropod generalist predators.” Annual Review of Ecology, Evolution, and Systematics 37 (2006): 95–122. Suarez, A. V., et al. “Effects of fragmentation and invasion on native ant communities in coastal southern California.” Ecology 79 (1998): 2,041–2,056. Svoboda, Elizabeth. “The unintended consequences of changing nature’s balance.” New York Times, February 17, 2009. Available online. URL: http://www.nytimes. com/2009/02/17/science/17isla.html. Accessed August 8, 2011. Tennesen, Michael. “When juniper and woody plants invade, water may retreat.” Science 322 (2008): 1,630–1,631. Terrill, Geiridwen. Unnatural Landscapes: Tracking Invasive Species. Tucson: University of Arizona Press, 2007. Todd, Kim. Tinkering With Eden: A Natural History of Exotic Species in America. New York: Norton, 2002. Traveset, Anna, and D. M. Richardson. “Biological invasions as disrupters of plant reproductive mutualisms.” Trends in Ecology and Evolution 21 (2006): 208–216. United States Department of Agriculture. “Animal and Plant Health Inspection Service: Safeguarding American agriculture.” Available online. URL: http://www. aphis.usda.gov. Accessed August 8, 2011. Vogt, J. T., Stanley A. Rice, and Steven A. Armstrong. “Seed preferences of the Red Imported Fire Ant (Hymenoptera: Formicidae) in Oklahoma.” Journal of Entomological Science 38 (2003): 696–698. Vredenburg, V. T. “Reversing introduced species effects: Experimental removal of introduced fish leads to rapid recovery of a declining frog.” Proceedings of the National Academy of Sciences USA 101 (2004): 7,646–7,650. Wiles, G. J., et al. “Impacts of the brown tree snake: Patterns of decline and species persistence in Guam’s avifauna.” Conservation Biology 17 (2003): 1,350–1,360. Williams, Susan L., and Jennifer E. Smith. “A global review of the distribution, taxonomy, and impacts of introduced seaweeds.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 327–359.

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island biogeography  Biogeography is the

study of what kinds of organisms grow in different geographical locations. Even before Charles Darwin and Alfred Russel Wallace, islands were of special interest because their isolation has allowed the evolution of many endemic species. It was the uniqueness of island species but also their similarity to the species of the nearby mainland that helped Charles Darwin formulate the theory of evolution. But island biogeography remained largely a collection of interesting evolutionary stories until ecologists Robert H. MacArthur and Edward O. Wilson formalized it into a mathematically based theory. An island may have no species when it first forms. New species disperse to the island from nearby mainland areas and evolve on the island. Meanwhile, species become extinct as well. Two factors affect the extent to which these processes occur: ●●

●●

Distance effect Islands that are more distant from the mainland are less likely to receive immigrants. Area effect Larger islands are able to maintain a greater number of species than smaller islands.

The consequences of these processes are that smaller and/or more distant islands will have fewer species and that an island may reach an equilibrium number of species. New species will continue to arrive or evolve, and old species will become extinct, leaving the equilibrium number of species unchanged. The area effect results from the fact that larger islands have a greater number of different kinds of habitats in which different species can live. This results in the species-area relationship. A very small island might force different species to compete, whereas on a larger island the species could specialize on different ways of obtaining resources. Even though the theory of island biogeography mainly concerns the arrival and survival of species that already exist, there is also a longer-term evolutionary dimension to it. A larger island will allow the evolution of more new species than will a smaller island. The Galápagos Islands collectively have enough area that 13 species of finches have been able to evolve different specializations, whereas Cocos Island does not have enough area for the finches to form separate breeding populations. The Cocos Island finch remains a single species even while different individuals obtain food in different ways, some of them similar to the specializations of the different Galápagos finches. The greater

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336 island biogeography  336 species capacity of a larger island not only allows more species to evolve but prevents those species from becoming extinct as often. The species-area relationship, however, is not linear. As islands get bigger, the increased area is not associated with an increased number of new habitat types. That is, as islands get larger, the number of species tends to level off. The curve never reaches a maximum number, however, unless the island becomes nearly as large as a continent itself. It might appear simple enough to test island biogeography theory by comparing species richness on different islands, but modern species richness is produced both by ecological and evolutionary processes. How is it possible to test island biogeography on an ecological timescale short enough that new species will not evolve? Ecologist Daniel Simberloff, working with Edward O. Wilson, tried an experimental approach. They identified different mangrove islands (islands formed by mangrove tree clumps growing out of shallow water) in the Gulf of Mexico, of many different sizes and distances from the mainland. They then used insecticides to kill all of the arthropods on these islands. They waited for arthropods to colonize the islands from the mainland. They then counted the number of arthropod species on each island. They focused on arthropods because vertebrates were unlikely to be permanent residents on such small islands. Also, arthropods have short enough generation times that the equilibrium species number could be reached within a manageable length of time. They did find that smaller islands and more distant islands had fewer arthropod species after a few years. Of course, there were other factors that affected the number of species on each island, including the hurricanes that occasionally came through their research area. The concepts of island biogeography are important for ecological islands as well as for geographical islands. Some habitats, especially those that have many endemic species, are isolated pockets surrounded by habitat that is unsuitable for those species. The surrounding area might as well be an ocean, for all the difference it makes to the species in the small habitats. The dry temperate oak forests on mountaintops surrounded by the Chihuahuan Desert are called “sky islands.” In a more general sense, nearly every habitat can be thought of as an island surrounded by some other kind of habitats. The consequences for conservation are important. Just how big does a protected area need to be? And where should protected areas be located? They need to be big enough to have microhabitat hetero-

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first entry geneity that will allow all of the species to survive. If a habitat type is protected by several small areas rather than one large one, these small areas need to be close enough together that a species, should it happen to become extinct in one of them, can be replaced by colonists from another one. One reason that conservation biologists use island biogeography analysis is that the option of protecting entire habitats usually does not exist. They have to make scientifically based arguments for even the smallest amount of habitat area that they ask the government to protect from development or exploitation. Island biogeography theory allows them to make the best decisions for the protection of small areas that may allow as many species as possible to survive. Island biogeography theory also helps to explain why habitat fragmentation can so severely damage the survival prospects of rare species. See also biogeography; endemic species; habitat fragmentation. Further Reading Davis, Anthony M., and Thomas F. Glick. “Urban ecosystems and island biogeography.” Environmental Conservation 5 (1978): 299–304. Diamond, Jared M. “The island dilemma: Lessons of modern biogeographic studies for the design of natural reserves.” Biological Conservation 7 (1975): 129–146. Drakare, Stina, et al. “The imprint of the geographical, evolutionary, and ecological context on species-area relationships.” Ecology Letters 9 (2005): 215–227. Gilbert, F. S. “The equilibrium theory of island biogeography: Fact or fiction?” Journal of Biogeography 7 (1980): 209–235. Harris, Larry D. The Fragmented Forest: Island Biogeography Theory and the Preservation of Biotic Diversity. Chicago: University of Chicago Press, 1984. Kadmon, Ronen, and H. Ronald Pulliam. “Island biogeography: Effect of geographical isolation on species composition.” Ecology 74 (1993): 977–981. MacArthur, Robert H., and Edward O. Wilson. Theory of Island Biogeography. Princeton, N.J.: Princeton University Press, 1967. Quammen, David. The Song of the Dodo: Island Biogeography in an Age of Extinctions. New York: Scribner, 1996. Scheiner, Samuel M. “Six types of species-area curves.” Global Ecology and Biogeography 12 (2003): 441–447. Simberloff, Daniel S. “Equilibrium theory of island biogeography and ecology.” Annual Review of Ecology and Systematics 5 (1974): 161–182. ———, and Lawrence G. Abele. “Refuge design and island biogeographic theory: Effects of fragmentation.” American Naturalist 120 (1982): 41–50.

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isolating mechanisms  337 Simberloff, Daniel S., and Edward O. Wilson. “Experimental zoogeography of islands: The colonization of empty islands.” Ecology 50 (1969): 278–296. Whittaker, Robert J., and José María Fernandez-Palacios. Island Biogeography: Ecology, Evolution, and Conservation. New York: Oxford University Press, 2007. Zimmerman, B. L., and R. O. Bierregaard. “Relevance of the equilibrium theory of island biogeography and

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species-area relations to conservation with a case from Amazonia.” Journal of Biogeography 13 (1986): 133–143.

isolating mechanisms  See speciation.

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J jackson, Wes (1936– ) American Agricultural ecologist Wes Jackson is the founder and leader of the land institute, a Kansas organization that is the principal proponent of a biodiversity-based agriculture (natural systems agriculture). Born June 15, 1936, on a farm in Kansas, Jackson received a master’s degree in botany from the University of Kansas and a Ph.D. in genetics from north carolina State University. He established one of the earliest environmental studies programs in the United States while he was at the Sacramento campus of california State University. in 1976, he resigned and returned to Kansas to establish the land institute. the institute began with farmland and intact prairie, and Jackson wanted to use the prairie as a model for how agriculture could be transformed from an industrial mode to a natural and sustainable mode. the land institute has attracted researchers from around the world who work either at the land institute or at their home institutions. For many years, the land institute sponsored undergraduate interns but now focuses on supporting graduate student research. Some land institute staff, including Jerry Glover, have received international recognition for their research. Wes Jackson is widely recognized as one of the major ecological visionaries of modern times. His books tie in agricultural themes with every aspect of modern environmentalism. Life magazine listed Jackson as one of the 100 most important people of the 20th century, and Smithsonian magazine listed him as one of the 35 people who had made the greatest difference in the world in the 20th century. See also natural systems agriculture.

Further reading Jackson, Wes. Altars of Unhewn Stone: Science and the Earth. Wooster, Ohio: Wooster Books, 2006. ———. Becoming Native to This Place. Washington, D.c.: counterpoint, 1994. ———. Consulting the Genius of the Place: An Ecological Approach to a New Agriculture. Washington, D.c.: counterpoint, 2010. ———. New Roots for Agriculture. lincoln, neb.: University of nebraska Press, 1980.

janzen, daniel h. (1939– ) American Ecologist, evolutionary biologist, conservationist Dan Janzen is one of the most significant figures in modern ecology and conservation. He is famous for his original insights, his creative ways of researching and expressing them, and his dynamic lectures about them. among his research contributions have been the following: ●



● ●

ants (such as Pseudomyrmex ferruginea) protect acacia trees (e.g., Acacia cornigera) from herbivores, one of the prime examples of the evolution of mutualism. the seed dispersers of Spondias mombin, a tropical tree, became extinct at the end of the Pleistocene epoch, and today it depends on white-tailed deer to disperse its seeds. Herbivory is one of the reasons that there are so many species of trees in tropical forests. Because tropical rain forests have uniform temperatures throughout the year, tropical organisms are more likely to experience even the slightly cooler conditions of tropi-

338

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Jurassic period, biodiversity in  339

●●

cal mountains as a barrier to dispersal than are temperate organisms. That is, mountain passes “are higher” in the Tropics. Decomposers produce chemicals that repel herbivores and scavengers that would otherwise eat them along with the old or dead plant or animal tissue. This is why “fruits rot, seeds mold, and meat spoils.”

Even when later researchers have challenged some of his broad hypotheses, none have denied that they were creative. Born in 1939 in Milwaukee, Wisconsin, Janzen graduated from the University of Minnesota in 1961 and earned his doctorate from the University of California at Berkeley four years later. Since 1965 he has been one of the leaders of the Organization for Tropical Studies, which trains students in tropical biology. He taught at universities in Kansas, Chicago, Venezuela, and Puerto Rico before joining the faculty at the University of Pennsylvania. Janzen has been on the faculty of the University of Pennsylvania since 1976, but for many years he has served without remuneration as an adviser to the government of Costa Rica. Largely through his leadership, Costa Rica has the best system of ecological reserves, relative to its size, of any country in the world, including a plan that connects the reserves together; as a result, one-quarter of Costa Rica is protected or being restored. Janzen has incorporated the need for local inhabitants to use the land sustainably, rather than simply keeping people out of the parks. He is also leading an ambitious project to catalog the country’s biodiversity, including the use of DNA barcoding to reveal previously unrecognized biodiversity. In 1984 he received the Crafoord Prize, given to scientists whose research is not in a category specified for the Nobel Prize. See also Essay: Ghosts of Biodiversity Past; biodiversity, patterns of; DNA studies of biodiversity; habitat fragmentation; mutualism; Pleistocene extinction; restoration ecology; seed dispersal. Further Reading Ghalambour, Cameron K., et al. “Are mountain passes higher in the tropics? Janzen’s hypothesis revisited.” Integrative and Comparative Biology 46 (2006): 5–17. Hebert, P. D. N., et al. “Ten species in one: DNA barcoding reveals cryptic species in the neotropical skipper butterfly Astraptes fulgerator.” Proceedings of the National Academy of Sciences 101 (2004): 14,812–14,817. Janzen, Daniel H. 1966. “Allelopathy by myrmecophytes: The ant Azteca as an allelopathic agent of Cecropia.” Ecology 50 (1969): 147–153.

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——— “Coevolution of mutualism between ants and acacias in Central America.” Evolution 20 (1966): 249–75. ———. “Escape of Cassia grandis L. beans from predators in time and space.” Ecology 52 (1971): 964–979. ———. “Gardenification of wildland nature and the human footprint.” Science 279 (1998): 1,312– 1,313. ———. “Herbivores and the number of tree species in tropical forests.” American Naturalist 104 (1970): 502–528. ———. “Why fruits rot, seeds mold, and meat spoils.” American Naturalist 111 (1977): 691–713. ———. “Why mountain passes are higher in the tropics.” American Naturalist 101 (1967): 233–249. ——— and Paul S. Martin. “Neotropical anachronisms: The fruits the gomphotheres ate.” Science 215 (1982): 19–27. Sherratt, Thomas N., et al. “Why fruits rot, seeds mold, and meat spoils: A reappraisal.” Ecological Modeling 192 (2006): 618–626. Smith, M. A., et al. “Extreme diversity of tropical parasitoid wasps exposed by iterative integration of natural history, DNA barcoding, morphology, and collections.” Proceedings of the National Academy of Sciences USA 105 (2008): 12,359–12,364.

Jurassic period, biodiversity in  The Jurassic period (210 to 140 million years ago) was the middle period of the Mesozoic era. It followed the Triassic period. The Mesozoic era is also known as the Age of Dinosaurs, because dinosaurs were the largest land animals during that time. Dinosaurs first evolved during the Triassic period but became the largest, most diverse, and most abundant terrestrial vertebrates during the Jurassic period and into the Cretaceous. Dinosaurs became extinct during the Cretaceous extinction, which is one of the two most important mass extinctions in the history of the Earth. Climate. In the mild climate of the Jurassic period, swamps and shallow seas covered widespread areas. As in the Carboniferous, atmospheric levels became very high, even though carbon dioxide continued to create a greenhouse atmosphere (see table on page 340). Continents. The continents formed by the breakup of Pangaea continued to separate. The northern continent (Laurasia) consisted of what are today the northern continents (North America, Europe, Asia). The southern continent (Gondwana) consisted of what are today the southern continents (South America, Africa, Antarctica, Australia), with the Tethys Sea between them.

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340 Jurassic period, biodiversity in 340

first entry

Multicellular Biodiversity in the Jurassic Period Conditions Atmospheric oxygen Atmospheric carbon dioxide Global temperature Sea level

30% above modern level 5.5 times modern level 5°F (3°C) above modern level 300 ft (100 m) higher than today

Approximate number of families* Continental Marine Total

200 450 650

Examples of marine animals Belemnobatis morinicus Cycloprosopon dobrogea Ermoceras sp. Eryon actiformis Grendelius mordax Hybodus houtiensis Leptolepis talbragarensis Metriorhynchus geoffroyi Plesiosaurus dolichodeirus

ray (shark relative) crab cephalopod mollusk lobster ichthyosaur reptile shark bony fish sea crocodile plesiosaur reptile

Examples of continental animals Allosaurus fragilis Apatosaurus ajax Archaeolepis mane Archaeopteryx lithographica Bharatagama rebbanensis Brachiosaurus altithorax Castorocauda lutrasimilis Ceratosaurus ingens Compsognathus longipes Diplodocus longus Frutafossor windscheffeli Grimmyia baltica Iguanodon bemissartensis Mesocordulia boreala Microraptor zhaoianus Morganucodon watsoni Patarchaea muralis Pterodactylus antiquus Siamochelys peninsularis Sigmaboilus peregrinus Stegosaurus amatus Supersaurus vivianae Tritylodon longaevus Velociraptor mongoliensis Xyletoma nigricornis

large herbivorous dinosaur large herbivorous dinosaur butterfly or moth feathered dinosaur lizard large herbivorous dinosaur mammal large predatory dinosaur small predatory dinosaur large herbivorous dinosaur mammal fly medium herbivorous dinosaur dragonfly feathered dinosaur mammal spider pterosaur turtle cricket relative large herbivorous dinosaur large herbivorous dinosaur mammallike reptile feathered dinosaur wasp

Examples of land plants Araucarioxylon arizonicum Bucklandia sp. Ginkgo sibirica Komlopteris nordenskioeldii Sewardiodendron laxum Williamsoniella coronata

conifer cycad ginkgo seed fern conifer bennettitalean seed plant

*Based on Benton.

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Jurassic period, biodiversity in 341 Marine life. Marine continued to evolve:

life

Invertebrates. the invertebrates that predominated in the triassic oceans continued to proliferate. among the crustaceans, the fi rst lobsters and crabs evolved. One of the crabs, Cycloprosopon, had no legs. ● Vertebrates. Bony fishes and sharks continued to proliferate in the oceans. Rays, relatives of sharks, fi rst evolved during the Jurassic. Stegosaurus was a large armored dinosaur of the Jurassic period. Marine reptiles that evolved in the triassic continued to flourish; in addition, new groups of marine allowed them to eat foliage from the tops of conifers. reptiles evolved: plesiosaurs (marine reptiles examples include Apatosaurus (formerly Brontowith very long necks) and sea crocodiles, saurus), Diplodocus, and Brachiosaurus; Supersausome of them 10 feet (three m) long. rus, almost 100 feet (30 m) long and weighing 100 tons (metric tons), was nearly at the theoretical maxContinental life. Gymnosperms dominated the imum size that is possible for a terrestrial animal. terrestrial forests, in which dinosaurs proliferated Some herbivorous dinosaurs, such as Iguanodon, and in which the fi rst birds evolved. were smaller and could run on two legs. though there were some large predators such as Ceratosau● Plant life. conifers, such as relatives of rus, many of the predators were small and rapid— the modern monkey puzzle tree, dominated and many of them had feathers. Small feathered the forests, which also contained many spedinosaurs were, in fact, the fi rst birds, of which 23 cies of ginkgo and cycads. Araucarioxylon Jurassic genera have been found. the most famous is trees made up the forest now preserved at Archaeopteryx, but there were many others as well. Petrified Forest national Park in arizona. it is not known which of them might have been the Seed ferns persisted but were becoming less ancestor of more recent birds. Fossils of Archaeopcommon. teryx were preserved with feather impressions in ● Invertebrates. terrestrial invertebrates the surrounding rock. the flying pterosaurs (such as continued to diversify, especially insects Pterodactylus) were a separate lineage of evolution such as fl ies, crickets, beetles, wasps, and and were not birds. dragonfl ies. the earliest lepidopterans (butSee also dinosaurs. terfl ies and moths) are known from the Jurassic. Further reading ● Vertebrates. Freshwater fishes, lungfishes, Benton, Michael J. “Dinosaur summer.” in The Book of and amphibians continued to evolve. Some Life: An Illustrated History of the Evolution of Life on reptiles such as turtles persisted. the fi rst lizEarth, edited by Stephen J. Gould. new york: norton, ards appeared during the Jurassic. Mammal2001. like reptiles were becoming less abundant, ———. “Diversification and extinction in the history of as true mammals evolved. although not as life.” Science 268 (1995): 52–58. diverse as dinosaurs, mammals did come in carpenter, K., and J. Mcintosh. “Upper Jurassic sauropod numerous forms, including some beaverlike babies from the Morrison Formation.” in Dinosaur aquatic mammals (Castorocauda) and some Eggs and Babies, edited by K. carpenter, K. F. Hirsch, that ate termites (Frutafossor). and J. R. Horner. cambridge: cambridge University ●

the dominant land vertebrates of the Jurassic were the dinosaurs, which diversified into many forms after the triassic extinction. Some herbivorous dinosaurs grew very large and had long necks that

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Press, 2007. Feldmann, Rodney M., et al. “Ekalakia (Decapoda: Brachyura): the preservation of eyes links cretaceous crabs to Jurassic ancestors.” Journal of Paleontology 82 (2008): 1,030–1,034.

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342 Jurassic period, biodiversity in  342 Foster, J. Jurassic West: The Dinosaurs of the Morrison Formation and Their World. Bloomington, Ind.: Indiana University Press, 2007. Ji, Qiang, et al. “A swimming mammaliaform from the Middle Jurassic and ecomorphological diver-

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first entry sification of early mammals.” Science 311 (2006): 1,123–1,127. Stevens, Kent A., and J. Michael Parrish. “Neck posture and feeding habits of two Jurassic sauropod dinosaurs.” Science 284 (1999): 798–800.

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K keystone  species  Keystone species play an

around. in fact, even the increase in fi re frequency was an effect rather than a cause. the spread of forests, during the mammoth and mastodon declines, caused a buildup of dead wood that promoted fi res. the authors of the study speculated that the decline in large mammals was due to overhunting by earlier peoples, and that the clovis hunting technology was a response to, rather than a cause of, declining abundance of prey. consider the following examples of large, abundant keystone species:

important role in their ecological communities far out of proportion to their abundance or diversity. the name is borrowed from the keystone of an arch which, while just a single stone, maintains the integrity of the arch. ecologist Robert Paine introduced the idea in the 20th century. a keystone species performs an important function that creates or alters conditions upon which many other species depend. therefore, keystone species are often irreplaceable in an ecological community, and their disappearance leads to great disruption. Many of the large mammals that perished in the Pleistocene extinction were keystone species. at the end of the most recent ice age, about 12,000 years ago, many large mammals became extinct, including grazers and browsers such as mammoths and mastodons. Several major events appeared to have happened simultaneously: the large mammal extinctions; changes in climate, which caused forests to spread and grasslands to retreat; an increase in the frequency of fi res; and the arrival of humans with advanced hunting techniques such as the clovis style of arrowheads. Some scientists attributed the large mammal extinctions to vegetation changes caused by climate; others attributed them to overhunting by the clovis people. a more careful study of the sequence of events, as recorded in lake sediments, showed that the large mammal populations began to decline a thousand years before the forests began to spread and the clovis people arrived. Something caused the large herbivores to begin dying. these animals had maintained the grasslands. the decline in keystone herbivores caused the vegetation changes, not the other way



large grazing animals eat a lot of grass and other plants, thus playing a major role in the food chain and making a major contribution to the cycling of nutrients. in fact, they alter their ecosystems. Grasses grow from underground stems and easily grow back after grazing, while many dicot herbs, shrubs, and tree seedlings do not recover as easily. Heavy grazing pressure can therefore encourage the spread of grasslands at the expense of forests. elephants can function as keystone species, just as did their ancient mammoth and mastodon relatives. One reason that the african savanna does not become acacia woodland is that elephants rip and bulldoze the trees to eat their leaves and seed pods. But african elephants function as keystone species in another way as well. they consume the seeds but do not chew all of them. Most acacia seed pods are infested with insect larvae, which destroy most of the seeds—unless, that is, the seed pods are eaten by an elephant. the

343

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344 keystone species  344

●●

●●

●●

elephant’s digestive tract destroys the insect larvae. Elephant droppings often contain intact acacia seeds. Elephants are one of the major sources of new acacia trees in the African savanna. Top predators often control the populations of many species of prey. One example is the dusky shark, Carcarhinus obscurus. It preys upon other predatory fish, keeping their populations low. When the shark populations decline, populations of the middle predators in the food chain increase. They eat a lot of scallops, causing the scallop populations to decline. Another example is starfish, which are predators upon mussels. Without starfish predators, mussels would dominate some rocky shorelines. Starfish predation opens up some room on the rocks, where barnacles and seaweeds can grow. The disappearance of top predators may cause trophic cascades, in which bursts of overpopulation and decline pass down each link in the food web, from predators to prey to plants. Some keystone species actually create habitats in which other species live. Beavers build dams, which can convert an entire terrestrial habitat into a wetland. Some ecologists call beavers “ecosystem engineers.” Corals are keystone species in the reef communities that are named after them mainly because their calcium carbonate shells accumulate, creating a new and complex substrate upon which seaweeds can grow and starfish can graze. Small herbivores can be keystone species (or sets of species) as well. The application of pesticides that killed most of the arthropods and mollusks in European meadows caused the plant species diversity to decrease.

It is not necessary that other species entirely depend upon the activities of the keystone species. Prairie dogs (Cynomys spp.) are generally considered keystone species in the shortgrass prairies of North America because of their extensive tunnel systems. They aerate and fertilize the soil and create pockets of disturbed soil in which many plant species grow better than in undisturbed grass sod. It turns out that few if any of the animal and plant species that benefit from prairie dog activities actually depend upon them; they are all found in nearby areas, though not as abundantly. Despite this, prairie dogs can still be considered a keystone species because they greatly

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first entry enhance the abundance of other species. The same is true of the plateau pika (Ochotona curzoniae) in Tibet. In both of these cases, humans extensively poison the keystone species in the mistaken belief that they eat too much of the grass upon which livestock forage. Keystone species interactions can get very complex. Ecologists Gretchen Daily and Paul Ehrlich describe a keystone species system in the subalpine forests of Colorado, where red-naped sapsuckers are keystone species in two different ways. First, they excavate nest cavities in aspens in which the heartwood has decomposed. Two other bird species depend upon these nests, after the sapsuckers have abandoned them. The sapsuckers also drill holes in willow trunks, which collect sap that is eaten by many other animal species. The authors conclude, “Disappearance of any element of the complex could cause an unanticipated unraveling of the community.” In many cases, a group of species, rather than a single keystone species, may control an ecological community. A couple of examples are the following: ●●

●●

Wolves and deer on the Kaibab plateau.  The Kaibab Plateau forms the North Rim of the Grand Canyon in Arizona. It is a mixture of grassland, aspen groves, and temperate pine forests. Deer prefer aspen over other kinds of forage, therefore aspen is rare during deer population explosions. One of the pioneers of modern ecological science, Aldo Leopold, had once participated eagerly in government-sponsored predator eradication campaigns, which aimed to increase the deer population for hunters by removing the predators that competed with the hunters for prey. He changed his mind, however, when he noticed that, in the absence of wolves, hunters did not kill enough deer to keep the populations from exploding. He attributed the deer population explosion in the early 20th century directly to wolf eradication campaigns. As it turns out, very few wolves were killed on the Kaibab Plateau, where mountain lions were the principal predators. It therefore appears that a set of predator species, rather than just one, controls deer populations. The American chestnut. Chestnuts (Castanea dentata) were important forest trees in eastern deciduous forests of North America until a fungus (Cryphonectria parasitica, formerly Endothia parasitica) escaped from

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keystone species  345 imported European chestnut trees and killed all of the adult American chestnut trees. The chestnut blight spread from New York down to Georgia, killing almost all large Appalachian chestnut trees by the 1950s. The forests were temporarily disrupted, but within decades the spaces formerly filled by chestnuts were taken by other trees, mostly oaks. Chestnuts were just one of several species that can play a keystone role in deciduous forests. Sometimes the keystone effect of a species can change, depending on its behavior. Alewives (a species of fish, Alosa pseudoharengus) eat zooplankton in lakes. Heavy predation by alewives results in zooplankton with smaller bodies. In some lakes, the alewives remain all year, while in others they can migrate to the ocean and back. Lakes with landlocked alewives had small-bodied zooplankton year-round, and lakes that had no alewives had large-bodied zooplankton year-round. In contrast, zooplankton communities in lakes with migratory alewives cycled between large-bodied zooplankton in the winter and spring and small-bodied zooplankton in the summer. Because of their importance, keystone species are a special focus of preservation and restoration efforts. Keystone species are essential in a restored habitat, because they create the habitat conditions upon which many other species depend. Keystone species are merely pursuing their own interests. They do nothing for the benefit of the ecological community that they help to create. They may benefit from the results but they evolved because their way of living, which just happened to have important ecological effects, enhanced their evolutionary fitness. The most significant keystone species in the world is, of course, humans, who have altered the ecosystems of the Earth in numerous ways described throughout this encyclopedia. Even some of the mildest human activities can have cascading effects on ecosystems. Consider the example of Yosemite National Park. Millions of people visit it, and they are forbidden to cause any harm to the natural areas, a rule that is largely respected. However, their presence scares away cougars. Mule deer, in contrast, have learned that people like to watch them. Mule deer populations are therefore quite large, and they graze seedlings of Quercus kelloggii oak seedlings as well as wildflowers such as the evening primrose Oenothera hookeri, which were once one of Yosemite’s most famous beauties. Oaks and evening primroses are becoming scarce in Yosemite Valley,

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despite control burns intended to encourage their propagation. See also ecosystems; Leopold, Aldo; Pleistocene extinction. Further Reading Baum, J. K., et al. “Collapse and conservation of shark populations in the northwest Atlantic.” Science 299 (2003): 389–392. Binkley, Dan, et al. “Was Aldo Leopold right about the Kaibab deer herd?” Ecosystems 9 (2006): 227–241. Daily, Gretchen C., Paul R. Ehrlich, and N. M. Haddad. “Double keystone bird in a keystone species complex.” Proceedings of the National Academy of Sciences USA 90 (1993): 592–594. Gill, Jacquelyn L., et al. “Pleistocene megafaunal collapse, novel plant communities, and enhanced fire regimes in North America.” Science 326 (2009): 1,100–1,103. Summarized by Johnson, Christopher. “Megafaunal decline and fall.” Science 326 (2009): 1,072–1,073. Kotliar, Natasha B., et al. “A critical review of assumptions about the prairie dog as a keystone species.” Environmental Management 24 (1999): 177–192. Menge, Bruce A., et al. “The keystone species concept: Variation in interaction strength in a rocky intertidal habitat.” Ecological Monographs 64 (1994): 249–286. Mills, L. Scott, et al. “The keystone-species concept in ecology and conservation.” BioScience 43 (1993): 219–224. Mooney, Kailen A., et al. “Evolutionary trade-offs in plants mediate the strength of trophic cascades.” Science 327 (2010): 1,642–1,644. Morell, Virginia. “Yosemite: Protected but not preserved.” Science 320 (2008): 597. Myers, R. A., and B. Worm. “Rapid worldwide depletion of predatory fish communities.” Nature 423 (2003): 280–283. ———, et al. “Cascading effects of the loss of apex predatory sharks from a coastal ocean.” Science 315 (2007): 1,846–1,850. Paine, Robert T. “Food web complexity and species diversity.” American Naturalist 100 (1966): 65–75. Post, David M., et al. “Intraspecific variation in a predator affects community structure and cascading trophic interactions.” Ecology 89 (2008): 2,019–2,032. Ripple, William J., and Robert L. Beschta. “Hardwood tree decline following large carnivore loss on the Great Plains, USA.” Frontiers in Ecology and the Environment 5 (2007): 241–246. Schmitz, Oswald J. “Effects of predatory hunting mode on grassland ecosystem function.” Science 319 (2008): 952–954. Sharam, Gregory J., et al. “Serengeti birds maintain forests by inhibiting seed predators.” Science 325 (2009): 51.

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346 keystone species  346 Smith, Andrew T., and J. Marc Foggin. “The plateau pika (Ochotona curzoniae) is a keystone species for biodiversity on the Tibetan Plateau.” Animal Conservation 2 (1999): 235–240. Stein, Claudia, et al. “Impact of invertebrate herbivory in grasslands depends on plant species diversity.” Ecology 91 (2010): 1,639–1,650. Terborgh, John, and James Estes, eds. Trophic Cascades: Predators, Prey, and the Changing Dynamics of Nature. Washington, D.C.: Island Press, 2010.

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first entry Watson, David M. “Mistletoe—A keystone resource in forests and woodlands worldwide.” Annual Review of Ecology and Systematics 32 (2001): 219–249. Willson, Mary F., and Karl C. Halupka. “Anadromous fish as keystone species in vertebrate communities.” Conservation Biology 9 (2002): 489–497. Wright, Justin P. “Linking populations to landscapes: richness scenarios resulting from changes in the dynamics of an ecosystem engineer.” Ecology 90 (2009): 3,418–3,429.

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L lakes  and  ponds  See rivers, streams,

He also began to develop what he called “the land ethic,” in which he called for the preservation of entire ecological communities as an ethical imperative. His ideas were developed in essays, published posthumously as A Sand County Almanac, one of the most famous environmental books. in one essay he wrote, “a thing is right when it tends to preserve the integrity, stability, and beauty of the biotic community. it is wrong when it tends otherwise.” in this way, he diverged from Pinchot’s view of nature as resources to be managed for human use. He also referred to the ecological view of nature as “thinking like a mountain.” leopold died of a heart attack on april 21, 1948, while doing a control burn to manage his rural property. See also conservation biology; keystone species.

ponds, and lakes.

leopold,  aldo (1886–1948) American Ecologist, conservationist aldo leopold was one of the founders of modern environmental ethics. Born January 11, 1886, in Burlington, iowa, Rand aldo leopold spent much time exploring the natural world. He not only watched birds but counted them, an attitude that prepared him for a scientific view of nature. He was trained in the forestry school that Gifford Pinchot had started at yale University. Beginning in 1909, leopold worked for the U.S. Forest Service in arizona and new Mexico. Much of his responsibility was to shoot predators such as wolves. One of his transformative moments was when he shot a mother wolf with pups. He later interpreted his experience in this way:

Further reading

We reached the old wolf in time to watch a fierce green fi re dying in her eyes. i realized then, and have known ever since, that there was something new to me in those eyes—something known only to her and to the mountain. i was young then, and full of trigger-itch; i thought that because fewer wolves meant more deer, that no wolves would mean hunters’ paradise. But after seeing the green fi re die, i sensed that neither the wolf nor the mountain agreed with such a view.

aldo leopold Foundation. “the aldo leopold Foundation.” available online. URl: http://www.aldoleopold. org. accessed august 15, 2010. Knight, Richard l., and Suzanne Riedel, eds. Aldo Leopold and the Ecological Conscience. new york: Oxford University Press, 2002. leopold, aldo. A Sand County Almanac. new york: Oxford University Press, 2001. lorbiecki, Marybeth. Aldo Leopold: A Fierce Green Fire. Helena, Mont.: Falcon Press, 1996. newton, Julianne lutz. Aldo Leopold’s Odyssey. Washington, D.c.: island Press, 2006.

He then began to develop the modern practices of wildlife management, which recognizes the important role of predators in ecological communities. He developed these ideas when he joined the faculty of the University of Wisconsin in 1933.

lichens  lichens are a mixture of two very different kinds of organisms: fungi and single-celled photosynthetic organisms.

347

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348 lichens  348 ●●

●●

The photosynthetic cells (phycobionts) are usually green algae of the kingdom Protista; the genus Trebouxia is the phycobiont of about 40 percent of lichen species. Cyanobacteria, usually of the genus Nostoc, may also be associated with fungi in lichens. Only about 8 percent of lichens have cyanobacterial phycobionts. It is the phycobionts that give lichens their diverse and often brilliant colors. Many different species of fungi (mycobionts) participate in the lichen symbiosis. About 20 percent of all fungal species (40 percent of the sac fungi) are lichen mycobionts. Almost 98 percent of lichens have sac fungus mycobionts.

Each lichen is a mutualistic association, and since they grow and reproduce as single individuals, they can be considered examples of symbiogenesis. Both partners benefit from the association: ●●

●●

Lichens can withstand severe conditions of drought, cold, and heat, because the fungus shields the algae from sunlight when conditions are too dry, cold, or hot to allow photosynthesis. For example, some lichens live on rock surfaces and in the nearly barren lands of the far north; reindeer lichens (Cladina spp.) are in fact abundant enough that reindeer graze upon them. The fungus also absorbs and retains water that may be briefly available from rain or fog. Because of the protection provided by the fungus, the algae can live in places where no other algae can survive. Fungi require a source of organic molecules as food. The algae provide food to the fungi. Therefore these fungi can live in places where no other fungi can survive.

Although the fungus strands penetrate and occasionally destroy the photosynthetic cells, the photosynthetic cells reproduce rapidly enough to maintain the symbiosis. The ability to survive on bare rock surfaces is the reason that lichens were among the earliest organisms to live on dry land. Because the fungi determine the structures of lichens, lichens are classified as fungi. The phycobionts, however, are classified independently. Both phycobionts and mycobionts can be cultured independently, but they do not grow independently in nature. Each phycobiont species can be associated with different fungus species, and each mycobiont species can be associated with different algal species.

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first entry The fungus strands form the structure of the lichen body; the algae are sandwiched between and intermingled with the strands. Lichens are most commonly crustose (forming a crust like paint), foliose (leaflike), or fruticose (appearing to have branches) (see figure). Like corals that have photosynthetic cells in their tissues, lichens spread their phycobionts out into a layer that can absorb the maximum amount of sunlight. Lichens usually disperse to new locations either by fragmenting into smaller pieces when they are dry or by forming and releasing small structures in which phycobiont cells are wrapped in mycobiont strands. In some cases, the mycobionts produce spores as if they were free-living fungi. The spores germinate into a new fungus in a new location, where they must find a suitable phycobiont if they are to survive. Lichens are dependent upon the absorption of nutrients from dust and rainwater. As a result they absorb a great deal of air pollution from both sources. They also have no deciduous parts and cannot shed tissue that may be damaged by pollution. Lichens are

Lichens, such as these from the Black Hills of South Dakota, have single-celled “algae” inside a fungus structure. The resulting structure is a mutualistic association between two species.  (Stanley A. Rice)

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life history, diversity of  349 therefore sensitive to air pollution, some more than others. Lichens are frequently studied as biological monitors of air pollution in natural habitats. See also bacteria; fungi; mutualism; protists. Further Reading Esseen, Per-Anders, and Karl-Erik Renhorn. “Edge effects on an epiphytic lichen in a fragmented forest.” Conservation Biology 12 (2008): 1,307–1,317. Gargas, A., et al. “Multiple origins of lichen symbioses in fungi suggested by SSU rDNA phylogeny.” Science 268 (1995): 1,492–1,495. Lesica, Peter, et al. “Differences in lichen and bryophyte communities between old-growth and managed second-growth forests in the Swan Valley, Montana.” Canadian Journal of Botany 69 (1991): 1,745–1,755. Lutzoni, François, et al. “Major fungal lineages are derived from lichen symbiotic ancestors.” Nature 411 (2001): 937–940. Nash, T. H., ed. Lichen Biology. New York: Cambridge University Press, 1995. Pettersson, Roger B., et al. “Invertebrate communities in boreal forest canopies as influenced by forestry and lichens with implications for passerine birds.” Biological Conservation 74 (1995): 57–63. Rose, C. I., and D. L. Hawksworth. “Lichen recolonization in London’s cleaner air.” Nature 289 (1981): 289–292. Sancho, L. G., et al. “Lichens survive in space: Results from the 2005 LICHENS experiment.” Astrobiology 7 (2007): 443–454. Sillett, Stephen C., et al. “Dispersal limitations of epiphytic lichens result in species dependent on old-growth forests.” Ecological Applications 10 (2000): 789–799. Yuan, X., et al. “Lichen-like symbiosis 600 million years ago.” Science 308 (2005): 1,017–1,020.

life history, diversity of  Life history refers to the patterns of growth, reproduction, and death in organisms. Differences in life history are among the most important differences among species. Certain sets of life history characteristics, called strategies, function successfully together; however, seldom does an environment or habitat have a single best life history strategy. Below are examples, rather than a complete overview.

Consider this simplified example of plant growth. The plant uses its food resources to produce leaves; this is an investment, because the leaves then allow the plant to make more food. However, it must also produce stems, to supply the leaves with water and to hold the leaves up higher than the leaves of other plants, and roots, which obtain water and minerals for the leaves. If the plant allocates most of the food that the leaves make into the production of new leaves, neglecting its stems (for example, by making them flimsy) and producing few new roots, it may be able to grow very fast but will probably be unable to survive the winter. This is part of the life history strategy of a weed; it grows fast because it invests all its resources in growth rather than maintenance. If the plant allocates more of the food made by the leaves into the production of wood and perennial roots, it will grow more slowly but will be able to maintain a system of trunk, stems, and roots for many years. This is part of the life history strategy of a tree. Tree species differ from one another in their life history patterns. Trees that grow quickly after an ecological disturbance (early successional trees) produce cheap wood and do not live very long; trees that grow slowly and dominate old forests (late successional trees) produce expensive wood and live a long time. The wood of early successional trees contains more of the large vessels (pores) that transport water and allows rapid growth than does the wood of later successional trees (see figure on page 350). An animal example of different life histories would be to compare a butterfly and a turtle. The butterfly has wings that cannot repair themselves, but this does not matter, as the butterfly dies very quickly. The turtle, however, has a body built to last. Consider the interactions of organisms with other species. If the plant produces lots of defensive chemicals in its leaves, it cannot grow as fast, since it has expended many of its resources on defense rather than growth. Often, the plants that live longer produce leaves that are more toxic, while short-lived plants have less toxic leaves. If insects attack, the plant with the defenses will not suffer as great a loss of leaf material; however, the faster-growing plant may rapidly grow back after the insects attack it. The plants and animals have coevolved in response to one another.

Physiology and Growth

Reproduction

Organisms have limits. In particular, they have limited resources and must allocate those resources among functions. Frequently, to do more of one thing means to do less of another. Organisms accordingly invest resources into those functions that will allow them to obtain more resources and to reproduce more successfully.

Investment and allocation patterns can allow organisms to grow large and strong, but if they do not reproduce, natural selection eliminates their adaptations. The timing, amount, and pattern of reproduction are important parts of life history; in fact, they make the growth and physiology worthwhile from an evolutionary viewpoint. Reproductive

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350 life history, diversity of  350

first entry

tinuum of life histories. There are no mammals that produce thousands of offspring, but mice produce many offspring and have brief lives, in contrast with elephants, which live for 50 to 70 years and produce fewer offspring. There are no birds that produce thousands of eggs, but mourning doves can produce several broods in a season and live only a couple of years, in contrast to the few, large eggs of the longlived ostrich. There are no trees that live only a year, but some trees have relatively short lives and produce many small seeds; for example, the tree-of-heaven (Ailanthus altissima) grows fast, produces many small seeds, and dies after a few decades, in contrast to an oak tree that can live for centuries, producing relatively few large acorns throughout that time. One example of the trade-off between size and numTrees (such as sycamores, sweet gums, box elders, and cottonwoods) that grow soon after ecological disturbances have wood with more pores ber of offspring is found among than do trees that grow later (such as black oaks, water oaks, post oaks, fishes. Fishes that are raised in black hickories, and pecans). Pores are xylem vessels and deliver more hatcheries have a higher survival water to the tree, allowing rapid growth.  (Based on unpublished data from rate than fishes that hatch in the Stanley A. Rice) wild. As a result, small eggs are more likely to result in surviving offspring in a hatchery than in the wild. The ­investments are, therefore, more important than surrecent practice of supplementing wild fish populavival. For example, when spiderlings hatch, they may tions with individuals grown in fish hatcheries has eat their own mother. therefore resulted in a reduction in the average egg Consider this simplified example of plant reprosize in wild fish species. duction. When the plant allocates its resources to The weed life history strategy has been labeled reproduction, it can either produce lots of small r, meaning that the populations of these species seeds or a few large ones. Fast-growing plants frespend most of their time in the rapid growth phase; quently produce many small seeds; as they store natural selection favors characteristics that help nothing, they die after a large burst of reproduction. them grow and reproduce rapidly. The tree life This is part of the life history strategy of a weed. history strategy has been labeled K, meaning that Plants that grow more slowly often produce fewer, the populations of these species spend most of larger seeds. Sometimes they save up resources for their time in the phase of high population density; years, then reproduce in a large burst (semelparous natural selection favors characteristics that help species), and sometimes they reproduce a little bit them compete with other individuals. The varievery year or every few years (iteroparous species). ables r and K, first used by ecologist Eric Pianka, The production of many small seeds is part of the come from the theoretical equation for population weed life history, while the production of fewer, growth. Ecologist Philip Grime proposed a system larger seeds is part of the tree life history. Animal in which plants (and other organisms) have three examples of the two extremes include some inverlife history strategies: C for competitive (similar tebrates that produce thousands of tiny eggs, and to K), R for ruderal (similar to r), and S for stress-­ humans that produce very few but very expensive tolerant, referring to organisms that grow slowly offspring. where resources are very limited or climatic condiBetween the “weed” and “tree” extremes and tions are extreme. their animal counterparts, there is a whole con-

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life history, diversity of  351 No single life history strategy is always better than another. The weed strategy and the tree strategy both work but in different ways. Both minnows and sturgeons and both mice and elephants successfully make their living in the world. Although no one life history is superior over others, certain environments may favor one strategy over another. ●●

●●

●●

The tundra has few weeds. The growing season is so brief and chilly that a plant could not grow rapidly enough to reproduce successfully after only one year. If the plant must survive the winter, in order to have two or more growing seasons, it must have adaptations such as strong stems or underground storage organs, which force it to have slower growth. Deserts may have many plant species with a weedy life history. The brief wet springtime of a desert is warm enough that many plants can, in fact, complete their growth and reproduction within a few weeks. These plants may be extremely small. This is not the only successful strategy for a desert plant. Cactuses store water, and desert bushes such as mesquite and creosote grow very deep roots that allow them to survive the dry season so that they can grow for many years. In areas such as a forest disturbed by fires or storms, many weeds grow. Their small seeds germinate into small seedlings, but there is little competition from other plants (most of which were killed by the fire or storm). The seedlings grow rapidly and reproduce soon; they complete their lives before the forest grows back. Once the forest has grown back, however, weedy species are at a disadvantage, since their tiny seeds could not grow well in the shade of the trees; now the K or C plants have the advantage.

Just as the human economy has evolved a great diversity of different ways of making a living, so the “economy of nature” has produced communities of plants and animals that make their living by means of many different life history strategies. Charles Darwin, following the lead of economist Thomas Malthus, noted that all organisms have the capacity to reproduce far in excess of the space and resources available. Darwin calculated that even a pair of elephants, if they bred as much as possible and all the offspring survived, could produce 19 million individuals in 750 years. The elephant represents the K end of the life history spectrum. Species at the r end of the spectrum have almost ridicu-

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lously large potential reproductive outputs, because the vast majority of their offspring die. If resources were unlimited and all offspring survived, a pair of houseflies could produce a population of 200 quintillion in five months and a pair of starfish could produce a population in 16 years as great as the number of electrons in the visible universe. A single bacterium, dividing every few minutes, could cover the Earth two meters deep in bacterial slime in less than two days. These organisms use their prodigious reproductive capacity only during brief times when resources are abundant. Organisms may increase or decrease their reproductive investments, depending on the immediate circumstances. During stressful years with inadequate resources, plants may produce fewer seeds, and animals smaller litters than during years of abundance. Adjustments can be made even after the next generation has been initiated. Under conditions of inadequate resources or pollination, plants may abort seeds or fruits. Spontaneous abortions are common in animals. In golden hamsters, a mother may even eat some of her own offspring if resources become inadequate. The life history of Homo sapiens and its immediate evolutionary ancestors is a particularly striking example of the K strategy. One of the major features of the evolution of the hominin lineage has been the prodigious increase in brain size; both relatively and absolutely, the modern human brain is outstanding in the animal kingdom. The first hominins to experience the evolutionary explosion in brain size were the early members of the genus Homo. Once large brains and their associated intelligence had evolved, they provided an advantage that justified their tremendous cost. Much of this brain growth occurs during fetal development and continues well past childhood. A human fetus, because of its large head, is born only with great difficulty. The passage of the head through the birth canal is the most prolonged, painful, and dangerous part of the birth process in humans. The birth canal cannot evolve to be much larger than it is, for otherwise a woman would not be able to walk. Therefore natural selection favored an increase in brain size but also put constraints upon it. The evolutionary solution to this dilemma was for the fetus to be born early, while the head was still small. In chimpanzees, the ratio of the gestation period (in weeks) to the total lifespan (in years) is about 0.8. If the human gestation period were the same length of time, relative to the life span, as it is in chimp primates, the human gestation period would be about 15 months and birth would be impossible (see table on page 352). By being born after nine months’ gestation, the baby’s head is small enough to

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352 life history, diversity of  352

first entry

Life Histories of Primates Characteristic

Lemur

Macaque

Gibbon

Chimp

Human

Ratio of gestation (weeks) relative to life span (years)

1

1

1

0.85

0.54

Infancy*

6%

8%

10%

10%

10%

Subadult*

11%

12%

17%

16%

14%

Adult*

83%

80%

73%

74%

76%

Years to end of reproductive life

18

24

30

40

50

Post-reproductive years

0

0

0

0

20

Ratio of post-reproductive years to life span

0

0

0

0

0.3

*Percentage of years to end of reproductive life

emerge, but the baby is still, in many ways, a fetus, having undergone only a little over half of the prenatal development that is normal for primates. This is why babies are born in such a helpless condition. As a result, they require continual protection and care. The level of reproductive investment of a human mother is among the highest in the animal kingdom, for not only is the baby large when born (up to one-tenth the mother’s weight), but it requires nursing and continual attention. The consequences do not stop there. Human mothers can take care of their babies by themselves, but the baby is much more likely to survive and be healthy if taken care of by both parents, and even more so with the help of grandparents. A human male would be able to produce more offspring by having multiple mates, but might produce more surviving and healthy offspring by staying home and helping out with just one mate. This may be the evolutionary basis for the human family unit. The cascade of evolutionary causation is: selection for big brains → selection for premature births → selection for intense parental care of offspring → selection for parental cooperation in child care. Human societies have a full range of social structures, from monogamy to harems (one male with multiple females). The family unit has not always proven to be the arrangement that results in the greatest fitness in humans. Frequently, the allocation of resources that is best, from the viewpoint of the parents, is not the best from the viewpoint of the offspring. This concept was called parent-offspring conflict by evolutionary biologist Robert Trivers. It is a conflict of interest rather than open violence. Consider the example of reproductive rates. It may be in the interests of the parents to produce numerous offspring, as a hedge against environmental unpredictability. But the existing offspring would benefit most from hav-

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ing all of the parents’ attention and resources go just to them. This conflict of interest can play itself out in different ways: ●●

●●

●●

●●

Hormonal conflict. The fetus produces an insulinlike growth factor that encourages the allocation of more resources to the fetus, even at the expense of the mother’s health. The mother, however, has a gene that inactivates the fetal gene for this growth factor. Emotional and physical conflict among siblings. A child often displays jealousy when a new baby sibling arrives. In many bird species, the bigger chicks push smaller chicks out of the nest or even peck the smaller ones to death in full view of the parents. Deception. The offspring benefit from being deceptive about their needs, for example by signaling a greater degree of hunger than they are actually experiencing. Marsupial life history. The babies of marsupial mammals are born at a very early stage of development and must crawl from the birth canal to a pouch, where they attach to nipples. Most of their fetal development occurs in the pouch, not the uterus. In placental mammals, most of the development occurs in the uterus, and when the baby is born, it is usually nearly ready for survival. The marsupial life history may provide an advantage for the mother under conditions of variable resource availability. In times of scarcity, when raising offspring would be a significant burden and possibly dangerous to the mother, the mother marsupial can simply discard the offspring. Except under special circumstances, however, placental mammals cannot abort their own offspring.

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life history, diversity of  353 no physiological constraints on life span. A leukemia patient, Henrietta Lacks, died in 1951 but some of her “HeLa” white blood cells are still alive in medical laboratories all over the world.

From the viewpoint of the offspring, the marsupial life history is never an advantage; a womb is always safer than a pouch. Most animals are either males or females. In many fishes, however, an individual animal can change from one gender to another. This makes the life histories of these fishes very unusual. Sexual selection favors large males; therefore a small, young male would be at a disadvantage in competition with the few, large, dominant males. In these fishes, there are many small and medium-sized females. Some females, when they become large, change into males. These individuals are maximizing their reproductive output by being female when they are young and small and male when they are older and larger.

The inescapable conclusion is that natural selection has actually favored organisms that die. The reason seems to be that reproduction itself poses a survival cost on the parent. In order to reproduce more, organisms must take metabolic and behavioral risks. ●●

Death Evolution cannot produce immortal organisms. Every organism runs the risk of accidents leading to injury or death. Furthermore, mutations accumulate in the chromosomes of organisms. Radiation in the environment and even the very oxygen in the air induce mutations. The longer an organism lives, the greater risk it runs of death. It is quite clear, however, that cells and organisms ought to be able to live much longer than they actually do: ●●

●●

Animal populations contain genetic variability that would allow an increased life span. Researchers have found the indy (“I’m not dead yet”) gene in the fruit fly Drosophila melanogaster and a similar gene in the roundworm Caenorhabditis elegans. This gene extends life span by reducing metabolic rate. Fruit flies have been experimentally bred that have life spans twice as long as those of wild fruit flies. Germ (germline) cells in animals and most plant cells are potentially immortal. Early in embryonic development, animal cells differentiate into somatic cells, which become nonreproductive tissues and organs and which eventually die, and germ cells, which are passed on to the next generation in the form of eggs, sperm, or spores. (These are not to be confused with pathogens such as bacteria, which are popularly called germs.) Among the somatic cells, stem cells may also be potentially immortal. White blood cells, the basis of the immune system, have a much greater capacity to reproduce than most other cells of vertebrates. Cancerous white blood cells (as in leukemia) may have

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Metabolic risks. A higher metabolic rate may allow greater reproductive output. Animal species with faster metabolism do not live as long as species with slower metabolism. Experimental breeding of fruit flies has shown that the longer-lived strains have lower metabolism and have lower reproductive output. Food restriction can cause an individual, whether a fly or a human, to live longer. An exception is that most bats have rapid metabolism and long life spans. Behavioral risks. An animal that takes risks may be injured but may reproduce more than a cautious animal.

The expense of producing a long-lived body may so greatly impair reproduction that natural selection will favor shorter-lived organisms, if this allows them a greater total reproductive output. For animals, the continual renewal of components that are damaged, such as the beak of a woodpecker, would be enormously expensive—and that expense would come at the cost of reproductive fitness. Since very old individuals would be rare even in a population of biologically immortal animals (most would already have died from accidents), natural selection has not favored the evolution of adaptations that prolong the lives of very old individuals. The reptiles with some of the longest life spans are turtles, and the mammals with some of the longest life spans (aside from humans) are porcupines, both of which are relatively sluggish and well protected from injury. Therefore natural selection will not eliminate mutations that bring harm only to older individuals. One reason is that, in most populations, few individuals live to be old. Another reason is that even those individuals that do live to be old will have very little reproductive life left ahead of them. Scientists such as biologist Peter Medawar have pointed out that pleiotropic genes, which have more than one effect, may be responsible for aging (senescence). Such genes may enhance fitness in

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354 life history, diversity of  354 younger individuals even if they also reduce the survival of older individuals. Those few organisms that do live for a very long time (all of them trees) either possess very expensive adaptations or else grow slowly. An example of the former is the giant sequoia (Sequoiadendron giganteum), many of which are more than 2,000 years old and which produce very thick fire-retardant bark. An example of the latter is the bristlecone pine (Pinus longeava) in California. Many of these pines are more than 4,500 years old but have grown less than 30 feet (10 m) tall during that time, because of the harshly cold and dry environment in which they live. Many of the world’s oldest and largest trees, such as the ancient lime (linden) trees of England and Germany, are not actually the original trees but are the outgrowth of branches or roots that the original tree produced, from which the original trunks have been lost. Virginia opossums (Didelphus virginiana) on the mainland of the southeastern United States have evolved in the presence of predators, but on Sapelo Island there are no predators. The island opossums have evolved delayed old-age senescence (as measured by the breaking time of their collagen fibers). They also reproduce relatively more in their second year of life and less in their first year, compared to mainland opossums. This pattern suggests that under more dangerous conditions, in this case when predators are present, natural selection favors earlier reproduction and favors (or at least does not disfavor) more rapid aging. Humans are unusual not only in the enormous amount of care they give to offspring but also in the enormously prolonged post-reproductive life span. In most animals, once reproduction is finished, the individuals die. A comparison among different primates shows that chimps and humans have slightly longer infancy and juvenile periods, relative to the life span up to the end of reproduction, than do other primates. But the most striking difference is the human post-reproductive period, which adds another one-third to the life span (see table on page 352). In humans, the post-reproductive life span can be almost as long as the juvenile and reproductive life spans combined. The human with the longest life span verified by a birth certificate was Jeanne Calment, who died in Arles, France, at the age of 122 in 1997. The explanation usually given for this is that the older individuals possess a wealth of knowledge that can prove immensely valuable to individual families and to the tribe as a whole. This body of knowledge can be so large that it takes a lifetime to teach. A bird can learn its repertory of songs and how to forage in a single season, but human

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first entry knowledge fills a lifetime longer than the reproductive life span. Since the invention of writing, this knowledge can be passed from one generation to another impersonally, but through most of human evolutionary history old people, not books or databases, were the repository of tribal knowledge, especially about the uses of the many wild species. Science writer Natalie Angier calls grandmothers the “Alexandrian libraries for preliterate tribes.” This cultural knowledge would directly benefit the wise old person’s descendants. Evolutionary scientists have had a particularly difficult time explaining the origin of menopause. Many evolutionary scientists consider menopause to be a nonadaptive side effect of the evolution of human life history. Menopause evolved accidentally, and since very few old women survived in prehistoric societies, there was no selection against menopause. In contrast, some evolutionary biologists, such as Kristin Hawkes, say that menopause is adaptive. Dubbed the “grandmother hypothesis,” this theory says that a woman may have greater inclusive fitness by devoting herself to the nurture of her grandchildren than by continuing to have her own children, once she is old. This may explain why older women seldom reproduce, but how could natural selection have favored the sudden enforced cessation of reproduction? The reason may be that continued reproduction, even continued reproductive ability, in older women may present physiological risks: ●●

●●

Breast cancer. There is a correlation between the number of menstrual cycles and the risk of breast cancer, since the hormones that the woman’s body produces after ovulation (estrogen and progesterone) stimulate breast cell division. Continuation of menstrual cycles into old age could therefore represent a risk. Some evolutionary scientists conclude from this that menopause reduced breast cancer incidence in older women. Other evolutionary scientists point out that women have far fewer menstrual cycles in primitive societies than in civilized societies, because they were usually pregnant or lactating. Breast cancer incidence is much lower in societies with high reproductive rates. In early human societies, even old women would not have had enough menstrual cycles to create a risk of breast cancer. Difficulty during childbirth. An older woman would be at greater risk of difficulty during childbirth and would be less likely to live long enough to nurture her own child to maturity.

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Linnaeus, Carolus 355 Older men experience reduced sperm production but no discrete point in their lives at which sexual reproduction ceases. This may reflect the fact that sperm production is less risky than childbirth. Natural selection has favored, under some conditions, characteristics (including a brief life span) that go with the r life history strategy. But natural selection has also favored limited life spans for species with the K life history strategy. The short lives of weeds and mayflies, therefore, just like the long but finite life of a human, are not evolutionary shortcomings but are products of natural selection. Ecological communities nearly always consist of species with very different life histories, each one of them specializing in a different way of making a living: living rapidly in briefly available resources or surviving for a long time through times when resources are scarce. See also coevolution; natural selection; sexual selection; succession, ecological. Further Reading Charlesworth, Brian. “Fisher, Medawar, Hamilton and the evolution of aging.” Genetics 156 (2000): 927–931. Clutton-Brock, T. H. The Evolution of Parental Care. Princeton, N.J.: Princeton University Press, 1991. De Magalhães, João Pedro. “Why are we allowed to age?” Available online. URL: http://senescence.info/evolution.html. Accessed April 20, 2011. Elgar, Mark A. “Evolutionary compromise between a few large and many small eggs: Comparative evidence in teleost fish.” Oikos 59 (1990): 283–287. Ellison, P. T. On Fertile Ground: A Natural History of Human Reproduction. Cambridge, Mass.: Harvard University Press, 2003. Hawkes, Kristin. “Grandmothering, menopause, and the evolution of human life histories.” Proceedings of the National Academy of Sciences USA 95 (1998): 1–4. Hrdy, Sarah Blaffer. Mother Nature: Maternal Instincts and How They Shape the Human Species. New York: Ballantine, 2000. Kirkwood, Thomas B. L., and S. N. Austad. “Why do we age?” Nature 408 (2000): 233–238. Medawar, Peter. An Unsolved Problem in Biology. London: H. K. Lewis, 1952. Trivers, Robert L. “Parent-offspring conflict.” American Zoologist 14 (1974): 249–264. Westendorp, R., and Thomas B. L. Kirkwood. “Human longevity at the cost of reproductive success.” Nature 396 (1998): 743–746. Williams, George C. “Pleiotropy, natural selection and the evolution of senescence.” Evolution 11 (1957): 398–411. ———. Sex and Evolution. Princeton, N.J.: Princeton University Press, 1975.

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Linnaeus,

Carolus  (1707–1778)  Swedish  Botanist Carolus Linnaeus was the Swedish botanist who invented modern taxonomic classification of biodiversity using Latin names. He was born on May 23, 1707, as Carl Linnaeus, and his family name was originally Linné; both of his names are Latinized versions. The Linnaean system brought organization into the exuberant world of biodiversity. Like many other important intellectuals in world history, Linnaeus showed little promise as a student. His father apprenticed him to a cobbler, which inspired Carl to go back to school and improve his grades. He studied medicine, but his passion, starting in his twenties, was to catalogue all the known species of organisms. Linnaeus was passionate about two other things as well. First, he was passionate about his own greatness. He wanted Princeps Botanicorum (prince of botanists) on his tombstone and considered his method of classification to be “the greatest achievement in the realm of science.” Second, he was passionate about sex. He used a sexual system, based upon anthers and pistils, to classify plants. But he went further. His terms for the anatomy of mollusks included vulva, labia, pubes, anus, hymen, even though the structures he described had no relation to the corresponding parts of human anatomy. Among the names he gave plants were Clitoria, Fornicata, and Vulva. His descriptions of plant reproduction were very florid. He described the parts of the flower, correctly, as sexual organs, but went further: “The flowers’ leaves serve as a bridal bed . . . the bridegroom with his bride might there celebrate their nuptials . . . then it is time for the bridegroom to embrace his beloved bride and surrender himself to her.” Predictably, some scholars disliked Linnaeus’s sexual classification system. A professor in St. Petersburg, Johann Siegesbeck, wrote that God would not have created the natural world based on this “shameful whoredom.” Linnaeus’s response was to name a small, ugly weed Siegesbeckia (now Sigesbeckia) in his honor. In his personal life, Linnaeus was very conservative, despite his florid writings. The order that Linnaeus brought into biology by this system, however, inspired nearly all scientists. In particular, a number of young men were his disciples and explored all over the world at great personal risk to find new species of plants to classify with the Linnaean system. Peter Kalm explored Canada during the height of the tensions between France and England; Frederik Hasselquist explored Egypt; Peter Osbeck went to China; Pehr Löfling went to Spain; and Lars Montin went to Lapland, all spending their own fortunes to collect plants and send them back to Linnaeus. Though not a disciple of Linnaeus,

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356 living fossils  356 ­ otanist John Bartram went into the wilderness of b the American southeast looking for plants and was one of the first white visitors to the Cherokee tribe. Another reason that Linnaeus’s system caused a flurry of botanical exploration is that his system allowed naturalists to name plants after themselves or other naturalists whom they admired. The genus name of a small herbaceous plant of the north woods, Linnaea borealis, honors Linnaeus, and the species name of Abutilon theophrasti, the velvetleaf weed, honors the Greek philosopher Theophrastus. Both amateur naturalists and professional scientists yearned for the immortality that would result. Even though he did not even think about evolution, Linnaeus included in his writings some intermediate forms based on hearsay. He was willing to believe them because he accepted the concept of the Great Chain of Being (scala naturae), in which God had not only created every type of creature but all of the intermediates between them. For example, he wrote about strange species of humans such as Homo ferus, a feral human on all fours and unable to talk, and Homo caudatus, man with a tail. Linnaeus has gained scientific immortality, even though his classification system has become unwieldy and may possibly be superseded by an evolutionary (phylogenetic) system. Linnaeus died on January 10, 1778. See also biological classification; cladistics.

first entry are few living fossils among the flowering plants, teleost bony fishes, or tetrapod vertebrates. Horseshoe crabs have changed little for millions of years (see figure), and there are few species of them today. Within those groups, the living fossils resemble some of the most ancient species. Amborella trichopoda, which is often considered a living fossil flowering plant, is also the modern species that most closely resembles the ancestor of all flowering plants. The lake sturgeon, often considered a living fossil, is one of the most primitive of the ray-finned fishes, and tuataras represent one of the most ancient reptile lineages. There is no precise definition of a living fossil. Cockroaches are often called living fossils because representatives of the order Dictyoptera can be found in deposits as old as the Carboniferous period. However, it appears that, although the cockroach genus Cryptocercus appears to be very ancient, most modern cockroach species are not living fossils. It is often impossible to determine whether a species represented in the fossil record is the same as a modern species, no matter how closely it resembles it. An online search for living fossils will connect to dozens of creationist Web sites. They claim, based

Further Reading Conniff, Richard. “Happy birthday, Linnaeus.” Natural History, December 2006, 42–47. Gould, Stephen Jay. “Ordering nature by budding and full-breasted sexuality.” Chap. 33 of Dinosaur in a Haystack: Reflections in Natural History. New York: Harmony, 1995. Schiebinger, Londa. “The loves of the plants.” Scientific American, February 1996, 110–115. ———. “The Private Lives of Plants: Sexual Politics in Carl Linnaeus and Erasmus Darwin.” In Science and Sensibility: Gender and Scientific Enquiry 1780–1945, edited by M. Benjamin, 121–143. New York: Oxford University Press, 1991.

living fossils  Living fossils is the popular term

given to modern multicellular organisms that closely resemble forms that have been known from the fossil record for at least several million years (see table on page 357). Most of them, such as the ginkgoes and dawn redwoods in China, persist in habitats that have not changed very much for millions of years. Most are members of evolutionary lineages that have not rapidly diversified; for example, there

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Modern horseshoe crabs (bottom) closely resemble the fossils of their ancient ancestors (top).  (David Goehring [top] and U.S. Geological Survey [bottom])

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living fossils  357 “Living Fossil” Plants and Animals Organism

Taxonomic Category

Relatively Unchanged Since

Horsetail (Equisetum)

pteridophyte plant

Permian period

Wollemi pine (Wollemia)

gymnosperm seed plant

Jurassic period

Dawn redwood (Metasequoia)

gymnosperm seed plant

Pliocene epoch

Ginkgo (Ginkgo)

gymnosperm seed plant

Jurassic period

Monkey puzzle (Araucaria)

gymnosperm seed plant

Triassic period

Cycad (Cycas)

gymnosperm seed plant

Permian period

Amborella

flowering plant

Cretaceous period

Horseshoe crab (Limulus)

arthropod

Triassic period

Fairy shrimp (Triops)

arthropod

Silurian period

Lampshell (Lingula)

brachiopod

Silurian period

Giant termite (Mastotermes)

insect

Permian period

Coelacanth (Latimeria)

lobe-finned fish

Cretaceous period

Lake sturgeon (Acipenser)

bony fish

Jurassic period

Tuatara (Sphenodon)

reptile

Jurassic period

Plants

Animals

upon a profound misunderstanding of evolution, that because every species must have changed over time, living fossil species disprove evolution; that is, if anything changed, then everything must have changed. They thereby disregard the fact that, during their time on Earth, living fossil species have experienced long periods of stabilizing selection in

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connection with the stable environments in which they live. They also disregard the abundant evidence that only a tiny fraction of species that exist today can remotely be described as living fossils. Living fossils are frequently endemic species that have a high conservation priority. See also endemic species; natural selection.

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M maathai,  Wangari (1940–2011) Kenyan Con-

radation. She organized local women volunteers to plant trees in nairobi, grown from seeds of local forest species rather than the imported species that were commonly used for tree plantations. She married Mwangi Mathai, who won a seat in the Kenyan parliament. When he sued for divorce because of her outspoken devotion to political issues, he insisted she drop his name, but instead she changed it to Maathai. She wanted to run for parliament herself, and she resigned from the university to do so but was opposed by the autocratic leader Daniel arap Moi. She was left without home or employment. about this same time, Maathai’s tree-planting activity caught the attention of the norwegian Forestry Service and then the United nations, which provided support for her volunteers to continue planting trees, which led to the formal beginning of the Green Belt Movement. But the Green Belt Movement did more than plant trees. When she discovered that Moi’s government planned to use nairobi’s large public park to build a private business complex, Maathai led protests. Moi denounced her and her associates as crazy and even accused her of masterminding an aphid infestation. When she discovered that she was on an assassination list of government enemies, she organized media protests and barricaded herself in her house until government forces broke in and arrested her, charging her with treason. By now, Maathai’s struggle had gained much international attention. in 1992, eight american senators, including al Gore and edward Kennedy, warned Moi that relations with the United States would be severely harmed if he pursued his unsubstantiated accusations. Maathai continued leading protests, during which she was beaten by police, until all political prisoners were released.

servationist Wangari Muta Maathai (see photograph on page 359) founded the Green Belt Movement in Kenya. this movement enlisted thousands of Kenyan women in an effort to plant trees and to campaign for the rights of poor women. the quality of life in rural Kenyan villages depends strongly upon the availability of forests, particularly for firewood. Maathai’s work, for which she received the nobel Peace Prize in 2004, showed that improving the lives of the poor is inseparable from conservation and reclamation. She was the first african woman, and the first environmentalist, to win the nobel Peace Prize. Wangari Muta was born april 1, 1940, in the rural village of ihithe. at a time when it was uncommon for girls to go to school, Muta attended a catholic missionary primary school and high school. Her superlative grades qualified her as one of about 300 Kenyans to attend college in the United States under a program sponsored by Senator John F. Kennedy, in 1960. She earned a bachelor’s degree in biology at Mt. St. Scholastica college (now Benedictine college) in Kansas and then a master’s degree in biology at the University of Pittsburgh. She returned to Kenya as a research assistant in veterinary science. She earned a Ph.D. in anatomy at University college in nairobi in 1971, where she became a senior lecturer, department chair, and an associate professor, the fi rst woman at nairobi to attain any of these positions. Wangari Muta’s political activism began with seeking equal rights for women faculty, but her leadership in local organizations associated with the United nations environment Programme (UneP) opened her eyes to realize that most of Kenya’s social problems were associated with environmental deg358

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mammals  359 best expressed in a statement she made to National Public Radio on September 27, 2007, where she indicated that watching a poor person cut down the last tree for firewood to cook her last meal is a situation we need to avoid by planting trees now. Maathai died in Kenya on September 25, 2011. See also ecosystem services; restoration ecology. Further Reading Green Belt Movement. “Wangari Maathai.” Available online. URL: http://greenbeltmovement.org/w. php?id=59. Accessed May 16, 2011. Maathai, Wangari. Unbowed: A Memoir. New York: Random House, 2006.

Wangari Maathai led thousands of Kenyan women to plant native trees in places where forests had been destroyed.  (United Nations Environment Programme)

When, in 1998, Moi’s government again attempted to expropriate public forest land (this time for a golf course), the Green Belt Movement, along with parliament members and international observers, protested and were attacked—but the visual images of the attack spread around the world. Then it happened again in 2001. This time, however, Maathai was released without charge. Maathai and her political supporters did well in the 2002 elections, when Moi lost power. She was elected to parliament and then appointed as assistant minister of the environment and natural resources. She was awarded the Nobel Peace Prize in 2004. She continued to lead environmental restoration and education programs, such as the United Nations Billion Tree Campaign that began in 2006. The Green Belt Movement has planted more than 30 million trees in Kenya. She gained world admiration for promoting conservation and tree planting as an essential component of democracy in nations where poor people suffer the most from environmental destruction. Maathai began the Green Belt Movement, not simply because she loved trees, but because she saw that trees were essential to the livelihoods of the poor: Trees prevented floods, soil erosion, and droughts and provided essential materials such as firewood. Maathai was not so much planting trees as empowering the poor people of Kenya. She had seen forested hillsides in the village where she grew up and freshwater in streams, and she saw the forests cut down and the streams dry up. Her passion may have been

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mammals  The class Mammalia consists of vertebrates that have live birth, hair, are warmblooded, and produce milk. Carolus Linnaeus classified mammals into one group and even invented the name, based on the Latin mammae, referring to breasts. Mammals also have four-chambered hearts and teeth clearly differentiated into incisors, canines, premolars, and molars. Mammals constitute a vanishingly small percentage of animal species—about 1 to 2 percent as many species as beetles—but are of intense interest to human observers. Characteristics of Mammals Some of the distinctive characteristics of mammals are explained below: ●●

●●

Live birth.  Monotremes such as the duckbilled platypus lay eggs. The eggs have rubbery shells and remain glued to the mother’s underside for incubation while she is in her burrow. In all other mammals, the embryo begins to develop into a fetus inside the uterus of the mother. In marsupial mammals such as opossums and kangaroos, the very young fetus is born and crawls out of the birth canal into the pouch, inside of which they locate and nurse from nipples. In placental mammals, a placenta develops in which nutrients and oxygen from the mother’s blood diffuses into the developing blood system of the fetus. Therefore placental fetuses remain inside the uterus far longer than marsupial fetuses. Hair.  Hairs are cylindrical structures made primarily of keratin, the same protein that makes up vertebrate skin, reptile scales, and bird feathers. Humans have about as many hair follicles per unit area of skin (about 1,500 per square inch or 250 per cm 2) as

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360 mammals  360

●●

●●

other mammals, but on most of the skin surface the hairs do not develop to full size. This produces the appearance of hairless skin in humans. Keratin is strong and lightweight. A single hair can hold almost a quarter of a pound (100 grams) of weight and stretch to twice its length before it severs. Cells in the hair follicle adhere to the growing hair shaft and die; the hair shaft grows from the base and consists of dead cells. Hair is an excellent insulator, holding pockets of air against the skin. Tiny muscles (arerectores pilorum; singular arrector pili) attach to each follicle and control the angle of each hair. When a mammal is cold, the muscles make the hairs stand straight up, holding warm air next to the skin. When a mammal is in danger, it may contract these muscles, allowing the vertical hairs to make it appear larger. On human skin surface that appears hairless, these muscles produce goose bumps. Goose bumps are therefore one of the vestigial characteristics of evolution. Warm blood.  Mammals and birds are warm-blooded, because they have the highest metabolic rates of all vertebrates. Mammals are endothermic (Greek for “heat from within”), which means they produce enough body heat to create a temperature that is usually warmer than the environment, and homeothermic (Greek for “same heat”), which means they regulate their body temperature at a relatively constant level. This allows mammals to have high metabolic rates even in cold environments or during winter. Milk.  Mammae, possessed by both males and females, are modified sweat glands that produce milk, a liquid with a high content of sugars and fats and used to feed newborns. Mammae do not develop in males except under unusual hormonal conditions, for example in starving men who suddenly have all the food that they can eat. In monotremes, the most primitive group of mammals, the mammae are scarcely more than milk glands on the abdomen. In marsupials and placentals, the mammae have nipples that deliver milk to newborns when sucked. Mammae swell during lactation. Uniquely among mammals, mammae of women store fats on a continual basis and function as indicators of fitness in sexual selection. The number of mammae on a female mammal is roughly proportional to the number of offspring she produces at one time. Some Australian rats have at least 22 nipples and

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first entry

●●

●●

may give birth to 17 pups at a time; in contrast, humans have two nipples and usually give birth to one child at a time. Hearts.  Mammal hearts have four chambers, which allow them to have two separate circuits of blood flow. The first circuit is the pulmonary circulation: Blood returns to the heart from throughout the body in veins, which deliver deoxygenated (dark) blood to the right atrium of the heart. The right ventricle pushes this blood to the lungs, where the red blood cells absorb oxygen and the blood becomes bright red. The red blood from the lungs enters the left atrium of the heart. The left ventricle pushes the red blood through the aorta and out into the rest of the body, which forms the second circuit, the systemic circulation. Mammal blood therefore flows in a figure 8: a pulmonary loop alternating with a systemic loop. This system allows mammalian blood to be well and quickly oxygenated, which allows mammals to have high metabolic rates. Birds have even higher metabolic rates than mammals and also have four-chambered hearts. Most reptiles, except for crocodiles and their relatives, have three-chambered hearts and a slower metabolism. Teeth.  Mammals have differentiated teeth. Incisors allow mammals to bite their food, canines allow them to tear it, and premolars and molars allow them to grind it. Reptiles, in contrast, have teeth that are all more or less alike. Modern birds have no teeth, although their ancestors had reptilian teeth. Not only does the differentiation of teeth allow mammals to have close control over the processing of food but allows the developmental basis for specialization to different diets. Grazing animals have large molars, allowing them to grind coarse plant materials such as grass; they may possess no canine teeth at all. Carnivores have large canine teeth that they use to capture and consume their prey (and to fight with one another). Rodents have incisors that grow continually, as they are worn down by piercing the tough outer coverings of fruits and seeds. Humans have teeth less differentiated than those of most mammals, reflecting their omnivorous diet.

Origin of Mammals Mammals evolved from synapsids, one of the lineages of reptiles. Many vertebrates have openings in the right and left temporal bones of the skull;

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mammals  361 synapsids have a single opening, unlike many other reptiles. One synapsid reptile of the late Carboniferous period was Dimetrodon, which had a huge sail of bony extensions along its back. Although Dimetrodon itself is unlikely to have been the ancestor of mammals, it may have shared a characteristic that may have been widespread among synapsids: warm blood. Dimetrodon may have used its sail to warm its blood in the morning (by absorbing sunshine) and cool it off in midday (by radiating heat through the skin surface). This may have helped Dimetrodon to be, while not homeothermic, at least partly endothermic. By the Permian period, the dominant lineage of synapsids was the therapsids (from the Greek for “nurse”). While earlier synapsids had a sprawling gait similar to that of modern reptiles, the therapsids had legs underneath the body, allowing them to run more rapidly. Scientists infer that a higher metabolic rate (and more efficient body heat production) was necessary for this way of life. Compared to earlier reptiles, therapsids had fewer skull bones, teeth that were more differentiated, and multiple sets of replacement teeth rather than just juvenile “milk teeth” replaced by adult teeth. One group of therapsids that survived the Permian extinction was the cynodonts (from the Greek for “dog teeth”), with teeth even more differentiated (doglike) than those of earlier therapsids. Small pits in the facial bones of cynodonts may have been openings for extensive blood vessels, and this has led some scientists to conclude that cynodonts were fully warm-blooded. Cynodonts such as Morganucodon and Sinocodon, which lived during the Jurassic period, represent nearly perfect “missing links” (actually not missing) between earlier synapsid reptiles and modern mammals. Morganucodon is considered one of the earliest mammals, even though it is intermediate between synapsid reptiles and modern mammals. The very fact that so many “missing links” have been discovered means that the line between reptiles and mammals is somewhat arbitrary. Like modern mammals, Morganucodon had juvenile milk teeth replaced by adult teeth; Sinocodon retained the ancestral reptilian pattern of multiple replacement sets of teeth. The intermediate status of the cynodonts is illustrated in three ways: ●●

Lower jaw. In early synapsid reptiles, as in modern reptiles, the lower jaw consists of several bones, one of which is the dentary bone; but in mammals the lower jaw consists entirely of the dentary bone. In cynodonts, the dentary bone was intermediate in size.

xviii+598_Biodiversity_F.indd 361

●●

●●

Ear bones. In early synapsid reptiles, as in modern reptiles, the inner ear has a single bone, the stapes, which conducts vibrations to the cochlea. The mammalian inner ear consists of three bones: the incus, which corresponds to the reptilian quadrate bone; the malleus, which corresponds to the reptilian articular bone; and the stapes. In cynodonts, these bones are intermediate between the upper jawbones of reptiles and the inner ear bones of mammals. In fact, juvenile opossums (genus Didelphis) have inner ear bones that closely resemble those of Morganucodon. Jaw joint. In early synapsid reptiles, as in modern reptiles, the quadrate bone articulates with the articular bone of the skull, but in mammals it is the dentary bone that articulates with the skull. This means that during the evolution of mammals, the location of the jaw joint had to change from quadrate-articular to dentary-skull. In cynodonts, both jaw joints were functional.

From the Carboniferous to the Triassic periods, synapsids were the dominant reptiles on the Earth, in terms of size and species diversity. By the end of the Triassic period, synapsids had become less abundant and were represented mainly by small individuals. The thecodont lineage of reptiles, which evolved into crocodiles, dinosaurs, and birds, became dominant. Most of the evolutionary history of mammals occurred during the Mesozoic era, alongside the dinosaurs. Though none was large or abundant, there were numerous species of mammals at that time. The dinosaurs were, on the average, larger and ruled the day, while most mammals were smaller and were probably most active at night. While carnivorous dinosaurs must have often eaten mammals, occasionally a large mammal would eat a small dinosaur. Scientists have found the fossil of a three-foot-long (1-m-long) Kepenomamus robustus mammal that had eaten a baby dinosaur 130 million years ago. By the Jurassic period, mammals had backbones and shoulders that allowed them to have a more flexible, mammalian way of running. Three major lineages of mammals survived by the Cretaceous period: the monotremes, the multituberculates, and the therians. The modern descendants of the Jurassic monotremes are the duck-billed platypus and the spiny anteater (echidna) of Australia and nearby islands (see photograph on page 362). Monotremes retain some primitive features shared by most (but not all) reptiles. For example, they lay eggs. They also possess, like reptiles, a common opening ­for

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362 mammals  362

The duck-billed platypus is one of the few surviving species of the monotreme mammal lineage.  (National Human Genome Research Institute)

feces, urine, sperm, and eggs. Monotreme mothers produce milk but do so from glands rather than from breasts. The multituberculate lineage resembled rodents and became extinct during the Oligocene epoch of the Tertiary period, perhaps due to competition with rodents. Other modern mammals evolved from the Jurassic therian lineage. Some Mesozoic mammalian adaptations have turned out to have unexpected consequences. Scientists infer that mammals at this time suckled their young, because newborn mammals did not have teeth and could not chew. It would therefore have been necessary that they possess the complex facial muscles that mammals now have, allowing newborns to suck, something that reptiles and birds cannot do. Much later, these facial muscles made the evolution of human speech possible. By the Cretaceous period, the therian lineage had already split into its two modern branches: the marsupials and the placentals. Since the developing embryo is genetically different from the mother, the mother’s body begins to launch an immune response against it. Marsupials and placentals have two different solutions to this problem. In marsupials, before the mother’s immune response can launch its attack, the embryo is born. The newborn marsupial has few developed external structures, except forelimbs, which it uses to crawl over the mother’s fur into the pouch (see figure). This hazardous journey eliminates unfit newborns. The infant marsupial continues its development inside the pouch, where the mammary glands are located. By the time it leaves the pouch, the young marsupial is ready to move about on its own, although it returns occasionally to the pouch for nursing. Placentals are characterized by the placenta, a structure vascularized by both the mother’s and the fetus’s blood vessels, allows the mother’s blood to come close to but not in contact with the fetus’s blood. This prevents the

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first entry mother’s body from launching an immune attack against the fetus. Therefore the fetus can stay inside the mother’s body until highly developed. When born, the offspring has a relatively high chance of survival. Marsupials and placentals differ in numerous other respects as well. Marsupials usually have more teeth than placentals; the Virginia opossum (Didelphus virginiana) has 50 teeth while humans have 32. Aquatic placental mammals, however, have a much larger number of teeth. The Cretaceous extinction caused the extinction of the dinosaurs (except for the bird lineage). When the dust settled, the surviving mammals encountered a world in which dinosaur competitors had been cleared away. Within 10 million years, during the Paleocene epoch of the Paleogene period, the modern orders of mammals and many that are now extinct had evolved. Because this was a time of rapid evolution, it is difficult to reconstruct those early steps, whether from fossils or from DNA. Although

A tammar kangaroo fetus nurses inside its mother’s pouch. Kangaroos are born in a very undeveloped state and must crawl from the birth canal to a nipple inside the pouch. A human forefinger provides scale.  (Geoff Shaw; department of zoology, University of Melbourne, Australia)

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mammals  363 all modern orders of mammals existed in the early Paleogene, the dominant animals were in families that no longer exist, and the representatives of modern orders did not look like their modern counterparts. That is, modern orders existed, but modern families and genera did not. In contrast, most of the genera of early Paleogene trees would have been recognizable to an experienced naturalist. In contrast to most mammals, most birds evolved into lightweight, airborne forms. There was, therefore, little direct competition between birds and mammals in the post-dinosaur world. One exception was in South America, where until only about 2 million years ago the largest vertebrate was a predatory phorusrhacid bird that stood almost 10 feet (three meters) tall.

Mammal Diversity There are or have been in the recent past about 5,000 genera of mammals. The surviving 1,135 genera contain about 4,700 species. This is far less than the almost one-and-a-quarter million species of insects, three-quarter million of which are beetles. Though mammals have less species diversity than insects or even nematodes, they are overwhelmingly important in natural ecosystems and in the human perception of nature. Many are large grazers or predators, and some species have large populations. Their activities can transform entire ecological communities. Almost 160 years ago, American naturalist Henry David Thoreau made numerous careful observations that allowed him to conclude that the main reason that oak trees grew up underneath pines was the activity of squirrels that buried the acorns. Grazing animals (harboring cellulytic bacteria in their digestive systems) transform a huge amount of plant material into wastes on which many insects feed and which cycle more rapidly through grassland ecosystems than would be the case with simple decomposition. Humans, being mammals themselves, are more fascinated by wild mammals than by any other group of organisms. This is especially true of the big ones, referred to as charismatic megafauna, a fact that conservation organizations know very well: They raise money to save pandas, not roundworms. The five species of monotreme mammals (see above) are the last survivors of the most ancient mammal lineage still in existence. The duck-billed platypus and four species of echidnas lay eggs and have a single cloacal opening. The adults are toothless. Male monotremes have spurs on their hind legs that can inject poison into other animals. There are about 315 species of marsupial mammals (see table on page 364). These include the 95 species of opossums, all of them in South America except for the Virginia opossum. These, together

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with the six species of shrew opossums and Dromiciops gliroides (which more closely resembles Australian marsupials), are the New World marsupials. There are many species of Australian marsupials. The red kangaroo (Macropus rufus) lives in arid regions of Australia and can be six to seven feet (two meters) tall and weigh 200 pounds (90 kg). Three other species of kangaroos are smaller and live in other parts of Australia. Kangaroos have adapted well to human activity, especially ranching. They are the ecological equivalent of placental mammals such as deer and cattle. Unlike cattle, kangaroos do not release methane during the digestion of coarse vegetation in their diet; instead they produce citric acid, which provides further energy to the animal rather than being a waste product. Thirty species of wallabies are small relatives of kangaroos. There are about 20 species of bandicoots, smaller than wallabies, which often live in forests. Because of their size, and because of their varied diet, they are the ecological equivalent of placental rodents. The Tasmanian devil Sarcophilus harrisii lives today only on Tasmania and resembles a stocky and ferocious placental dog. Wombats are medium-sized burrowing marsupials that eat underground vegetative matter. There are two species of marsupial moles that, like placental moles, are blind burrowers. The koala is a slow-moving marsupial that consumes almost nothing but eucalyptus leaves; its slow metabolism allows it to subsist on these leaves, which are toxic and offer little nutrition. Thylacines were called marsupial wolves because of their external resemblance to dogs; the last thylacine became extinct in captivity in the early 20th century. These examples clearly demonstrate that most surviving or recently extinct marsupials closely resemble placental mammals, even though they evolved as entirely separate evolutionary lineages. Modern placental mammals include the following groups (as well as others in the table on page 364). Carnivores (order Carnivora) (see photograph on page 365) have sharp canine teeth, sharp claws, and binocular vision, and most of them are predators. They also have carnassial teeth (the last premolars and the first molars) that are sharp and come together in a scissorlike fashion that tears meat. Cats, pinnipeds, and weasels are exclusively carnivorous, while raccoons and bears are omnivorous. Even the giant panda bear (Ailuropoda melanoleuca), which primarily eats bamboo, will eat eggs or insects if they encounter them. They range in size from the least weasel (less than an ounce, or 25 g) to the elephant seal (11,000 pounds, or 5,000 kg). Most carnivores are terrestrial, although otters spend a lot of time in the water. Pinnipeds, however, are poor walkers and live mostly in water. Their name (which means

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364 mammals  364

first entry

“feather foot”) refers to the webbing between their toes that promote swimming. Carnivores include: ●● ●● ●● ●●

Canids (dogs, wolves, foxes) Mephitids (skunks) Mustelids (weasels, otters) Procyonids (raccoons)

●● ●● ●● ●● ●●

Ursids (bears) Otariids and phocids (seals) and odobenids (walruses), the “pinnipeds” Felids (cats including lions, tigers, leopards, cheetahs) Herpestids (mongooses) Hyaenids (hyenas, which are not dogs)

Estimated Number of Species Within the Orders of Mammals Order

Common Name

Number of Species

Marsupials (New World) Didelphimorphia Paucituberculata Microbiotheria

opossums shrew opossums

95 6 1

Marsupials (Australia) Dasyuromorpha Peramelemorphia Notoryctemorphia Diprotodontia

Tasmanian devil bandicoots marsupial moles koala, wombat, kangaroos

73 21 2 117

Placentals Proboscidea Chiroptera Carnivora Perissodactyla Artiodactyla Cetacea Sirenia

elephants bats dogs, cats, seals, bears horses, rhinoceroses pigs, camels, cattle, deer whales, dolphins manatees

3 1,100 260 20 220 90 4

Insectivorelike and shrewlike placentals Afrosoricida Macroscelidea Scandentia Erinaceomorpha Soricomorpha

tenrec, golden moles elephant shrew tree shrews hedgehogs shrews, moles

51 16 20 24 420

Edentate placentals Tubulidentata Pilosa Cingulata Pholidota

aardvark anteaters, sloths armadillos scaly anteater

1 10 20 8

Rodentlike placentals Hyracoidea Rodentia Lagomorpha

hyraxes mice, rats, squirrels, beavers rabbits, pikas

4 2,280 80

Primatelike placentals Dermoptera Primates

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flying lemurs prosimians, monkeys, apes

2 430

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mammals  365 ●●

Carnivores, such as this Bengal tiger, have large sharp teeth that allow them to capture and tear the flesh of their prey.  (iStockPhoto.com) ●● ●●

Viverrids (civet cats, which are not cats) Euplerids (Madagascar fossas)

Cetartiodactyls are the cetaceans (order Cetacea) and even-toed ungulates (order Artiodactyla). ●●

Cetaceans (see photograph) have numerous adaptations that permit them to live entirely in water (all of them marine, except for four species of freshwater dolphins). The nostril (blowhole) is on top of the head, and the muscles contain a much greater amount of myoglobin, which holds oxygen, than those of other mammals. (Rabbit muscle may be 0.06 percent myoglobin by fresh weight, while some whale muscles are 6 percent myoglobin.) These adaptations allow cetaceans to dive deeply and for a long time. Their ears are adapted for hearing underwater, where sounds can travel for long distances. The blue whale (Balaenoptera musculus) is the largest animal that has ever lived: It can be over 100 feet (more than 30 m) in length and weigh 190 tons (more than 170 metric tons). Cetaceans feed either on plankton by baleen filters, as do the largest whales, or by hunting animals with their numerous teeth, as do the dolphins and smaller whales. The front legs of cetaceans are flippers, and they have no hind legs except for occasional evolutionary vestiges. Cetaceans live in complex societies and migrate thousands of miles. They communicate by songs that are highly structured and can be heard almost a thousand miles (over a thousand kilometers) away. Dolphins have larger brains than most other mammals.

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The artiodactyls are herbivores that browse on herbs and shrubs or graze on grasses. When they walk, the weight is primarily on the third and fourth toes (even-toed). They include pigs; camels; cattle, sheep, and goats; deer and antelope; hippopotamuses; giraffes; and pronghorns. Pigs are omnivorous, and their stomachs have only two chambers; fermentation of coarse plant material occurs in the caecum, a pouch in the intestine. In contrast, ruminants (deer, giraffes, pronghorns, cattle, sheep, goats, antelope, and camels) have several stomachs in the first of which bacteria break down cellulose, a process that is aided by regurgitation of the undigested roughage (the cud) for further chewing.

Few scientists seriously considered that cetaceans and artiodactyls were closely related until fossil transitional forms from the early Cenozoic era showed the relationship, which was confirmed by DNA comparisons. Manatees (order Sirenia) are, like the cetaceans to which they are not closely related, entirely aquatic, living in shallow waters rather than the open sea. They have front flippers and only remnants of hind legs. Odd-toed ungulates (order Perissodactyla) includes horses, tapirs, and rhinoceroses. Like artiodactyls, they browse or graze. Unlike artiodactyls, their legs put most of the weight on the third (middle) toe. In modern horses, the hoof is a single toe. They have simple stomachs; as in pigs, fermentation of coarse plant material in perissodactyls occurs in the intestine. Bats (order Chiroptera) are the only flying mammals, although several groups of mammals can glide. Bat wings, unlike bird wings, consist of a membrane

Cetaceans, such as this breaching whale, are fully adapted to marine existence.  (SeaTurtle.org)

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366 mammals  366 that connects elongated fingers; bat and bird flight represent an evolutionary convergence from separate nonflying ancestors. Most of the larger bats (also called flying foxes) and many smaller ones have large eyes and feed on fruit and pollen. The giant goldencrowned flying fox (Acerodon jubatus) has a wingspan of five feet (a meter and a half). Most of the smaller bats (about 70 percent of species) eat insects, which they locate using very high-pitched sounds. Their brains construct something like a visual map using sound, very similar to human sonar imaging equipment. Insectivorous bats, while relying primarily on sound for navigation, have rudimentary eyes and are not blind. Bats can form enormous colonies of a million or more individuals, which roost and nest in caves and emerge en masse at nightfall. A single cave can contain a million nesting bats, yet a mother can find her own offspring by distinguishing its vocalizations from those of others nearby. Rodents (order Rodentia) constitute 40 percent of mammal species (see photograph). They eat primarily seeds (including those stored by humans) and

Some rodents, such as this black-tailed prairie dog (Cynomys ludovicianus) from the badlands of South Dakota, form complex social networks.  (Stanley A. Rice)

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first entry other plant material. Their two long incisor teeth in each jaw are very sharp and allow them to penetrate some of the hardest seeds. These teeth continually grow, and rodents continually wear them down. They range in size from the African pygmy mouse (Mus minutoides) at a quarter of an ounce (seven grams) to the South American capybara (Hydrochoerus hydrochaerus) at 180 pounds (80 kg). Rodents include mice, rats, squirrels, chipmunks, gophers, porcupines, beavers, and guinea pigs. In contrast to the rodents, the rabbits, hares, and pikas (order Lagomorpha) have four continually growing incisors in their upper jaws. Hyraxes (order Hyracoidea) look like small rodents but are more closely related to elephants. Primates (order Primates) usually have binocular (stereoscopic) vision and opposable thumbs. They have arboreal adaptations, for example the ability to jump or swing among branches, even if they do not live in trees. Primates have the largest brains relative to body size of any order of mammals. Many have three-color vision, which is useful in identifying fruits amidst leaves; primates rely on vision much more than on other senses for locating food. They range in size from the pygmy mouse lemur (Microcebus myoxinus) at one ounce (30 g) to the mountain gorilla (Gorilla beringei) at 440 pounds (200 kg). The Strepserrhini (“curly-nosed”) primates include the lemurs, aye-ayes, and lorises. The Haplorrhini (“dry-nosed”) primates include the tarsiers, the platyrrhines (“flat-nosed”) New World monkeys, and the catarrhines (“downward-nosed”) Old World monkeys and apes. New World monkeys include capuchin, howler, and squirrel monkeys. Old World monkeys include macaques and baboons. Apes include gibbons, orangutans, gorillas, chimpanzees, and humans. Humans are most closely related to the chimpanzee-bonobo lineage, from which they separated just more than 5 million years ago. The colugos (order Dermoptera) used to be considered primates. They have large surfaces of skin between all of their limbs and are the best gliding mammals. Elephants (order Proboscidea) consist of only three species (two in Africa, one in Asia) but extinct mammoths, mastodons, and gomphotheres were close relatives of elephants. They are remarkable for their long noses, with which they can manipulate food and drink water, and for their long canine teeth, curled into tusks. They are the largest terrestrial mammals. They consume a great deal of leaves, stems, and fruits, sometimes bulldozing small trees to do so. They contribute importantly to the reproduction of those very trees. Elephants have large brains and are nearly unique among nonprimate mammals in being able to recognize their own reflections. Elephants can remember the voices of other

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mammals  367 large front legs and consume small invertebrates that fall into the burrows. They can dig toward animals whose vibrations they can feel with their tubular snouts. They have small eyes but are not blind. The insectivore manner of living has evolved separately several times; therefore, the old order Insectivora has been split into Soricomorpha (shrews and moles), Scandentia (tree shrews), Afrosoricida (tenrecs and golden moles), Macroscelidea (elephant shrews), and Erinaceomorpha (hedgehogs). Some placental mammals retain presumed ancestral characteristics. The hyraxes, for example, are only primitively homeothermic; they must occasionally bask in the Sun in order to maintain a constant body temperature. Tree shrews have skeletal features and feeding habits that resemble those of the earliest mammals. In contrast, several other orders of placental mammals have evolved amazing specializations to their environments and modes of living. Consider the two extremes of size and habitat represented by the bats and the cetaceans. Competition between marsupials and placentals.  Wherever marsupials and placentals have been in contact, the placentals usually prevail: ●●

Sloths eat very low-quality food (toxic plant leaves) in tropical rain forests. One of their adaptations to a low-energy diet is to move very slowly and hang from branches by their claws.  (Stanley A. Rice) ●●

elephants from whom they have been separated a long time. Edentates live primarily on small invertebrates. The ones that live on ants and termites (anteaters and aardvarks) have long snouts and long tongues that allow them to invade nests and few or no teeth. Armadillos have epidermal scales that form a leathery armor. The giant armadillo (Priodontes maximus) can be five feet (one and a half meters) long and weigh 130 pounds (60 kg). The only armadillo in North America is the nine-banded armadillo (Dasypus novemcintus). Sloths (see photograph) consume leaves that contain a lot of toxins, from which they obtain little nourishment. Their very slow movement is an adaptation to this diet. The edentate manner of living has evolved separately several times; therefore, the old order Edentata has been split into Pilosa (anteaters and sloths), Tubulidentata (the aardvark Orycteropus afer), Pholidota (scaly anteaters), and Cingulata (armadillos). Insectivores are a diverse group of small mammals that live in forests and eat small invertebrates or are omnivorous. Moles dig burrows with their

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●●

In the Mesozoic era, marsupials were widespread in the world. After the Oligocene epoch, however, most marsupials were found in Australia and South America. Placental mammals may have outcompeted them in other places. About 2.5 million years ago, the Panama land bridge formed, connecting North and South America for the first time since the breakup of Pangaea during the Mesozoic era. South America had many marsupial mammals, as well as some placentals such as sloths, armadillos, anteaters, and some rodents. When the land bridge formed, many placental mammals migrated south from North America and outcompeted marsupials in South America. Few South American marsupials successfully moved northward, the opossum being the lone North American marsupial success story. When modern humans arrived in Australia thousands of years ago, they brought dogs, which became the wild dingos; Europeans brought many placental mammals such as dogs, cats, and rodents a couple of hundred years ago. Competition with placentals has driven most Australian marsupials (except kangaroos) near or into extinction.

This should not, however, be taken as evidence of inherent inferiority of the marsupial reproductive

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368 Margulis, Lynn 368 system. Some observers think that marsupials lost in competition because they had not been, in southern continents, subjected during their evolution to the climatic extremes that had occurred in the northern continents. The fact that the marsupial reproductive system seems well suited to variable and occasionally harsh conditions seems to contradict this idea, however. In placentals, short of spontaneous abortion, the mother has to carry the fetuses to full term, even under stressful conditions such as famine. The infants may die soon after birth, but not until after the placental mother has made a tremendous prenatal investment in them. In marsupials, in contrast, the fetus is born at a very early stage, and when food is scarce this is the stage at which they can be abandoned. Marsupials, in addition, have a lower metabolic rate during rest, which may help them conserve scarce energy. Because marsupials appear superior under the stressful conditions that all lineages have experienced at some time or other, the reasons why the placentals have largely prevailed over the marsupials are not clear. See also convergence; primates. Further Reading Agustí, J., and M. Antón. Mammals, Sabertooths, and Hominids: 65 Million Years of Mammalian Evolution in Europe. New York: Columbia University Press, 2002. Angielczyk, Kenneth D. “Dimetrodon is not a dinosaur: Using tree thinking to understand the ancient relatives of mammals and their evolution.” Evolution Education and Outreach 2 (2009): 257–271. Benton, Michael. “Four Feet on the Ground.” Chap. 4 of The Book of Life: An Illustrated History of the Evolution of Life on Earth, edited by Stephen Jay Gould. New York: Norton, 1993. Frick, Winifred F., et al. “An emerging disease causes regional population collapse of a common North American bat species.” Science 329 (2010): 679–683. Gibson, Robert A., et al. “Fatty acids of the milk and food of the platypus (Ornithorhynchus anatinus). Lipids 23 (1988): 377–379. Gould, Stephen Jay. “Sticking up for marsupials.” Chap. 28 in The Panda’s Thumb. New York: Norton, 1980. Hopson, J. A. “The mammal-like reptiles: a study of transitional fossils.” American Biology Teacher 49 (1987): 16–26. Jehle, Martin. “Marsupials: A southern success story.” In Paleocene Mammals of the World. Available online. URL: http://www.paleocene-mammals.de/marsupials. htm. Accessed August 3, 2010. Kemp, T. S. The Origin and Evolution of Mammals. Oxford, U.K.: Oxford University Press, 2005. Kielan-Jaworowska, Zofia, et al. Mammals from the Age of Dinosaurs: Origins, Evolution, and Structure. New York: Cambridge University Press, 2004.

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first entry Prothero, Donald R. “Evolutionary transitions in the fossil record of the terrestrial hoofed mammals.” Evolution Education and Outreach 2 (2009): 289–302. Rich, Thomas H., et al. “Independent origins of middle ear bones in monotremes and therians.” Science 307 (2005): 910–914. Rubidge, Bruce S., and Christian A. Sidor. “Evolutionary patterns among Permo-Triassic therapsids.” Annual Review of Ecology and Systematics 32 (2001): 449–480. Teague, Matthew. “Camel beauty queens.” National Geographic, August 2009, 114–125. Turner, A., and M. Antón. Evolving Eden: An Illustrated Guide to the Evolution of the African Large-Mammal Fauna. New York: Columbia University Press, 2004.

Margulis, Lynn (1938–  ) American  Evolutionary biologist Lynn Margulis is one of the few scientists alive today who has changed some of the basic assumptions of a whole field of study. She persistently defended the endosymbiotic theory of the origin of mitochondria and chloroplasts that had been proposed decades earlier by Russian botanists and by American biologist Ivan Wallin. She gathered evidence from many studies that finally established this theory. Mitochondria and chloroplasts are the evolutionary descendants of bacteria. She is currently testing the theory that eukaryotic cilia, flagella, and microtubules are also the evolutionary descendants of bacteria. She has presented evidence that symbiogenesis (the symbiotic origin of cellular structures) is an important source of evolutionary novelty and diversification. Symbiosis (for example, with microorganisms living inside the roots of plants) made plant life on land possible, and plants then created the habitats in which animals lived. Margulis says, “Symbiogenesis was the moon that pulled the tide of life from its oceanic depths to dry land and up into the air.” She also explains that, because all life-forms interact so closely, they produce a global living system that regulates some physical conditions (such as temperature and atmospheric gas composition) of the entire planet, an idea called the Gaia hypothesis. To Margulis, symbiosis is pervasive throughout the living world, from the smallest cellular components to the global ecosystem. She says, “Symbiosis is not a marginal or rare phenomenon. It is natural and common. We abide in a symbiotic world.” Margulis has always been a creative thinker and willing to take bold steps to pursue new theories. Born on March 5, 1938, Lynn Alexander was an early entrant, at age 14, into the University of Chicago. She pursued a general liberal arts degree that emphasized independent study and the reading of

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marshes and swamps  369 original publications rather than textbooks. While at Chicago she met another precocious and creative student of science. Astronomer Carl Sagan was already a graduate student at age 19. Both she and Sagan, who later married, were to become two of the most creative thinkers and prolific writers in modern science, and both were to contribute in different ways to an understanding of planetary atmospheres as well as of evolution. Lynn and Carl Sagan moved to Wisconsin. She studied genetics at the University of Wisconsin, Madison, then continued her studies at the University of California at Berkeley, where she completed her doctorate in 1965. She became especially interested in cytoplasmic inheritance, in which genetic traits were passed from one generation to another in the cytoplasm rather than by the nucleus. She found out that early 20th-century geneticists Hugo DeVries and Carl Correns knew that not all of a plant cell’s genes were in the nucleus and had discovered that chloroplasts also had genes. But they and most geneticists since them had divided genetic inheritance into “nuclear v. unclear,” dismissing cytoplasmic inheritance as unimportant. After 15 rejections and losses, Lynn Sagan’s paper was published in 1967. Her persistence and her refusal to accept a simplistic doctrine eventually led to a revolution in biology. Lynn Margulis joined the biology faculty of Boston University in 1966. The departmental chair, biologist George Fulton, described Margulis as “the only instructor who was paid half time and worked time and a half.” Margulis left Boston University, and in 1988 joined the faculty, first in biology then in geosciences, at the University of Massachusetts at Amherst, where she is currently a distinguished professor. She believes strongly that students in her courses should go outdoors and directly observe organisms in their contexts of symbiotic interaction. Margulis is a member of the National Academy of Sciences and has written numerous books and articles with her son, the writer Dorion Sagan. See also Gaia; symbiogenesis. Further Reading Margulis, Lynn. “Mixing it up: How I became a scientist.” Natural History, September 2004, 80. ——— Symbiosis in Cell Evolution: Microbial Communities in the Archaean and Proterozoic Eons, 2nd ed. New York: W. H. Freeman, 1993. ———. Symbiotic Planet: A New Look At Evolution. New York: Basic Books, 1998. Margulis Lynn, and Dorion Sagan. “The beast with five genomes.” Natural History, June 2001, 38–41. ———. Mystery Dance: On the Evolution of Sexuality. New York: Touchstone, 1992.

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———. Slanted Truths: Essays on Gaia, Symbiosis, and Evolution. New York: Copernicus, 1997. Margulis, Lynn, and Karlene V. Schwartz. Five Kingdoms: An Illustrated Guide to the Phyla of Life on Earth, 3rd ed. New York: W. H. Freeman, 1998. Sagan, Lynn. “On the origin of mitosing cells.” Journal of Theoretical Biology, 14 (1967): 225–274. Sciencewriters. “Sciencewriters: About the Authors.” Available online.URL: http://www.xsnrg.com/sciencewriters/ authors.htm. Accessed August 15, 2010.

marshes and swamps  Marshes and swamps

are terrestrial and coastal wetlands. They are flooded by shallow water most of the time; the dominant plants are rooted in the soil and emerge above the water surface. Grasslike plants dominate marshes, while shrubs or trees dominate swamps (see photograph on page 370). In the absence of ecological disturbance, ponds become swamps or marshes. If a river changes course and takes a shorter route, the old riverbed becomes an oxbow swamp or marsh.

Some Types of Wetlands Freshwater marshes. The most abundant marsh plants are the grasslike sedges, rushes, cattails (or tules), and bur reeds in the shallow water and water lilies in the deeper water (see table on page 371). Many of these plants form thick, clonally spreading mats that cannot easily be penetrated by other plants. Surprisingly enough, it is often fire that keeps trees from growing in marshes. Fires burn plant tissues above water level or during the dry season; this kills trees and shrubs but allows the grasslike plants to resprout. One of the largest freshwater marshes in North America is the Everglades of Florida. During the wet season, water flows from Lake Okeechobee across a limestone shelf (which prevents the water from percolating into the ground) in a slow river about 60 miles (almost 100 km) wide into Florida Bay. It is dominated by sawgrass, a sedge. The Central Valley of California (the Sacramento and San Joaquin Valleys) was until the 20th century the largest marsh in the United States. Snowmelt from the Sierra Nevada fed the marshes, and the water was blocked by the Coast Range. All the major rivers have been dammed and the entire marsh converted to irrigated agriculture. Trees may grow on hummocks of raised soil in marshes. Live oak (Quercus virginiana) and gumbo limbo (Bursera simaruba) trees and Roystonea palms dominate the hummocks of the Everglades. Freshwater swamps. The most famous swamp tree is the bald cypress, a tall tree that dominates swampland throughout most of the eastern United States. Cypress swamps are relatively undisturbed.

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first entry

Trees dominate swamps, such as this bald cypress swamp in the National Audubon Society’s Corkscrew Swamp Sanctuary in Florida. Emergent herbaceous plants are rooted to the soil under the water.  (Marc Ryckaert)

In many cases, new plants have no place to germinate except the stumps of old cypress trees. Swamps with more disturbance may be dominated by shrubs such as the hazel alder, which has numerous trunks continually sprouting from the rootstock as disturbances destroy the older trunks. Many marsh and swamp plants, such as sawgrass, grow best when oxygen can reach the roots. However, thick layers of anaerobic organic ooze accumulate at the bottom of many marshes and swamps. Bacteria in these deposits may produce methane, which can ignite and form a ghostly bluish glow known as will-o’-the-wisp or foxfire. The roots of swamp trees and shrubs also build up mounds of soil. Estuaries.  Brackish marshes or salt marshes have ocean water diluted by freshwater to varying degrees. The most abundant estuary plant is cordgrass. Salinity is one of the most important factors that produce zonation within estuaries. In San Francisco Bay, cordgrass (Spartina foliosa) dominates the

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zone between mean sea level and the average high tide level, while pickleweed, a small succulent (Salicornia virginica), dominates the zone above average high tide, where the soil contains more salt due to evaporation. Mangrove swamps. Around the world, mangroves form thick woodlands along beaches. Wetland animals.  Many species of animals live primarily in wetlands. Herbivores include muskrats (Ondatra zibethicus), Northern river otters (Lontra canadensis), and beavers (Castor canadensis). Predators include alligators (Alligator mississippiensis) and snapping turtles (Macrochelys temminckii). Beavers are a keystone species, as they construct dams that can transform a creek into a marsh or swamp. Among the birds that are common in marshes are red-winged blackbirds (Agelaius phoeniceus), which live in the aerial vegetation, and wading birds such as the great blue heron (Ardea herodius), which hunt fishes. The larvae of many insect species live in wetlands.

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marshes and swamps  371 Some Important Wetland Plants Common Name

Scientific Name

Family

Wild rice

Zizania aquatica

Poaceae (grass)

Sawgrass

Cladium jamaicense

Cyperaceae (sedge)

Woolgrass

Scirpus cyperinus

Cyperaceae (sedge)

Western rush

Juncus occidentalis

Juncaceae (rush)

Narrow-leaved cattail

Typha angustifolia

Typhaceae (cattails)

American bur reed

Sparganium americanum

Sparganiaceae (bur reed)

Spatterdock

Nuphar lutea

Nymphaceae (water lily)

Bald cypress

Taxodium distichum

Taxodiaceae (cypress)

Hazel alder

Alnus serrulata

Betulaceae (birch)

Red mangrove

Rhizophora mangle

Rhizophoraceae

Black mangrove

Avicennia germinans

Acanthaceae (acanthus)

White mangrove

Laguncularia racemosa

Combretaceae

Spartina alterniflora

Poaceae (grass)

Freshwater marsh plants

Freshwater swamp plants

Mangrove swamp plants

Salt marsh Cordgrass

Wetland Plant Adaptations The roots of many swamp and marsh plants experience low oxygen conditions. Among the ways that swamp and marsh plants provide oxygen to their root systems are the following: ●●

●●

Bald cypress tree roots produce knobs that protrude above the water level and enhance the aeration of the root system. Many herbaceous plants have tissues filled with air spaces, which conduct air down to the root zone. Sometimes they create red zones of rusted iron in anaerobic soil filled with black iron.

Wetland plants have numerous adaptations that allow them to function both in and out of water, as in these examples: ●●

Leaf structure.  Underwater leaves are often narrow and fiberlike, which increases the absorption of carbonate ions (instead of carbon dioxide) from the water. Leaves above the water are flat and have a waxy cuticle that

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●●

●●

controls evaporative water loss. Some plants, such as certain buttercups, produce fiberlike leaves below the water level, and flat leaves on the stems that emerge above the surface. Pollination.  Most emergent wetland plants produce flowers above the water level, where the wind or insects can carry their pollen. Some wetland plants live entirely underwater. The ribbonweed (Vallisneria) produces male flowers that float to the surface, where the currents carry them to female flowers that just barely emerge from the water. Seeds.  Mangrove trees are viviparous— that is, they produce live offspring. The seeds begin to germinate while they are still on the tree. When they fall into the water, upright like daggers, the first leaves are already expanded.

Ecological Importance and Peril of Wetlands Ecological processes in wetlands provide benefits to adjacent ecological communities, as well as to humans, as in these examples:

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372 marsupial mammals  372 ●●

●●

●●

Breeding grounds for ocean fishes.  Many marine fishes begin their lives in estuaries, where plankton food is abundant and the young fishes can hide from larger fishes. Cleaning the runoff water.  Wetlands serve as a filter in which organic compounds (including some of human origin) decompose in the soil. Storm surge protection.  Wetland plants, particularly mangroves, hold down the soil and protect inland areas from storm surges. Scientists frequently attribute the high levels of damage that follow tsunamis and hurricanes to the destruction of mangrove swamps, often to use the land for shrimp farms.

Not only are wetlands threatened by habitat destruction, but they are frequently the recipients of pollution, which flows downstream and concentrates in them. Many of the examples of biomagnification occur in wetlands. Several invasive plant species are taking over large areas of wetlands as well. Many areas of open water in the southern United States have been covered with water hyacinth (Eichhornia crassipes) or water lettuce (Salvinia molesta). Large areas of the Everglades have been invaded by shrubs such as the pepper tree (Schinus terebinthinifolius) or large trees such as Melaleuca quinquenervia. Melaleuca trees, which transpire huge amounts of water vapor into the air, were imported from Australia specifically to help drain the Everglades, a job that they are now doing all too well. Purple loosestrife is an escaped ornamental wetland plant that is spreading throughout the marshes of the United States. It displaces the wetland plants that serve as food for native animals. Because of their importance to other habitats, wetlands are a frequent focus of habitat mitigation, in which an agency or business must establish a new wetland if they destroy or disturb an old one. See also biomagnification; disturbances, ecological; keystone species. Further Reading Barnett, Cynthia. Mirage: Florida and the Vanishing Water of the Eastern U.S. Ann Arbor, Mich.: University of Michigan Press, 2007. Carter, W. Hodding. Stolen Water: Saving the Everglades from its Friends, Foes, and Florida. New York: Simon & Schuster, 2004. Grunwald, Michael. The Swamp: The Everglades, Florida, and the Politics of Paradise. New York: Simon & Schuster, 2006. Kathiresan, R. M. “Allelopathic potential of native plants against water hyacinth.” Crop Protection 19 (2000): 705–708.

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first entry Mahall, Bruce E., and Roderic B. Park. “The ecotone between Spartina foliosa Trin. and Salicornia virginica L. in salt marshes of northern San Francisco Bay: I. Biomass and production.” Journal of Ecology 64 (1976): 421–433. Myers, Randell S., et al. “Baldcypress (Taxodium distichum (L.) Rich.) restoration in southeast Louisiana: The relative effects of herbivory, flooding, competition, and macronutrients.” Wetlands 15 (1995): 141–148. Naiman, Robert J., et al. “Ecosystem alteration of boreal forest streams by beaver (Castor canadensis).” Ecology 67 (1986): 1,254–1,269. Saiki, Michael K., and T. Peter Lowe. “Selenium in aquatic organisms from subsurface agricultural drainage water, San Joaquin Valley, California.” Archives of Environmental Contamination and Toxicology 16 (1987): 657–670. Valiela, Ivan, et al. “Macroalgal blooms in shallow estuaries: Controls and ecophysiological and ecosystem consequences.” Limnology and Oceanography 42 (1997): 1,105–1,118.

marsupial mammals  See mammals. mass extinctions  Mass extinction occurs when many species become extinct at roughly the same time. Extinction in general may result if populations do not have the genes that allow them to adapt to environmental changes, that is, from “bad genes”; but extinction may also occur suddenly as a result of a worldwide disaster, for which no populations possess genetic resistance, that is, from “bad luck,” to use paleontologist David Raup’s terminology. Global mass extinctions are usually considered to have resulted from “bad luck.” Therefore true mass extinction events may result from rare catastrophic events rather than an acceleration of normal extinction patterns. Most of the geological periods ended with global changes in climate and the origin of recognizably different sets of species. That is, there were global extinctions at the end of every geological period. Five of these events were mass extinctions (see table on page 373). Two of the mass extinction events brought the first two eras of the Phanerozoic eon: the Permian extinction ended the Paleozoic era, and the Cretaceous extinction ended the Mesozoic era. A mass extinction, especially of the Ediacaran organisms, may have occurred at the end of the Precambrian time. The Ordovician, Permian, and Cretaceous mass extinctions occurred against a background of rapid evolution and therefore were caused by global catastrophes, whereas the Devonian and Triassic mass extinctions occurred against

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mass extinctions  373 Major Extinctions in the History of Life Millions of Years Ago

Percent of Families Dying

Percent of Genera Dying

Percent of Species Dying

Ordovician

439

26

60

85

Devonian

367

22

57

83

Permian

251

51

82

95

Triassic

208

22

53

80

Cretaceous

  65

16

47

76

Geological Era End of

a background of ongoing extinction and may have been caused by an amplification of climatic trends that were already occurring.

A Common Pattern in Mass Extinctions Perhaps the biggest unsolved mystery regarding global extinction events is what appears to be their recurring pattern. Paleontologists David Raup and J. J. Sepkoski have calculated a 26-million-year cycle of recurring mass extinctions. The pattern is not perfect: Global extinctions have not occurred every 26 million years, nor have they occurred at precisely this interval. However, their results are statistically significant. Scientists have been unable to explain normal geological events that might cause such a recurring synchronous pattern. Earth scientists Marc Davis, Piet Hut, and Robert Muller have suggested that there is a small companion star to the Sun, which sweeps a mass of comets and asteroids along with it. The orbit of this star, they speculate, brings it close enough to the Earth every 26 million years to bombard the Earth with comets and asteroids. Even those that suggest the existence of this “Nemesis star” admit that it has not been seen or otherwise detected. Furthermore, this theory does not explain why five of the global extinctions should have been so much more significant than the others. Mass extinctions all seem to share certain characteristics. In particular, they are preceded by anoxic deep oceans—that is, oceans with a well-defined deep layer of water that lacks oxygen. Most of the time, the deep oceans contain oxygen because oceanic currents bring oxygen from the surface. Today, these currents plunge into the ocean depths mostly in the North Atlantic and in the Southern Ocean around Antarctica. Geologist Donald Canfield suggested that global warming could cause these currents to draw water into the ocean depths in locations where the surface water contains less oxygen.

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The global warming could occur as a result of massive volcanic eruptions. The result would be that the deep oceans would contain less oxygen and eventually become anoxic, resulting in a “Canfield ocean.” If the depth at which the oceans became anoxic is several hundred meters or more, life can thrive in the oxygenated surface waters. Geologist Lee Kump and associates suggested in 2005 that mass extinctions could occur if the anoxic waters came too close to the surface, causing the extinction of life-forms that lived in oxygenated waters. If the anoxic water layer was close enough to the surface to allow light to penetrate to it, photosynthetic sulfur bacteria populations would explode. Photosynthetic cyanobacteria produce oxygen, but photosynthetic sulfur bacteria produce hydrogen sulfide, which would emerge into the atmosphere. The resulting acid rain would be poisonous to life on land. Planetary scientist Peter Ward describes the scene as a purple ocean (filled with purple sulfur bacteria) releasing bubbles of hydrogen sulfide (from green sulfur bacteria), with very high clouds in a green sky. Not all marine life would have become extinct, because oxygenated surface waters would have persisted in some parts of the ocean. Each mass extinction event was unique but each of them may have had volcanic eruptions, global warming, and Canfield oceans. Solar flares, which would flood the Earth with intense radiation, have been suggested as a possible cause of mass extinctions. Scientists know little about the timing of these solar flares through the history of the solar system, and these flares would leave no evidence of having struck the Earth, other than the mass extinction itself. Because they cannot think of a way to investigate this possibility, most scientists dismiss solar flares as a cause of extinction events. Following each mass extinction event, the diversity of species has not only recuperated but

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374 mass extinctions  374 increased. The best fossil record that is available is that of marine invertebrates. This record indicates a steady increase in worldwide species diversity, especially after mass extinction events. One example of evolution following a mass extinction is the adaptive radiation of mammal species after the extinction of the dinosaurs. Some extinction events, although not considered mass extinctions, have still had an important effect on the evolutionary history of life. The Hemphillian extinction event about 5 million years ago drove relatively few species to extinction, but among them were many grazing animals. A diversity of horse species was reduced to just one. Terrestrial plants may not respond to mass extinction events as rapidly or as markedly as marine and terrestrial animals. Most plant extinctions have been caused by long-term climatic changes. While many plants became extinct during the five mass extinction events, their response was delayed until several million years after each of the extinction events. The Permian mass extinction that brought the Permian period and the whole Paleozoic era to an end 250 million years ago was, in the words of paleontologist Douglas Erwin, the “mother of all extinctions.” At this time, at least half of all families of organisms became extinct. Because some families contain many species, it has been estimated that up to 95 percent of all species became extinct at that time! Biodiversity recovered after the Permian extinction, but it took 100 million years to regain its former level. And the Permian extinction had longterm consequences. During the Permian period, the oceans contained many filter feeders that remained attached to rock surfaces. After the Permian extinction, many motile animals evolved in the oceans. Therefore the post-Permian increase in diversity was not merely the evolution of new species but new ways of obtaining resources. Furthermore, during the Permian period, mollusks (Phylum Mollusca) and lampshells (Phylum Brachiopoda) were of roughly equal abundance, but (perhaps due to chance) the lampshells suffered greater extinction than the mollusks. Today, mollusks are abundant and lampshells remain rare.

The Cretaceous Extinction Was Unique The most famous example of a mass extinction event is the Cretaceous extinction event 65 million years ago. At that time, many species of organisms, most famously the dinosaurs, became extinct. Exceptionally high levels of the element iridium in the geological deposits 65 million years ago suggest that the Earth was hit by an asteroid; asteroids usually contain higher levels of this element than do the rocks

xviii+598_Biodiversity_F.indd 374

first entry of the Earth’s crust. The greatly eroded remnants of this impact can still be seen in the Chicxulub crater of Yucatán. Even though some evidence for an asteroid collision at the end of the Permian period has been presented, it has failed to convince most scientists. Therefore the Cretaceous extinction may have been the only one caused by an asteroid. Even the Cretaceous extinction event, however, had more than one cause. By the time the asteroid hit the Earth, populations of many dinosaur and other species had already been in decline for millions of years. (However, many other species flourished up until the moment of the extinction event.) Moreover, a massive volcanic eruption occurred about the same time in what is now India, producing a 200,000 square mile (over 500,000 km 2) lava flow called the Deccan Traps. Several interacting causes, the relative importances of which are still debated, brought about the Cretaceous extinction. Asteroid collisions and other planetary disasters have been relatively rare for the past 1 or 2 billion years. According to Earth scientists Peter Ward and David Brownlee, humans should, so to speak, thank their lucky stars for this: The Sun is a relatively stable star, compared to most in the universe, and the planet Jupiter (which can be considered a star that never ignited) has swept part of the solar system free of most asteroids except those in the asteroid belt. Craters on the Moon appear to be mostly 3 to 4 billion years old, indicating that during this time period comets and asteroids were very common in the solar system. Even though bacterial life appeared on Earth soon after Earth’s formation, frequent bombardment of the Earth during that period may have delayed the appearance of complex cells until about a billion and a half years ago. The evolution of complex life-forms would have been impossible on a planet subjected to frequent mass extinctions.

The Sixth Mass Extinction Many scientists describe the extinctions that are now occurring throughout the world, as a result of human activities such as the destruction of natural habitats, as the “sixth mass extinction.” Extinctions are in fact now occurring at a rate that would justify this description. Before the appearance of humans, the global extinction rate was about one per million species per year; now the global extinction rate is one per thousand per year. It is possible that global warming, caused by human carbon emissions, may eventually make its own contribution to the sixth mass extinction. It is possible that the most recent Canfield ocean event was the Paleocene-Eocene Thermal Maximum, a brief period of global warming following

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monocots  375 a sharp rise in atmospheric carbon dioxide that occurred 55 million years ago. Although it was not a mass extinction, this event was associated with a tremendous turnover of animal species, particularly the extinction of early Cenozoic mammals and the origin of modern mammalian groups. The atmospheric carbon dioxide concentration was only about 800 parts per million, a level that the atmosphere may reach again by the year 2100 if current rates continue. Writer Wendell Berry comments, regarding the countless extinctions that are now occurring, “We can less afford [these] losses than nature can.” It is humanity that is perhaps harmed most by the mass extinction that it is causing. Nor can we simply blame big business or government for destroying nature. All participants in the world economy are partly responsible. Berry noted that humans are all complicit in the murder of creation. See also acid rain and fog; bacteria; Cretaceous extinction; extinction; Permian extinction. Further Reading Courtillot, Vincent. Evolutionary Catastrophes: The Science of Mass Extinction. Transl. Joe McClinton. New York: Cambridge University Press, 2002. Davis, M., P. Hut, and R. Muller. “Extinction of species by periodic comet showers.” Nature 308 (1984): 715–717. Hallam, Anthony. Catastrophes and Lesser Calamities: The Causes of Mass Extinctions. New York: Oxford University Press, 2004. ——— and P. B. Wignall. Mass Extinctions and Their Aftermath. New York: Oxford University Press, 1997. Horner, Jack, and James Horman. How to Build a Dinosaur: Extinction Doesn’t Have to Be Forever. New York: Dutton, 2009. Krug, Andrew Z, et al. “Signature of the end-Cretaceous mass extinction in the modern biota.” Science 323: (2009): 767–771. Summarized by Crame, J. Alistair. “Time’s stamp on modern biogeography.” Science 323 (2009): 720–721. Kump, Lee, et al. “Massive release of hydrogen sulfide to the surface oceans and atmosphere during intervals of oceanic anoxia.” Geology 33 (2005): 397–400. Leakey, Richard, and Roger Lewin. The Sixth Extinction: Patterns of Life and the Future of Humankind. New York: Anchor Books, 1996. Lidgard, Scott, et al. “The search for evidence of mass extinction.” Natural History, September 2009, 26–32. Raup, David M. Extinction: Bad Genes or Bad Luck? New York: Norton, 1991. Villier, Loïc, and Dieter Korn. “Morphological disparity of ammonoids and the mark of Permian mass extinctions.” Science 306 (2004): 264–266.

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Ward, Peter D. Under a Green Sky: Global Warming, the Mass Extinctions of the Past, and What They Can Tell Us About Our Future. New York: HarperCollins, 2008. ——— and David Brownlee. Rare Earth. New York: Copernicus Books, 2000. ——— and Alexis Rockman. Future Evolution. New York: Freeman, 2001.

mimicry  See camouflage and mimicry. mineral cycles  See biogeochemical cycles. Miocene epoch  See Neogene period, biodi-

versity in.

monocots  Monocots are an evolutionary lineage of flowering plants. There are at least 90,000 species of monocots, ranging from tiny herbaceous plants to trees. Along with the conifers, the flowering plants have transformed the landscape of the Earth into a living surface of green. In addition, flowering plants have undergone coevolution with animals that pollinate their flowers and disperse their seeds. As a result, the flowering plants have filled the world with an astounding diversity of form, color, and scent. Flowering plants have flowers and fruits. Flowers may contain: ●● ●● ●● ●●

sepals: leaflike protective structures; petals: often colorful structures that attract pollinators; stamens: male structures that produce pollen; and pistils: female structures that produce seeds.

The term monocot refers to the embryo of the plant: when it emerges from the seed, the embryo has just one cotyledon, or embryonic leaf. Most monocots also have veins that are mixed with starch storage cells in the middle of the roots and in the young stems and are parallel to one another in the leaves, in contrast to the arrangement of veins in the dicots, the embryos of which have two cotyledons.

Monocots with Showy Flowers Some families of monocots have brightly colored flowers that attract pollinators (see photographs on page 376). Below are some important examples. The lilies (Liliaceae) are a large family of monocots, which includes lilies, daffodils, onions, and agaves. Some taxonomists divide this family

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376 monocots  376

first entry tiny seeds, some of which consist of only a few cells and cannot germinate unless they form a mutualistic partnership with a fungus. Palm trees (Arecaceae) are the largest monocots. Their trunks would not be able to support large branches. The large leaves emerge from a single crown at the top of the tree. The arums (Araceae) such as jack-in-the-pulpit produce many tiny staminate and pistillate flowers on a spike, which is surrounded by a large, usually colorful leaf. It is this leaf, rather than the flowers themselves, that attracts pollinators.

Monocots without Showy Flowers Several families of monocots have flowers the sepals and petals of which are greatly reduced. These monocots rely on wind pollination. The grass family (Poaceae) is one of the most important families of flowering plants on Earth, one of two families of seed plants (along with the pines) that can be seen from outer space. Their roots hold the soil, and their leaves and stems produce

The flowers of monocots, such as this Tradescantia ohiensis, often have three petals and either three or (in this case) six stamens. The leaves often have parallel veins.  (Stanley A. Rice)

into several smaller ones. They are all herbaceous, except the succulent agaves. The flowers have three sepals and three petals. Sometimes the sepals resemble the petals, giving the appearance of six petals. Six stamens surround a pistil of three united seed chambers. The irises (Iridaceae) have flowers similar to those of lilies, except that the three stamens surround a pistil whose seed chambers develop below the flower. The orchids (Orchidaceae) are very diverse, with at least 20,000 species, many of them pollinated by only one kind of insect. Orchid flowers have three petals, one of which (the labellum) is larger and more ornate than the others (see figure). In some orchids, the labellum forms an intricate mechanism that deposits packets of pollen on the body of the pollinator, perhaps temporarily entrapping it in the process. Many orchids are epiphytes, living in the branches of tropical trees and obtaining water from rain. Because epiphytic orchids cannot obtain water from the soil, they often have succulent leaves that store water. They produce a large number of very

xviii+598_Biodiversity_F.indd 376

Orchids are recognizable because one of their three petals is fancy and colorful relative to the others.  (Weddingaces.com)

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Muir, John 377 most of the food, in grassland ecosystems that cover almost one-quarter of the Earth’s dry land surface. They have coevolved with grazing mammals, largely because their leaves have cells that allow them to grow from the base of the blade; the leaves can therefore keep growing after the tip has been eaten. Each tiny flower is enclosed within two specialized leaves (bracts), and the flowers are compressed into a spikelet. Spikelets, in turn, can be arranged on reproductive stems in many ways. The flowers are visible only when the stamens and stigmas emerge from between the bracts during pollination. In addition to their ecological importance, the economic importance of grasses can hardly be overstated: wheat, maize, rice, sugarcane, oats, rye, and barley are all grasses. The sedge family (Cyperaceae) contains many species that live in and maintain the ecological integrity of wetlands. They closely resemble grasses, except that the tiny flowers of their spikelets are pressed against the reproductive stem by a single bract, rather than between two. Although the only economically important sedge today is the water chestnut, this family played an important role in human history. Leaves of the papyrus sedge were used by the ancient Egyptians to make the first paper. The rush family (Juncaceae) is also aquatic and resembles grasses and sedges. Its tiny flowers, however, have sepals and petals. The cattail family (Typhaceae) has long succulent leaves that emerge from an underwater stem. The reproductive stalk produces thousands of tiny staminate and pistillate flowers. When the pistillate flowers form seeds, they remain on the stem, producing the characteristic appearance of a hot dog on a stick. From simple ancestors that lived near the beginning of the Cretaceous period, the flowering plants have diversified into hundreds of thousands of species, produced many specialized reproductive structures, and adapted to every habitat on Earth, including coastal Antarctica. Of the two flowering plant species that live in Antarctica, one is a monocot and one is a dicot. Most of these flowering plants are dicots. No other group of multicellular organisms, except the insects, have evolved such tremendous diversity. Explorers continue to discover new species of monocots, usually but not always in tropical forests. Many species are driven to extinction, often before they have been studied by scientists, when humans destroy their habitats. This is a tremendous loss to the ecological communities of which they are the basis, to scientific research, and to the human economy. See also dicots; flowering plants (angiosperms); pollination.

xviii+598_Biodiversity_F.indd 377

Further Reading Brown, Lauren. Grasses: An Identification Guide. Boston: Houghton Mifflin, 1992. Dafni, A., and Y. Ivri. “Floral mimicry between Orchis israelitica Baumann and Dafni (Orchidaceae) and Bellevalia flexuosa Boiss. (Liliaceae).” Oecologia 49 (1981): 229–232. Darwin, Charles R. On the Various Contrivances by which British and Foreign Orchids are Fertilised by Insects. London: John Murray, 1862. Johnson, S. D., and K. E. Steiner. “Long-tongued fly pollination and evolution of floral spur length in the Disa draconis complex (Orchidaceae).” Evolution 51 (1997): 45–53. Neiland, Mary Ruth M., and Christopher C. Wilcock. “Fruit set, nectar reward, and rarity in the Orchidaceae.” American Journal of Botany 85 (1998): 1,657–1,671. Riffle, Robert Lee. The Timber Press Pocket Guide to Palms. Portland, Ore.: Timber Press, 2008.

monocultures

and

polycultures

culture)  See biodiversity, agriculture.

resources

(agrifor

monotremes  See mammals. montane forests  See temperate coniferous

forests.

mosses  See seedless plants. Muir, John (1838–1914) American  Conservationist  Born April 21, 1838, in Scotland, John Muir grew up as part of a large family of farmers in Wisconsin. While growing up, Muir acquired a deep love of the land and was disturbed to see the widespread destruction of the eastern forests. He studied botany at the University of Wisconsin, but did not finish a degree. He went to Canada during the American Civil War, apparently to avoid the draft, and worked in a sawmill. While he worked in a factory in Indiana, an accident left Muir temporarily blinded in one eye, and when he regained his sight, he decided to walk everywhere he could to see and appreciate the natural world. He walked from Indiana to Florida. He went to California to recover from malaria he contracted in Florida. In 1868, he first saw Yosemite Valley, in the Sierra Nevada, and he stayed there for six years, working mostly as a shepherd.

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378 mutualism  378 While wandering in the Sierras, Muir wrote articles about nature and what he had learned on his many hikes. He had a deeply spiritual reverence for all of the species in the forests and meadows (he often talked with wildflowers) and understood their interdependence. He valued the preservation not just of natural resources but of wilderness and of wilderness not just for recreation but for its spiritual value. Muir became a celebrity in Yosemite Valley for his knowledge of biodiversity and as a guide. He loved the writings of Ralph Waldo Emerson and Henry David Thoreau, whose writings promoted the kind of life that Muir was living. Emerson went to Yosemite and met Muir in 1871 and offered him a professorship at Harvard—which Muir declined. Muir dedicated himself to wilderness preservation. In 1892 he cofounded the Sierra Club, which remains one of the principal voices for conservation of wilderness. Muir was also the principal voice behind the formation of Yosemite National Park in 1899. Muir met Gifford Pinchot, who was to become the most important force for government conservation in the early 20th century, while hiking in the Adirondacks, and they became friends and traveled extensively through western forests. Although they shared a deep love of nature, their views on conservation differed markedly. Pinchot believed that the purpose of conservation was the efficient management of natural resources for the long term, while Muir defended wilderness preservation. In 1907, Pinchot (by then head of the United States Forest Service under President Theodore Roosevelt) defended the creation of Hetch Hetchy reservoir in the Sierras by building a dam and flooding a valley near Yosemite, while Muir opposed it vigorously. Pinchot and Muir spent their later lives debating their conflicting views of what conservation was supposed to accomplish. Muir married into a wealthy family in 1878 and became the manager of an orchard and a ranch. As Muir’s health began to fail, his wife encouraged him to go back to hiking in the mountains in the Pacific Northwest. On one of these hikes, in 1914, Muir got pneumonia. He died on December 24, 1914. See also environmental ethics; federal government role in conservation (United States); Pinchot, Gifford; Thoreau, Henry David. Further Reading Egan, Timothy. The Big Burn: Teddy Roosevelt and the Fire that Saved America. Boston: Houghton Mifflin, 2008. Worster, Donald. A Passion for Nature: The Life of John Muir. New York: Oxford University Press, 2008.

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first entry

mutualism  Mutualism is a symbiotic relationship between two species that benefits both of them. Each provides some service, often a nutrient, to the other. Many thousands of examples of mutualism are known, of which a few are here described.

Digestive and Other Mutualisms that Maintain Vertebrate Health Cows cannot digest grass, which is odd because they walk around and moo and eat grass all day. It is not the cow itself but the bacteria that live in its rumen (the first stomach) that digest cellulose, one of the major components of grass. The cow chews the grass and delivers it to the rumen. The bacteria live inside the rumen, where they are protected in warm, moist, anaerobic conditions, and digest food that has been broken into small pieces by the cow’s teeth. After a while, the grass returns to the cow’s mouth, where it “chews the cud” to further break down the grass, then swallows it again. The bacteria digest cellulose into sugar for their own benefit, but the cow’s stomach absorbs much of the sugar that the bacteria release. Many other ruminant animals have a similar relationship with digestive bacteria. Eucalyptus leaves are not very nutritious, but koalas eat large amounts of them and allow bacteria to release nutrients from them. Leaves of rain forest plants contain many toxins and are not very nutritious, but animals such as sloths and colobus monkeys eat them, relying on digestive bacteria. Marine iguanas of the Galápagos Islands are the only reptiles to eat seaweeds, and they rely on intestinal bacteria to help them digest their food. Most human intestinal bacteria are commensals, but some of them produce waste products that, to humans, are vitamins. The main human source of vitamin K and an important source of B vitamins are intestinal bacteria. One-quarter of the bacteria in the human intestine are Bacteroides thetaiotaomicron, which competes with food-borne pathogenic bacteria and produce protective compounds such as lactate, peroxide, and bacteriocins. They even stimulate the production of blood vessels in the lining of the intestine. In order to demonstrate the importance of intestinal bacteria in humans, it would be necessary to raise a human in completely sterilized conditions, which would be unethical even if it were possible. Such experiments can be done upon rats, which are physiologically similar to humans. Since a newborn mammal is exposed to bacteria during the birth process, scientists deliver baby rats by cesarean section and raise them in sterilized cages on sterilized rat chow. These gnotobiotic rats, never having been exposed to bacteria, are unhealthy. They show symptoms of vitamin deficiency and eat 30 percent

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mutualism  379 more calories, perhaps in an attempt to compensate for the lack of vitamins. They also have impaired immune function. Proper intestinal function in many animals requires a balanced community of bacterial species, a balance that can be disturbed by the use of broadspectrum oral antibiotics. Pathogenic bacteria may thrive in the depleted community following the use of these antibiotics. Typically, however, some of the resident bacteria have remained alive in the lining of the intestine and recolonize it. Disruption of digestive bacteria is, however, one of the reasons that the use of antibiotics should be reserved for emergency situations. There appears to be mutualism among the intestinal bacteria as well. Most of the intestinal bacteria are anaerobic—they die upon exposure to oxygen. But Escherichia coli (the famous “E. coli”) are microaerophiles, which means that their growth is enhanced by low levels of oxygen. E. coli lives mostly near the lining of the intestine, where oxygen diffuses out of the tiny blood vessels, and in so doing they use up the oxygen before it reaches the middle of the intestine, where the anaerobes live. There are many other examples of protective bacteria in the human body. One of them is the Lactobacillus bacteria that live in the vaginas of women, where they convert sugar to lactic acid. The acid inhibits the growth of Candida albicans fungi that

might otherwise cause infections. Some skin bacteria produce antimicrobial compounds. Some microbes in the human mouth produce antimicrobial compounds that help prevent gum disease. They do so as a weapon against other microbes with which they compete for food, but the indirect result is the maintenance of human health. Another mutualistic association that contributes to vertebrate health occurs when animals remove external parasites from the skins of other animals. Several species of birds remove arthropod parasites from mammals and even from reptiles (see figure). The birds get to eat the parasites, and the larger animals are relieved from those parasites. Cleaning mutualisms also occur in the ocean.

Termite and Ant Gardens Termites cannot digest wood. This is odd because termites spend all of their time eating wood. Instead, they depend on microbes and fungi to do it for them. Some termites have microbes in their intestines. Many termites, however, build collections of gigantic mounds that rise like Stonehenges from the African savanna. The termites do not live and breed in the mounds; they live underground. Instead the mounds are their flow-through composters. Worker termites bring a chewed wood slurry to the top of the mound, where the fungi begin to digest it. The termites ingest the product at the bottom, and then

A bird picks a parasite off a giant Galápagos tortoise.  (Stanley A. Rice)

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380 mutualism  380 their gut microbes proceed to digest it further. The wind ventilates the mounds, promoting the metabolism of the fungi. The termites even maintain a physiological homeostasis within their fungus gardens. The more metabolically active mounds require more oxygen, and they get it, because they are taller and protrude farther from the boundary layer of the ground. If the worker termites sense that carbon dioxide levels are too high within the mound, they will chew open more ventilation holes. Leaf-cutter ants (genus Atta) cannot digest leaves. This is odd because they spend most of their time gnawing leaves off of tropical trees and carrying them down into their nests. Some of the ant colonies are gigantic and can strip an entire tree of its leaves in a few hours. They chew up the toxic leaves, making a compost that feeds a fungus. The fungus consumes the compost but is not itself toxic. The ants eat structures produced by the fungus. When a queen flies off to form a new colony, she takes some of the fungus with her. Some of the workers maintain colonies of actinobacteria on their bodies. These bacteria produce antibiotics that suppress the growth of pathogenic fungi in the fungus gardens. A species of yeast also eats the bacteria. The result, as demonstrated by evolutionary biologist Cameron Currie, is a five-way symbiosis: ant, food fungus, parasitic fungus, actinobacteria, and yeast. Wood and leaves may be a good source of carbohydrates, thanks to fungi, but they are not good sources of nitrogen, which termites and ants, like all animals, need for the production of proteins. Many termites and leaf-cutter ants have nitrogen-fixing bacteria in their digestive systems, which convert atmospheric nitrogen gas into forms that the insects can use. In the tropical seasonal forests, many acacia trees (genus Acacia) are infested with Pseudomyrmex ants. The acacia tree has structures that feed

first entry the ants: nectaries that produce nectar and clusters of protein-rich food at the tips of immature leaflets. The ants chew holes in immature thorns and hollow them out (see photograph). The ants, including the queen, live inside of the thorns. In turn, the ants defend the acacia trees from herbivores and competitors. If a herbivorous insect or mammal begins to eat the foliage, the ants swarm and attack. If a vine begins to grow on the acacias, the ants chew it off. By eating the insects that land on the leaves, the ants are not merely defending the tree but are obtaining an extra source of food. The acacia trees remain green well into the dry season, when most other trees have lost their leaves. This makes the acacia trees a very visible target to herbivores, from which the ants protect them. A similar association is found in Old World tropics between ants of the genus Crematogaster and trees of the genus Macaranga. Agriculture is not merely a mutualism between a food species and an animal species that promotes its growth. It is an obligate mutualism. The termite and leaf-cutter ant gardens and the acacia trees may therefore qualify as agriculture. The termites, leafcutter ants, and Pseudomyrmex ants have no other food, and the fungi in their gardens live nowhere else. Without their ants, the acacia trees are quickly covered with vines. Some ants appear to be ranchers rather than farmers. Phloem sap in plants is sweet and is not toxic. Aphids have small mouthparts that they can insert into a single phloem cell. Aphids can therefore tap into pressurized sap. The pressure pushes more sap through the aphids than they can consume. Ants cannot tap into the phloem, but they can eat the leftover sap from the aphids. They do more than this, however. They protect the aphids, as a rancher would protect milk cows, from predators.

Ocean Mutualisms Mutualisms are as ubiquitous in the oceans as on land. Here are some examples: ●●

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Pseudomyrmex spinicola ants live in the thorns of acacia trees in tropical seasonal forests.  (Alex Wild)

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Coral reef fish line up at cleaning stations, where small fish crawl inside their mouths and remove parasites. Cleaner fishes of the species Labroides dimidiatus can clean 2,300 individuals of 132 fish species each day. Healthy embryos of the shrimp Palaemon macrocadtylus are covered with Alteromonas bacteria. The bacteria produce compounds that defend them against the fungus Lagenidium callinectes. If the bacteria are experimentally removed, the fungus kills the shrimp embryos. The antibacterial compound also works by itself in experimental treatments.

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mutualism  381 ●● ●● ●●

Up to 40 percent of a sponge’s weight is symbiotic bacteria. Fish guts, like those of marine iguanas, contain microbes that help them to digest algae. The crab Trapezia ferruginea and the shrimp Alpheus lottini protect reef corals from predation by the starfish Acanthaster planci. In return, the crab and the shrimp not only live safely in the crevices of the reef but they feed on mucus produced by the corals.

Ecological Rules of Mutualism Mutualism presents many interesting stories, but these stories add up to a tremendous impact upon the ecosystems of the world. One of the most common examples of mutualism is the lichen. A lichen is a sandwich of single-celled algae inside of layers of fungus. The algae produce food for themselves and the fungus through photosynthesis, while the fungus appears to protect the algae from light damage when they are dormant. Is a lichen one organism or two? Biologists have decided not to decide. They have assigned species names to the lichens, as well as to the fungal and algal symbionts. Lichens are able to grow in places where few other organisms can survive. For example, they grow on tree trunks in deciduous and coniferous forests and on rocks in grasslands. They are also the major ground cover in some environments such as the dry, northern edges of the tundra. In such places they are the major biological components of food production and the cycling of nutrients. “Reindeer moss” is actually a lichen (Cladonia rangiferina) and an important food source for reindeer. Lichens, which are very sensitive to toxic compounds, are also important indicators of air pollution. Lichens are therefore much more than an interesting story of symbiosis, but play a major role in some ecosystems. Mycorrhizae are fungi, of many different species, that live in plant roots. The plant feeds them with sugars from the root storage tissues. In return, the fungi extend their strands out into the soil, functioning as an extra set of tiny roots. They are especially effective at absorbing phosphorus from the soil, which then diffuses into the plant root. The mutualists are not deliberately helping one another out. The fungus obtains the phosphorus for its own use and cannot prevent the phosphorus from diffusing into the root. The ecological importance of mycorrhizae is difficult to overestimate. Many plant species rely on them to enhance their nutrient uptake and in some cases could not survive in poor soil without them. Many of the nutrients that pass through the food web begin as soil ions absorbed by mycorrhizae.

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Mutualisms are also important in the food web of the oceans. Cells of the diatom Hemiaulus haukii contain a photosynthetic bacterium, Richelia. The diatom carries out its own photosynthesis and does not need Richelia for this reason. However, like other cyanobacteria, Richelia can fix atmospheric nitrogen gas into a form that the diatom can use as fertilizer. In the portions of the ocean where this diatom is dominant, the mutualism stimulates growth by a factor of three and contributes 25 percent of the nitrogen in the food web. “To visualize the magnitude of this nitrogen addition,” says ecologist Mark Hay, “think of it as the mass of 1.5 million Harley-Davidson road king motorcycles, 7.3 million undergraduate students, or 157 million laptop computers.” It is possible to have mutualisms within mutualisms. Myxotricha paradoxa is a protist that lives in termite guts and allows termites to digest wood. Myxotricha appears to have cilia that allow it to swim. What appear to be cilia, however, are mutualistic bacteria embedded in the protist’s surface.

Conservation of Mutualism In order to protect the biodiversity of mutualists, it is necessary to protect the other species that interact with them. Here is one example. When there are no giraffe or elephant grazers, the acacia trees stop producing nectar, protein, and large thorns. Unless there are grazers to threaten the acacias, the mutualism begins to break down. It is also necessary to protect the habitats in which the mutualists live. If the habitat is suitable for one of the mutualists but not the other, both are doomed. This may be the case with cacti that survive but cannot reproduce without their mutualistic pollinators.

Mutualism and Humans Aside from the previous examples in which mutualism preserves human health, there are at least two major types of mutualism that humans have created. The first is agriculture. Humans have domesticated crop plants and livestock animals. Humans use them as food, but the crops and livestock also benefit, because humans plant, feed, and protect them. As science writer Michael Pollan points out, maize is one of the most successful plants in the world, and its success is due to the fact that humans have destroyed large areas of forest and prairie land and planted a gigantic lawn of corn. Moreover, as in the other examples of agriculture noted previously, humans and agricultural species have an obligatory mutual dependence. Agriculture is one of the main ways in which humans have transformed almost a third of the surface of the Earth into managed habitats.

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382 mutualism  382 The second way is by having pets. Humans keep billions of pet animals. The food that pets eat and the wastes that they produce have a major impact on the ecosystems of the Earth. Pets can be considered mutualists, because their companionship (and, in some cases, the protection that they offer) is a major psychological resource for humans. See also agriculture; biogeochemical cycles; coevolution; herbivory; lichens; pollination. Further Reading Arnold, A., et al. “Fungal endophytes limit pathogen damage in a tropical tree.” Proceedings of the National Academy of Sciences USA 100 (2003): 15,649–15,654. Banning, Jenifer L., et al. “Antifungal skin bacteria, embryonic survival, and communal nesting in four-toed salamanders, Hemidactylium scutatum.” Oecologia 156 (2008): 423–439. Bascompte, Jordi, and Pedro Jordano. “Plant-animal mutualistic networks: The architecture of biodiversity.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 567–593. Batra, L. R., ed. Insect-Fungus Symbiosis: Mutualism and Commensalism. New York: John Wiley, 1979. Becker, Matthew H., et al. “The bacterially produced metabolite violacein is associated with survival of amphibians infected with a lethal fungus.” Applied and Environmental Microbiology 75 (2009): 6,635–6,638. Bshary, R., and D. Schäffer. “Choosy reef fish select cleaner fish that provide high-quality service.” Animal Behaviour 63 (2002): 557–564. Clement, Lars W., et al. “Strategies of a parasite of the antAcacia mutualism.” Behavioral Ecology and Sociobiology 62 (2008): 953–962. Comstock, L., and M. Coyne. “Bacteriodes thetaiotaomicron: A dynamic, niche-adapted human symbiont.” Bioessays 25 (2003): 926–929. Dangerfield, J. M., et al. “The mound-building termite Macrotermes michaelseni as an ecosystem engineer.” Journal of Tropical Ecology 14 (1998): 507–520. Eckburg, Paul B., et al. “Diversity of the human intestinal microbial flora.” Science 308 (2005): 1,635–1,638. Fiala, B., et al. “Studies of a South East Asian ant–plant association: protection of Macaranga trees by Crematogaster borneensis.” Oecologia 79 (1989): 463–470. Fischer, R. C., et al. “Plants feed ants: food bodies of myrmecophytic and their significance for the interaction with Pheidole bicornis ants.” Oecologia 133 (2002): 186–192. Gaume, L., et al. “Ant-plant conflicts and a novel case of castration parasitism in a myrmecophyte.” Evolutionary and Ecological Research 7 (2005): 435–452. Grice, Elizabeth A., et al. “Topographical and temporal diversity of the human skin microbiome.” Science 324

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first entry (2009): 1,190–1,192. Summarized by Marx, Christopher J. “Getting in touch with your friends.” Science 324 (2009): 1,150–1,151. Hay, Mark E., et al. “Mutualisms and aquatic community structure: The enemy of my enemy is my friend.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 175–198. Heil, Martin, and Doyle McKey. “Protective ant-plant interactions as model systems in ecological and evolutionary research.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 425–454. Hill, M. “Intestinal flora and endogenous vitamin synthesis.” European Journal of Cancer Prevention 6 (1997): S43–S45. Hongo¯, Yuichi, et al. “Genome of an endosymbiont coupling N2 fixation to cellulolysis within protist cells in termite gut.” Science 322 (2008): 1,108–1,109. Izzo, T. J., and H. L. Vasconcelos. “Cheating the cheater: domatia loss minimizes the effects of ant castration in an Amazonian ant-plant.” Oecologia 133 (2002): 200–205. Jaenike, John, et al. “Adaptation via symbiosis: Recent spread of a Drosophila defensive symbiont.” Science 329 (2010): 212–215. Janzen, Daniel H. “Coevolution of mutualism between ants and acacias in Central America.” Evolution 20 (1966): 249–275. Oliver, Kerry M., et al. “Bacteriophages encode factors required for protection in a symbiotic mutualism.” Science 325 (2009): 992–994. Palmer, Todd M., et al. “Breakdown of an ant-plant mutualism follows the loss of large herbivores from an African savanna.” Science 319 (2008): 192–195. Summarized: Leslie, Mitch. “The importance of being eaten.” Science 319 (2008): 146–147. Pinto-Tomás, Adrián A., et al. “Symbiotic nitrogen fixation in the fungus gardens of leaf-cutter ants.” Science 326 (2009): 1,120–1,123. Raine, N. E., et al. “Guards and thieves: antagonistic interactions between two ant species coexisting on the same ant-plant.” Ecological Entomology 29 (2004): 345–352. Roth, R. R., and W. D. James. “Microbial ecology of the skin.” Annual Reviews of Microbiology 42 (1988): 441–464. Scott, Jarrod J., et al. “Bacterial protection of beetle-fungus mutualism.” Science 322 (2008): 63. Reviewed in: Berenbaum, May R., and Thomas Eisner. “Bugs’ bugs.” Science 322 (2008): 52–53. Stadler, Bernhard, and Anthony F. G. Dixon. “Ecology and evolution of aphid-ant interactions.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 345–372. Turner, J. Scott. “On the mound of Macrotermes michaelseni as an organ of respiratory gas exchange.”

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mycorrhizae  383 Physiological and Biochemical Zoology 74 (2001): 798–822. Usher, Kayley M., et al. “Exploring cyanobacterial mutualisms.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 255–273. Van der Heijden, M. G. A., et al. “Mycorrhizal fungal diversity determines plant biodiversity, ecosystem variability, and productivity.” Nature 396 (1998): 69–72. Woodhams, Douglas C., et al. “Symbiotic bacteria contribute to innate immune defenses of the threatened mountain yellow-legged frog, Rana muscosa.” Biological Conservation 138 (2007): 390–398.

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Xu, J., and J. I. Gordon. “Honor thy symbionts.” Proceedings of the National Academy of Sciences USA 100 (2003): 10,452–10,459. Youngsteadt, Elsa. “All that makes fungus gardens grow.” Science 320 (2008): 1,006–1,007. Yu, D. W. “Parasites of mutualisms.” Biological Journal of the Linnean Society 72 (2001): 529–546. ———, and N. E. Pierce. “A castration parasite of an antplant mutualism.” Proceedings of the Royal Society of London B (Biology) 265 (1998): 375–382.

mycorrhizae  See mutualism.

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N natural  selection  natural selection is the

ally cause varieties to be different enough that they would constitute different species. artificial selection, however, has not gone on long enough for this to happen. natural selection occurs within populations. individual organisms cannot evolve because they cannot undergo whole-body genetic changes. if mutations occur in somatic cells, which make up most of the body of an animal, the cells that contain the mutations will die when the organism dies. Only those mutations that occur in germline cells, either eggs or sperm or the cells that produce them, can be passed on to the next generation. therefore the genetic effects of evolution can only be observed in the next generation of the population. natural selection occurs because individuals within populations differ from one another in how successfully they reproduce. evolutionary theories before Darwin, such as lamarckism, were incorrectly based upon the transformation of an entire population or species, and/or as a result of changes within the individuals themselves. But Darwin’s insight was that, because some individuals in the population reproduce more successfully than others, over time the population begins to resemble the successful individuals. Biologist ernst Mayr said that by formulating the theory of natural selection, Darwin introduced population thinking into evolution, to replace typological thinking—that is, evolution occurs in populations of diverse individuals, rather than being the transformation of one type into another.

process by which evolution produces adaptation. Other processes, such as genetic drift, can cause evolution to occur, but in a random direction. Only natural selection guides the evolutionary process in a direction that produces adaptation to environmental and social conditions. evolution is the source of all biodiversity. natural selection is the process that was fi rst clearly explained by charles Darwin, although some earlier writers such as W. c. Wells, edward Blyth, and Patrick Mathew had presented fragments of the idea. natural selection was independently discovered by alfred Russel Wallace. Darwin not only demonstrated that evolution had occurred but also explained how it occurred. as a result, evolution became believable for the fi rst time. Darwin’s contemporaries largely accepted his demonstration that evolution had occurred, but the scientific community did not embrace natural selection for another 80 years. Sexual selection, which was also fi rst elucidated by charles Darwin, operates in a manner similar to natural selection. However, sexual selection usually produces arbitrary and sometimes outlandish characteristics that are not usually considered adaptation. Both Darwin and Wallace alluded to artificial selection, the process by which humans breed crops and livestock in desired directions, in crafting the phrase natural selection. in both cases, some individuals are selected to propagate and others are not; in natural selection, it is nature rather than humans that does the selecting. Both artificial and natural selection can produce genetic changes within populations and can cause divergence of populations into different varieties. either could eventu-

proCESS of NaTural SElECTIoN ernst Mayr summarized the process of natural selection as five facts and three inferences that can be 384

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natural selection  385 derived from those facts. All of these facts are part of the science of ecology, the study of the relationship between organisms and their living and nonliving environments. Therefore by elucidating the process of natural selection, Darwin was not only making evolution believable for the first time, but also inventing the science of ecology while he was at it. Fact 1.  Populations can grow exponentially. Because reproductive groups of individuals can multiply, populations grow in curves, not in lines. In a population of bacteria, one bacterium can produce two, but 1 million bacteria can produce 2 million bacteria during cell division. This allows populations to grow explosively. This will occur, of course, only in an unlimited environment. As Darwin wrote in The Origin of Species: There is no exception to the rule that every organic being naturally increases at so high a rate, that, if not destroyed, the earth would be covered by the progeny of a single pair. Even slow-breeding man has doubled in twenty-five years, and at this rate, in less than a thousand years, there would literally not be standing-room for his progeny. Linnaeus has calculated that if an annual plant produced only two seeds—and there is no plant so unproductive as this—and their seedlings next year produced two, and so on, then in twenty years there should be a million plants.

Darwin did some calculations for the Origin of Species (incorrectly, as it turned out) on the reproductive rate and population growth of elephants in an unlimited environment: The elephant is reckoned the slowest breeder of all known animals, and I have taken some pains to estimate its probable minimum rate of natural increase; it will be safest to assume that it begins breeding when thirty years old, and goes on breeding till ninety years old, bringing forth six young in the interval, and surviving till one hundred years old; if this be so, after a period of from 740 to 750 years there would be nearly nineteen million elephants alive, descended from the first pair.

Fact 2.  Populations sometimes grow, and sometimes become smaller, but tend to remain stable. Therefore something must be preventing population growth, either by repressing reproduction or by causing death. Darwin wrote: Lighten any check, mitigate the destruction ever so little, and the number of the species will almost instantaneously increase to any amount.

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Darwin insisted on evidence and on experimentation where possible. He dug and cleared a small plot of ground at his estate and laboriously marked each seedling that germinated. The total was 357. Of these, 295 seedlings died, mainly because slugs and insects ate them. He also counted the number of bird nests on his property in the spring of 1854 and again the spring of 1855 and estimated that during the intervening winter nearly four-fifths of the birds had died. Fact 3.  Resources are limited. Ultimately, if reproduction continued unabated, the world could not contain the offspring. However, resources are limited by much more than simply room in the world. Organisms need resources and ecosystem services that provide food, water, shelter, oxygen, and process their wastes. Each kind of organism is adapted to live in only a limited range of conditions; therefore, for a polar bear, it does not much matter how big the world is, but only how big the Arctic is, and for species that are limited to a single island or mountain or swamp, the world is pretty small. The disparity between limited resources and exponential population growth in human societies had been famously pointed out by economist Thomas Robert Malthus, and Darwin simply applied it to nature: “It is the doctrine of Malthus applied with manifold force to the whole animal and vegetable kingdoms . . .” These three facts lead to inference 1, which is the struggle for existence. In nearly all natural populations, there are not enough resources for all of the individuals to have all of the resources they need. Today scientists say that competition occurs in nearly all natural populations nearly all of the time. Sometimes competition is strong enough that scientists can actually observe the struggle. In a jungle, vines grow over trees, and trees crowd together, as if they are fighting for access to the light. In a desert, the bushes are evenly spaced across the landscape, because there is not enough water for any bush to grow close to another bush. Predators fight over a kill, and birds chase one another out of the choice territories. But even when it cannot be seen, competition can be inferred. Competition is the unavoidable result of exponential population growth and limited resources. As Darwin wrote: Nothing is easier than to admit in words the truth of the universal struggle for life, or more difficult—at least I have found it so—than constantly to bear this conclusion in mind . . . We behold the face of nature bright with gladness, we often see superabundance of food; we do not see or we forget, that the birds that are idly singing round us live on insects or seeds, and are thus constantly destroying life; or we forget how largely

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386 natural selection  386 these songsters, or their eggs, or their nestlings, are destroyed by birds or beasts of prey; we do not always bear in mind, that, though food may now be superabundant, it is not so at all seasons of each recurring year.

Darwin’s theory of evolution by means of natural selection severely shook the complacency of European science, which had comfortably assumed the divine creation and long-term stability of species. His invention of ecology had at least as great an effect on scientific and popular thought. Many people thought of the natural world as God’s vast and orderly garden, full of life. Darwin showed the natural world to be violent and full of death. To his readers, Darwin had shaken their view of the world—and they had not even gotten past chapter 3 (The Struggle for Existence) of his book, On the Origin of Species! The poet Alfred, Lord Tennyson, reflected the sadness not only of the death of individuals but the extinction of species in his poem In Memoriam, which is the origin of the famous phrase “red in tooth and claw.” (Tennyson published the poem before Darwin wrote his book.) The fact of extinction may have forced scholars to think about the fact that disease and death—often the result of the struggle for existence—were much more painful than they needed to be in a perfectly ordered world. Darwin experienced this firsthand through the death of his mother when he was young. Even without evolution, religious scholars had, and still have, to struggle with the “problem of natural evil.” Fact 4. Each individual in a population is unique. Each population contains a tremendous amount of diversity. Humans can easily observe this diversity in their own populations, but it is true of the populations of all other species as well, even if humans cannot recognize it. Darwin learned this not from other scientists, but from animal breeders, particularly pigeon fanciers. All the different breeds of pigeon had been selected from ancestral stocks of rock pigeons (Columba livia). These breeds included some with outlandish feathers, anatomy (for instance, the ability to inflate their crops massively), or behavior (such as the ability to tumble during flight). Since all of these breeds had come from rock doves, then all of their characteristics had to be present, but hidden, within the rock dove populations. Breeding brought out these traits, distilling them as one might distill brandy from wine. The first two chapters of the Origin described how artificial selection and the observation of natural populations showed the tremendous amount of diversity that they contained. Fact 5.  Much of the variability in populations is heritable. Darwin knew nothing about genetics.

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first entry He was apparently unaware of the writings of Gregor Mendel, which explained how traits could be passed from one generation to another. But every plant and animal breeder knew that this was the case. There was confusion about the mechanism. Many scientists held theories about varieties of Lamarckism, or the inheritance of acquired characteristics. Many also believed in “blending inheritance” in which parental traits blended permanently in their offspring, like blending different colors of paint. Mendel, in contrast, was one of the researchers who demonstrated that traits were inherited in a particulate rather than a blending fashion; that is, a trait could disappear in one generation and reappear in another, like mixing different colors of marbles rather than of paint. Darwin himself ended up accepting a variation of Lamarckism, which he called pangenesis, a theory which most evolutionary scientists today consider to be his only major blunder. The first inference, plus facts 4 and 5, give rise to inference 2, which is natural selection itself. In order to reproduce, an individual needs to obtain resources beyond just what is needed for survival. Because of the struggle for existence (inference 1), not all individuals in the population can reproduce or even survive. If all individuals in the population were alike, then the ones that prevailed would be due either to chance or to historical contingency, which might just be another form of chance. But since individuals are unique, then some of the individuals have what it takes to survive and reproduce more than others. For example, in a moist environment, some of the plants may have larger leaves and shallower roots than others. The plants with larger leaves could grow faster because they would have greater photosynthesis, and they would not waste their resources producing deep roots which are not needed in a moist environment. But if the trait cannot be passed on to the next generation, the superior survival and reproduction of the plants with larger leaves would not matter, since their offspring would not have leaves any larger than those of other plants. Natural selection is the differential reproduction of organisms in a population because of their genes. That is all that it is. If some genetically distinct individuals consistently reproduce more than others, natural selection occurs. Scientists may be able to determine what caused the superiority of some individuals over others, as in the case of Darwin’s finches, or they may not, as in the famous British study of the peppered moths. Either way, natural selection has occurred. As Darwin described it, Owing to [the] struggle [for existence], variations, however slight and from whatever cause proceeding, if they be in any degree profitable

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natural selection  387 to the individuals of a species, in their infinitely complex relations to other organic beings and to their physical conditions of life, will tend to the preservation of such individuals, and will generally be inherited by the offspring . . . I have called this principle, by which each slight variation, if useful, is preserved, by the term Natural Selection . . .

Inference 2 leads directly to inference 3, which is that if natural selection continues long enough, evolutionary change results in the population. The traits that confer superiority in natural selection, therefore in evolution, are not the same everywhere. There are countless pathways to success, in the natural world as in the human economy. The above example described successful plants in moist environments as having large leaves and shallow roots. In an arid environment successful plants would have small leaves (which waste less water than large leaves) and deep roots (that may be able to tap into new sources of water). In most cases, evolution can go in more than one direction, depending on the circumstances. To use one example close to home, the major pattern of evolution in the human lineage has been the increase in brain size, but in at least one case (the Flores Island people, Homo floresiensis), human brain size decreased during evolution.

Types of Natural Selection Evolutionary scientists generally classify natural selection into three types (see figure on page 388): 1. In stabilizing selection, the average individuals reproduce better than the extreme individuals. For example, in an environment with medium humidity, very large-leaved and very small-leaved individuals in a plant population would grow more slowly and reproduce less. Stabilizing selection reinforces the mean or average trait value by eliminating outlying variation. Stabilizing selection may be common in populations once a particularly successful combination of genes has been assembled. According to some evolutionary scientists, stabilizing selection has been the experience of nearly every species during most of its existence, resulting in long periods of evolutionary stasis between speciation events, a pattern known as punctuated equilibria. 2. In directional selection, individuals at one of the extremes reproduce better than either the average individuals or the individuals at the other extreme. If the environment of the population of plants described above became wetter, the largerleaved individuals would grow and reproduce better than the individuals with either medium or small leaves. A drier environment would favor the indi-

xviii+598_Biodiversity_F.indd 387

viduals with small leaves over all the others. Either of these would be directional selection. 3. In diversifying selection, the average individuals are at a disadvantage and the extreme individuals reproduce the most. During intense competition, the average individuals may compete most strongly. Individuals that are very small or very large might escape direct competition. As a result, the population may begin evolving in two directions at once. This process cannot continue as long as the individuals can all interbreed. If a reproductive barrier arises between the small and large individuals, they may begin to diversify into two species. Darwin neatly explained how a population could evolve, perhaps eventually becoming a new species. Natural selection does not itself explain how one species can evolve into two or more species. Reproductive isolation must also occur. Frequency-dependent selection is a special instance in which an individual has greater reproductive success not because of better adaptation to environmental conditions but simply from being rare. The most commonly cited example of frequency-dependent selection is that of sex ratios. If males are rare in a population, the average male will leave more offspring than the average female. Conversely, rare females will leave more offspring, on the average, than common males. Whichever sex is rare enjoys greater reproductive success. Frequencydependent selection is considered to be the main process by which most animal populations maintain an equal mix of males and females.

Limitations of Natural Selection Natural selection is not all-powerful. Below are examples of limitations upon the power of natural selection: ●●

●●

Physical constraints. Natural selection cannot cause the evolution of characteristics that violate the laws of physics and chemistry. For example, natural selection cannot produce a large animal with skinny legs. Also, the tallest trees in the world are about 350 feet (about 70 m) tall. Trees much taller than this are not possible, because there is a maximum height to which wood can conduct water, and the tallest redwoods may be very close to this maximum height. Large animals with wheels cannot evolve, for the wheel could not receive nutrition from the rest of the body through the axle. Phyletic constraints.  Once an evolutionary lineage has adopted a certain adaptation, this adaptation itself puts constraints on evolutionary change. It is not possible

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388 natural selection  388

●●

●●

for an animal to have an exoskeleton and to be large. Once arthropods evolved exoskeletons, large size was no longer an option in their lineage. Absence of genetic variation. Natural selection can only choose from among the genetic characteristics that are available in the population. These characteristics arise by chance mutations. Linkage of traits. Natural selection may be unable to select traits separately, if they are linked either on the same chromosome (as linkage groups) or in development. In flowers, petal size and stamen size share

first entry

●●

●●

developmental events, and natural selection cannot cause one to become bigger or smaller without the other. Plasticity and dispersal.  Organisms may respond to changes in environmental conditions by plasticity or acclimation or by dispersal to a new location. These are ways in which individual organisms can avoid becoming the victims of natural selection. Post-reproductive individuals. Natural selection cannot eliminate harmful mutations that have their effect when all or most of the organism’s reproduction has been completed. This is sometimes called the

Three types of natural selection. The top graphs indicate the frequency of people of different height categories in a population, with a few short people, many medium-sized people, and a few tall people. The solid line is before, the dashed line after, natural selection has occurred. If tall people reproduce more than medium or short people, directional selection causes the average height in the population to increase. If medium people reproduce the most, stabilizing selection causes the average height of the population to remain unchanged. If medium people reproduce the least, diversifying selection causes short people and tall people to dominate the population, which would have relatively few medium-sized people.

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natural selection  389

●● ●●

“kingpin principle,” based on a story about automobile manufacturer Henry Ford. He had his engineers study old Ford cars and find which part of the old cars was in the best condition. They reported that the kingpins were just like new. Ford told his factory managers to stop wasting their time making such good kingpins. There was no need for kingpins to last forever in a car that did not. Similarly, in organisms, there is no advantage for genes that promote the health and vigor of post-reproductive individuals. The future. Natural selection cannot anticipate the future and prepare for it. Group selection. Natural selection cannot favor characteristics that benefit the group but reduce the fitness of the individual that possesses them. Some adaptations result in harm for the individual (for example, worker bees that die after stinging a victim, and mother spiders that die when her spiderlings eat her) but these are compensated by an increase in inclusive fitness, an example of altruism. When pathogens infect a host, natural selection may favor those selfish lineages of pathogens that reproduce most rapidly, even if the host dies as a result. Natural selection may work against such selfish pathogens if the death of the host results in the death of the entire pathogen population or if the illness of the host causes other hosts to stay away from the sick individual, thus preventing the dispersal of any pathogens of that population to new hosts. But natural selection cannot result in individuals sacrificing their own fitness within a population.

Natural Selection Observed in Nature Below are just a few examples of natural selection that have been observed in nature. Stabilizing selection. Evolutionary biologists Arthur Weis and Warren Abrahamson studied insects that lay their eggs inside of plant stems. The grub releases a compound that causes the stem to produce a round swelling called a gall. The grub can develop, well fed, inside this gall. There are dangers from predators, however. Gall wasps can recognize galls and pierce their ovipositors into the gall, laying their eggs on the grub, and the wasp larvae eat the grub. Birds can also recognize galls and tear them open, to eat the protein-rich grub. Gall wasps prefer smaller galls; wasp parasitism therefore selects for larger galls. Birds prefer larger galls; bird predation therefore selects for smaller galls. The result is what looks like stabilizing selection for medium-sized

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galls but is actually a compromise of two processes of directional selection. Directional selection.  Soapberry bugs (Jadera haematoloma) pierce fruits of certain plants with their long beaks. They are native to the keys of Florida, where they obtained their food from native balloon vines. After 1925, landscapers introduced the golden rain tree, an Asian relative of the balloon vine but with smaller fruits, into central Florida. Soapberry bugs began to use the new trees as a food source. In central Florida, natural selection favored bugs with shorter beaks. Over the next few decades, the central Florida bug populations evolved shorter beaks, while the bugs in the keys retained their long beaks. Evolutionary scientists Scott Carroll and Christin Boyd documented this change by examining bug collections that had been made before and after the introduction of golden rain trees to central Florida. Diversifying selection. In populations of African black-bellied seedcrackers (a type of bird), individuals have either large or small beaks. These two beak sizes correspond to two different kinds of seeds (large v. small) that the birds eat. Juvenile birds have greater variation in beak size than adults. Evolutionary biologist Thomas Bates Smith found that the juveniles that survived were those that specialized most narrowly upon the available seed sizes. Among the large-beaked individuals, those with beaks too large or too small died, and among the small-beaked individuals, those with beaks too large or too small also died. Diversifying selection thus reinforced the large and the small beak sizes in this bird population.

Natural Selection Experiments Occasionally, natural selection can be verified in natural populations by manipulative experiments, as in these examples: Bacteria. Artificial selection of bacteria has produced strains of bacteria able to tolerate conditions very different from those to which the original bacterium was adapted. Anole lizards. Anoles are lizards that live in the Caribbean. Some very small Caribbean islands have no natural populations of anoles. Evolutionary biologist Jonathan Losos introduced anole lizards onto some of these islands. The islands differed in the relative amount of plant cover. Within 10 to 14 years, recognizably different forms of anole had apparently evolved on different islands. Guppies.  Guppies live in freshwater pools on the island of Trinidad. In some pools, there are relatively large predators that eat guppies of all sizes; in other pools, there are only small predators, which eat only small guppies. The guppies that live with

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390 natural systems agriculture  390 large predators have a more rapid life cycle, growing faster and reaching reproductive maturity sooner, than those that live with small predators. Evolutionary biologist David Reznick found some pools that had small predators, no large predators, and also no guppies. This was the perfect opportunity for an experiment. He predicted that if fast-growing guppies that had previously experienced large predators were exposed to this new environment, they would evolve into slower-growing forms. He performed the experiment and obtained the expected results.

Importance of Natural Selection to All of Society Evolution in general, and natural selection in particular, has been a subject of little interest to many students (and professors) in the health sciences and agriculture. Recent developments, however, have shown that it was disastrous for medical and agricultural professionals to ignore the process of natural selection. In particular, natural selection has led directly to the evolution of antibiotic-resistant bacteria. Natural selection in pathogenic bacteria is fastpaced, outrunning the ability of the medical industry to produce new antibiotics; it costs a lot of money and it kills thousands of people. The evolution of pesticide resistance in mosquitoes, flies, ticks, lice, and other disease vectors presents yet another public health menace. Quite literally, what you do not know about evolution can kill you. Natural selection also occurs everywhere and all the time in agricultural fields, as insects evolve resistance to pesticides and weeds evolve resistance to herbicides. The response of many farmers is to spray more, with less success, which results in both the poisoning of the environment and the loss of agricultural production. Medical and agricultural professionals, however, have found some degree of success by using the process of natural selection in their favor rather than letting it work against them. By using antibiotics and pesticides sparingly rather than abundantly, and by using mixtures of several types rather than a single type, they have been able to slow down the evolution of resistance. As ecologist Rachel Carson indicated, Darwin could not have imagined such a vindication of his theory. Evolutionary biologist Richard Dawkins referred to the “devastating elegance” by which natural selection explains complex and seemingly perfect adaptations. The evolution of such adaptations may seem highly improbable, but natural selection breaks the problem of improbability into small pieces. Instead of multiplying the improbabilities of evolution, it allows the accumulation of probabilities. Because of natural selection, evolution makes sense. See also adaptation; Darwin, Charles; Darwin’s finches; ecology; founder effect and

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first entry genetic drift; life history, diversity of; sexual selection; speciation; Wallace, Alfred Russel. Further Reading Balanyá, Joan, et al. “Global genetic change tracks global climate warming in Drosophila pseudoobscura.” Science 313 (2006): 1,773–1,775. Bates Smith, Thomas. “Disruptive selection and the genetic basis of bill size polymorphism in the African finch Pyrenestes.” Nature 363 (1993): 618–620. Carroll, Sean P. and Christin Boyd. “Host race radiation in the soapberry bug: Natural history with the history.” Evolution 46 (1992): 1,052–1,069. Conrod, William, and Erica Bree Rosenblum. “A desert Galapagos.” Natural History, May 2008, 15–18. Jones, Kristina N., and Jennifer S. Reithel. “Pollinator-mediated selection on a flower color polymorphism in experimental populations of Antirrhinum (Scrophulariaceae).” American Journal of Botany 88 (2001): 447–454. Losos, Jonathan B., K. I. Warheit, Thomas W. Schoener. “Adaptive differentiation following experimental island colonization in Anolis.” Nature 387 (1997): 70–73. Mayr, Ernst. What Evolution Is. New York: Basic Books, 2001. Reznick, David N., et al. 1997. “Evaluation of the rate of evolution of natural populations of guppies (Poecilia reticulata).” Science 275 (1997): 1,934–1,937. Sultan, Sonia. “What has survived of Darwin’s theory? Phenotypic plasticity and the Neo-Darwinian legacy.” Evolutionary Trends in Plants 6 (1992): 61–71. Turner, Paul E. “Cheating viruses and game theory.” American Scientist 93 (2005): 428–435. Weiner, Jonathan. “Evolution in action.” Natural History, November 2005, 47–51. Weis, Arthur E. and Warren G. Abrahamson. “Evolution of host plant manipulation by gall makers: Ecological and genetic factors in the Solidago-Eurosta system.” American Naturalist 127 (1986): 681–695. Zimmer, Carl. “Fast-reproducing microbes provide a window on natural selection.” New York Times, June 26, 2007. Available online. URL: http://www.nytimes. com/2007/06/26/science/26lab.html. Accessed August 8, 2011.

natural systems agriculture  Natural systems agriculture is an approach to food production that builds upon the principles of biodiversity and ecology, rather than ignoring them. It is the opposite of industrial agriculture. Industrial agriculture, which has predominated food production in industrial countries for more than a century, seeks to eliminate biodiversity and ecology as much as possible from food production. An industrial farm consists, as far as possible, of one

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natural systems agriculture  391 species—a single variety of a single crop. All other species are eliminated, as far as possible, by chemical poisons. The soil exists only to temporarily hold onto chemical fertilizers. Soil loss through wind and water erosion is considered an acceptable expenditure; the use of more fertilizer can compensate for it. Some kinds of organic agriculture are very similar to industrial agriculture except that toxic chemicals are not used. It has been increasingly obvious even to industrial farmers that industrial agriculture cannot continue very far into the future. It is totally dependent upon fossil fuels, not only to make and apply the chemicals but to process and transport food from huge centralized farms. If soil loss continues, the only alternative will be hydroponic food production, in which food is grown, very expensively, in water, usually in greenhouses. It has also become obvious that the laws of ecology and evolution will not go away just by being ignored. Industrial agriculture itself creates perfect conditions for the continued eruption of pest populations and of resistance of those pests to the chemicals intended to control them. Natural systems agriculture was the insight of Wes Jackson, a geneticist who started The Land Institute in Salina, Kansas, in the 1970s. The Institute acquired some farmland and some adjacent intact tallgrass prairie. Jackson and later other scientists undertook the task of learning about food production by studying the nearby prairie. The following principles emerged, among others: ●●

●●

The prairie built up soil instead of losing it, for two reasons. First, the deep roots of the grasses and forbs prevented the mineral components from eroding and continually added humus. Second, there was never any season of the year in which the prairie soil was exposed to erosion. Even immediately after a fire, the prairie sod was thick with roots. Industrial agriculture, in contrast, was based on plants with shallow roots which lived only for part of a year, leaving bare soil exposed during late fall, winter, and early spring. Any agriculture that intends to continue indefinitely into the future must use perennial crops to prevent soil erosion. The prairie did not have pest outbreaks in the way that industrial farms did. Prairies have few weeds, since the sod is thick. Further, the mixture of species in the prairie (a polyculture) prevented any specialist herbivore populations from building up to excessive levels. Industrial agricultural

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●●

monocultures encourage pest population explosions. While no farm may withstand a horde of generalist herbivores such as grasshoppers that can eat anything, a polyculture farm resists specialist herbivores much more readily than a monoculture farm. And while these pests can evolve resistance to chemical pesticides, they cannot evolve resistance to a low density of their food base. The prairie does not need inputs of chemical fertilizer. The prairie not only holds onto its soil nutrients better than an industrial farm, but the mixture of species includes leguminous plants, which have nitrogen-fixing bacteria in their roots.

Research on natural systems agriculture has repeatedly shown that perennial polyculture farms are superior to industrial farms in all of the ways stated above. The big challenge for natural systems agriculture is to develop perennial crops and poly­ culture cropping systems that have a consumer market. There are virtually no wild prairie species that very many people want to eat. The Land Institute and affiliated researchers at a few universities in various countries are working on hybridization between major crops and their wild perennial relatives (for example, between annual wheat Triticum aestivum and wild wheatgrass Thinopyrum intermedium). The researchers select the hybrids that produce the most marketable seeds and that have perennial traits. Because industrial agriculture receives so much more funding (at public expense) and has so many more researchers compared to natural systems agriculture, a marketable alternative to industrial agriculture cannot be expected to emerge very soon. Many farmers use one or more parts of natural systems agriculture. Very few farmers (as opposed to orchardists) grow perennial crops, but many of them use conservation tillage, which allows stubble to remain on the surface of the soil after harvest, which reduces soil erosion and encourages the buildup of humus. Many farmers use contour plowing, in which the plowed ridges slow down the movement of water and thus reduces water erosion of soil. Many farmers now plant more than one kind of crop in adjacent strips, a process called strip-cropping, that somewhat mimics natural polycultures. These practices have been partly successful, but still retain enough industrial elements that they cannot make agriculture sustainable in the long run. See also biodiversity, resources for agriculture; communities, ecological; grasslands and savannas; Jackson, Wes; nitrogen cycle; population biology; resistance, evolution of.

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392 Neogene period, biodiversity in  392 Further Reading Cox, T. S., et al. “Prospects for developing perennial grains.” BioScience 56 (2006): 649–659. Glover, Jerry D., et al. “Future farming: A return to roots?” Scientific American, August 2007, 82–89. ———, et al. “Increased food and ecosystem security via perennial grains.” Science 328 (2010): 1,638–1,639. Scherr, Sara J., and Jeffrey A. McNeely, eds. The Science and Practice of Ecoagriculture. Washington, D.C.: Island Press, 2007.

Neogene period, biodiversity in  The Neo-

gene period (23 to 2.5 million years ago) was the second period of the Cenozoic era. It followed the Paleogene period; the Quaternary period followed it. The Neogene period is the second part of what has traditionally been called the Tertiary period, consisting of the Miocene and Pliocene epochs. Scientists have divided the Tertiary into Paleogene and Neogene periods largely because the climates of the two periods were different on a worldwide scale (see table). Climate. Though climatic conditions were warmer and wetter than those of today and forests remained widespread, the Neogene period was cooler and drier than the Paleogene period. Ice sheets covered much of Antarctica, which was forested in the Paleogene. Oxygen and carbon dioxide in the atmosphere were nearly at their modern levels; carbon dioxide was at preindustrial levels, which were lower than today. As more and more water was frozen in glaciers, ocean levels fell. About 5 million years ago, the Mediterranean Sea dried up and became a salt flat and the climate of much of Africa became arid. Continents. The continents assumed their modern arrangement, with slight exceptions. For example, North and South America were not yet connected by the isthmus of Panama. This slight difference was important, however. Ocean currents flowed between North and South America, allowing warm tropical water to reach the Arctic Ocean and prevent extensive ice formation. Marine life. Life in the Neogene oceans closely resembled that of modern times (see figure): ●● ●●

Invertebrates.  Ocean invertebrates were very similar to those of today. Vertebrates.  Bony fishes and sharks continued to diversify in the oceans, as did the toothed whales, baleen whales, porpoises, and dolphins. The largest known shark, Carcharodon megalodon, swam in the Neogene oceans. It grew up to 49 feet (15 m) in length.

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first entry

Multicellular Biodiversity   in the Neogene Period Conditions Atmospheric oxygen

8% above modern level

Atmospheric carbon dioxide

At preindustrial levels (20% below modern level)

Global temperature

same as today

Sea level

similar to today

Approximate number of families* Continental

1,300

Marine

1,100

Total

2,400

Examples of marine animals Carcharodon megalodon

shark

Eurhinodelphis longirostris

dolphin

Gadella sp.

bony fish

Hoploparia gazdzicki

lobster

Lepas kuwayamai

barnacle

Zygophyseter varolai

toothed whale

Examples of continental animals Australopithecus afarensis

bipedal ape

Bison paleosinensis

bison

Callicovatellus petrodytes

beetle

Capricamelus gettyi

camel

Coluber dolnicensis

racer snake

Equus simplicidens

horse

Gigantocamelus spatulus

giraffe

Hipparion forcei

horse

Lyssomanes sp.

spider

Mertensiella mera

salamander

Orrorin tugenensis

bipedal ape

Paranthropus robustus

bipedal ape

Pliohippus sp.

horse

Voltinia dramba

butterfly

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Neogene period, biodiversity in 393 Examples of land plants Acer pohangense

maple

Alnus kefersteinii

alder

Artemisia sp.

sagebrush

Carya protojaponica

hickory

Celtis rusingensis

hackberry

Distichlis sp.

grass

Ginkgo biloba

ginkgo

Lophocereus schottii

cactus

Pinus griffithii

pine

Quercus lonchitis

oak

*Based on Benton

Continental life. Plants and animals continued to thrive and diversify not only in the extensive forests but also in the world’s first grasslands and deserts: ●





rion migrated from north america, where all previous horses had lived, into eurasia, becoming the ancestor of all Old World horse species. like earlier horses, Hipparion had three toes, but the two outer ones were vestigial and did not touch the ground. Modern humans evolved during this time, fi rst in the dry forests, then in the savannas, of africa. Further reading arnold, caroline. Giant Shark: Megalodon, Prehistoric Super Predator. new york: Houghton Mifflin, 2000. Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Bianucci, Giovanni, and Walter landini. “Killer sperm whale: a new basal physeteroid (Mammalia, cetacea) from the late Miocene of italy.” Zoological Journal of the Linnaean Society 148 (2006): 103–131. Fortelius, Mikael, et al. “late Miocene and Pliocene large land mammals and climatic changes in eurasia.” Palaeogeography, Palaeoclimatology, and Palaeoecology 238 (2006): 219–227. Govers, Rob. “choking the Mediterranean to dehydration: the Messinian salinity crisis.” Geology 37 (2009): 167–170. lindsay, everett H., et al. “Pliocene dispersal of the horse Equus and late cenozoic mammalian dispersal events.” Nature 287 (1980): 135–138. Osborne, colin P. “atmosphere, ecology, and evolution: What drove the Miocene expansion of c4 grasslands?” Journal of Ecology 96 (2008): 35–45.

Plant life. Many modern genera of trees were in existence in the extensive forests. Species of cactus and grass, as well as many herbaceous wildflowers, spread in the grasslands and deserts. not only did grasses as a whole expand their range, but in particular the c 4 grasses, which have a type of photosynthesis that is particularly effective in hot, dry climates. these grasses may also have spread because c 4 photosynthesis is effective at low concentrations of carbon dioxide. atmospheric carbon levels were lower during the neogene than they had ever been in the history of the earth. Invertebrates. all major groups of terrestrial invertebrates had evolved before the neogene period. Ve r t e b ra t e s . M o d e r n groups of freshwater fi shes, amphibians, and reptiles continued to diversify. Mammals and birds were in the evolutionary lineages that are most common today. Horses adapted to the Diprotodon, a mammal of the Neogene period, was the largest marsupial spreading grasslands. Hippa- that ever lived.

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394 niche  394 Retallack, Gregory J. “Middle Miocene fossil plants from Fort Ternan (Kenya) and evolution of African grasslands.” Paleobiology 18 (1992): 383–400. ———. “Neogene Expansion of the North American Prairie.” Palaios 12 (1997): 380–390. Stanley, Steven M. Children of the Ice Age: How a Global Catastrophe Allowed Humans to Evolve. New York: W. H. Freeman, 1998.

niche  See competition, ecological. nitrogen cycle  The nitrogen cycle is the move-

ment of nitrogen atoms through the ecosystems of the Earth: through the atmosphere, food webs, and soils. It is a cycle because it begins and ends with nitrogen gas (N2) in the atmosphere. Organisms control the cycling of nitrogen atoms. The atmosphere consists mostly of nitrogen gas (N2). Because of this, there would seem to be no problem with the availability of nitrogen atoms to any organism on Earth. N2 , however, is virtually useless to most organisms. Nearly the only way that nitrogen atoms become available to organisms is through nitrogen fixation, a process carried out only by a few kinds of bacteria. In this process, nitrogen gas is made into ammonia (NH3). Once the ammonia is formed, microorganisms and plants can change it into compounds such as nitrates (NO3 -). Plants absorb and use ammonia and nitrates from the soil or from the nitrogen-fixing bacteria in the nodules of the roots of some plants. Biological nitrogen fixation is carried out by the nitrogenase enzyme. Nitrogenase operates most efficiently in the presence of relatively low concentrations of O2 . Among the microorganisms that fix nitrogen are the cyanobacteria and the nitrogenfixing bacteria: ●●

●●

Cyanobacteria are photosynthetic. Most of them live in rivers, lakes, and oceans. Nitrogenase is often found in specialized cells called heterocysts, which shield the nitrogenase from high concentrations of O2 found in atmosphere and water. Because the growth of cyanobacteria is not limited by the availability of nitrates or ammonia in the water, their populations may grow explosively (a process called eutrophication) if phosphates become abundant, as when water is polluted by even nontoxic concentrations of phosphate-containing detergents. Most nitrogen-fixing bacteria (in the genera Nitrobacter and Nitrosomonas) live inside

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first entry of the roots of certain plants, although many live independently in the soil. Many of these plants (beans, clover, alfalfa, and locust and acacia trees) are in the legume family Fabaceae. The roots of these plants have lumps called nodules which contain many nitrogen-fixing bacteria. Leguminous plants can obtain ammonia directly from these nodules. Other plants, such as alders, contain a different group of nitrogen-fixing bacteria, in the genus Frankia. When the leguminous plants die, decomposers consume them, breaking down their molecules. Major waste products of this decomposition are NH4+ and NO3 -, which accumulate in the soil. Plants that do not have nitrogen-fixing bacteria in their roots obtain nitrogen atoms from these soil reserves of NH4+ and NO3 -. Animals obtain the nitrogen atoms that they need by eating leguminous or other plants or by eating other animals. When these plants or animals die, decomposers release NH4+ and NO3 from them as well. The NH4+ and NO3 - released by decomposers enter the soil slowly, whereas the NH4+ and NO3 - fertilizers used by farmers are applied in large quantities. Much of the NO3 - that is applied to farmlands washes through the soil and into rivers or down into the underground water supplies from which people drink. If nitrogenous ions accumulated indefinitely in the soil, they would reach toxic levels. This does not occur, for two major reasons. First, water washes nitrates out of the soil, and they travel through streams and rivers to the ocean. There they accumulate, eventually ending up in sediments which are made into rocks. These rocks, millions of years later, can contribute nitrates to the soil that is formed from them. Ammonium clings more tightly to clay particles in the soil, but also eventually leaches from soil. Second, denitrifying bacteria can change soil nitrogen compounds back into nitrogen gas, which eventually returns to the atmosphere, completing the cycle. Farmers sometimes grow leguminous plants such as clover during the season when their principal crop is not under cultivation. Because they have nitrogenfixing bacteria in their roots, the clover is rich in nitrogen compounds. The farmers then plow the clover into the soil during spring planting. Two advantages result from this practice. First, the leguminous plants protect the soil from erosion during the late fall, winter, and early spring. Second, when the plants decompose in the soil, abundant nitrates are released. More often, farmers will practice crop rotation in which they plant a leguminous crop one year and another crop the next. They harvest the leguminous crop, thus remov-

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nitrogen cycle  395 ing some of the nitrate that would otherwise have returned to the soil. However, the leaf litter and the dead roots from the leguminous crop contribute some nitrate to the soil. This practice reduces the amount of fertilizer the farmers need to apply. Humans have had a tremendous impact on the global nitrogen cycle, primarily by the application of artificial fertilizers. Some bacteria produce nitrous oxide (N2O), which is a pollutant and greenhouse gas; the overuse of fertilizers has caused atmospheric levels of nitrous oxide to increase. See also biogeochemical cycles; ecosystems; rivers, streams, ponds, and lakes.

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Further Reading Falkowski, Paul G. “Evolution of the nitrogen cycle and its influence on the biological sequestration of CO2 in the ocean.” Nature 387 (1997): 272–275. Galloway, James N. “The global nitrogen cycle: Changes and consequences.” Environmental Pollution 102 (1998) supplement: 15–24. Leigh, G. J. The World’s Greatest Fix: A History of Nitrogen and Agriculture. New York: Oxford University Press, 2004. Vitousek, Peter M., et al. “Human alteration of the global nitrogen cycle: Sources and consequences.” Ecological Applications 7 (2007): 737–750.

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O oligocene  epoch  See Paleogene period,

animals more than tripled over that of the cambrian period. this was partly due to an increasing specialization in the ways that the animals obtained food. it was also partly due to the formation of the fi rst reefs, though the corals that formed them were of classes that are now extinct, and many reefs were formed by sponges. When the reefs formed, they created many new habitats for other swimming and crawling and sessile animals.

biodiversity in.

ordovician  period,  biodiversity  in  the Ordovician period (510 to 440 million years ago) was the second period of the Paleozoic era. it followed the cambrian period and preceded the Silurian period. an average of about 400 families of marine organisms existed during the Ordovician, ● Invertebrates. the most abundant group compared to 1,000 marine families (and 2,200 total of arthropods was the trilobites; modern families) today. forms of arthropods such as crabs were rare. Climate. Oceans were warm around equatothe early Ordovician period, with about 60 rial continents, but cool around the mass of southtrilobite families, was the peak of trilobite ern continents. there was little multicellular life diversity. the fi rst bivalve and cephalopod on the continents to be affected by terrestrial climollusks evolved. large cephalopod molmate. atmospheric oxygen levels were much lower, and carbon dioxide levels much higher, than today. Global temperatures were also higher than today (see table on page 397). Continents. Oceans separated the continents of laurentia, Baltica, Siberia (these three continents today dominating the northern Hemisphere) and Gondwana (today, the southern continents). Sea level was much higher than today—almost 700 feet (over 200 meters) higher than modern oceans. Marine life. almost all organisms lived in the oceans and freshwaters at this time (see fig- Eurypterids (also called sea scorpions) were some of the largest predators ure). By the end of the Ordovician in the Ordovician oceans. They were larger than, and may have preyed period, the diversity of marine upon, some early fishes. 396

xviii+598_Biodiversity_F.indd 396

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Ordovician period, biodiversity in  397 Multicellular Biodiversity   in the Ordovician Period Conditions Atmospheric oxygen

68% of modern level

Atmospheric carbon dioxide

12 times modern level

Global temperature

3°F (2°C) higher than today

Sea level

650 feet (200 m) higher than today

Approximate number of families* Continental

0

Marine

400

Total

400

Examples of marine animals Astrapsis splendens

jawless fish

Amplexograptus sp.

hemichordate

Asaphus kotlukovi

trilobite arthropod

Caleidocrinus multiramus

crinoid echinoderm

Cysaster stellatus

echinoderm

Endoceras sp.

cephalopod mollusk

Glyptarca sinensis

bivalve mollusk

Panderodus gracilis

conodont fish

Platystrophia ponderosa

brachiopod

Protaraea richmondiensis

coral

Pycnapsis splendens

ostracoderm fish

*Based on Benton

●●

lusks such as Endoceras had cone-shaped shells. Among the echinoderms were the stalked crinoids such as Caleidocrinus. Vertebrates. The only vertebrates were fishes, jawless descendants of the early fishes of the Cambrian period. Astrapsis had no jaws or fins; only its tail protruded outside a

xviii+598_Biodiversity_F.indd 397

bony armor that covered its body. This fourinch (10-centimeter) fish presumably used its simple tubelike mouth to filter food from the ocean floor. Larger jawless armored fishes included Pycnapsis. Continental life. Terrestrial life-forms have not been clearly confirmed from the Ordovician period. Spores characteristic of primitive land plants and trace fossils of animal activity have been found from the later part of this period. Extinctions.  One of the great mass extinctions occurred at the end of the Ordovician period. It is estimated that 26 percent of families, representing 83 percent of species, became extinct by the end of the Ordovician. While the continent that later became North America and Europe was equatorial and surrounded by tropical reefs, the large Gondwanan continent (which today exists as South America, Africa, Australia, Antarctica, and fragments of other land masses) was at the South Pole. Not only did Gondwanan weather become colder, but ocean levels dropped as glaciers formed around the pole, and this devastated tropical reefs. The return of warm weather and the melting of glaciers toward the end of the Ordovician may also have caused stagnation of deep-sea waters. Further Reading Adachi, Natsuko, et al. “Early Ordovician reef construction in Anhui Province, South China: A geobiological transition from microbial- to metazoan-dominant reefs.” Sedimentary Geology 220 (2009): 1–11. Benton, Michael. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Buatois, Luis A., et al. “The changing face of the deep: Colonization of the early Ordovician deep-sea floor, Puna, northwest Argentina.” Palaeogeography, Palaeoclimatology, and Palaeoecology 280 (2009): 291–299. Cope, John C. W. “Diversification and biogeography of bivalves during the Ordovician period.” Geological Society, London, Special Publications 194 (2002): 35–52. Webby, Barry D., et al., eds. The Great Ordovician Biodiversification Event. New York: Columbia University Press, 2004.

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P paleocene  epoch  See Paleogene period,

large increase in temperature (the Paleocene-eocene thermal Maximum). Due to its brevity and the lack of evidence of other causes, this event may have resulted from the sudden emergence of methane from continental shelves, similar to one of the factors that contributed to the Permian extinction. Fossils from that time indicate a sudden increase in the carbon isotope that is common in organisms. it took only 20,000 years for the global average temperature to increase almost 11°F (6°c). this is about the same rate that global temperatures are increasing today, which is one reason that the greenhouse effect is considered the most important ecological crisis of modern times. the rapid increase in global atmospheric and oceanic carbon also made the oceans acidic. this may help to explain why there was so much extinction of shelled marine organisms at that time, although other groups of organisms were not greatly affected. the regrowth of forests all over the world brought the high levels of atmospheric carbon back down. Continents. the northern and southern continents were largely separate from one another during the Paleogene. as the continents continued to move, connections began to form between the northern and southern continents. the subcontinent of india collided with the eurasian continent before the end of the Paleocene, about 34 million years ago, and began to form the Himalayas. europe and north america were just beginning to separate at the beginning of the Paleogene. Marine life. life in the Paleogene oceans closely resembled that of modern times:

biodiversity in.

paleogene  period,  biodiversity  in  the

Paleogene period (65 to 23 million years ago) was the fi rst period of the cenozoic era. it followed one of the mass extinctions which occurred at the end of the cretaceous period; the neogene period followed it. the cenozoic era is also known as the age of Mammals, because after the extinction of the dinosaurs the mammals had opportunity to evolve into tremendous diversity, including many large forms, including the fi rst fully aquatic mammals. the Paleogene period is the fi rst part of what has traditionally been called the tertiary period, consisting of the Paleocene, eocene, and Oligocene epochs. Scientists have divided the tertiary into Paleogene and neogene periods largely because the climates of the two periods were different on a worldwide scale (see table on page 399). Climate. Warm moist conditions that allowed extensive forests were widespread in the Paleogene period. the temperature difference between the equator and the poles was only half as great as it is today. Forests grew near the north and South Poles. Scientists estimate that conditions were warm enough that the trees in the far north did not need to be deciduous to avoid snowfall in winter. they were deciduous, scientists have concluded, because of the half year of darkness rather than because of cold temperatures. the land surface of the earth was virtually covered with forests at this time. Before the end of the Paleogene, ice sheets had begun to form in antarctica. about 55 million years ago, at the end of the Paleocene epoch, the earth experienced a brief and



Invertebrates. all modern groups of invertebrates were not only in existence but were

398

xviii+598_Biodiversity_F.indd 398

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Paleogene period, biodiversity in  399

●●

dominant. Ammonites (large cephalopod mollusks with coiled shells) had become extinct during the Cretaceous extinction. Vertebrates. All of the completely marine reptiles had become extinct during the Cretaceous extinction. At the beginning of the Paleogene, the dominant marine vertebrates were bony fishes and sharks. Very soon after the Cretaceous extinction, the first whales began to evolve. Pakicetus inachus was a terrestrial mammal that spent a lot of time in the water beginning about 56 million years ago. Ambulocetus natans lived in shallow waters about 50 million years ago and had hind legs more adapted to swimming than to walking. Like modern whales, Ambulocetus had no external ears—an aquatic adaptation. Rodhocetus, which lived about 47 million years ago, was almost exactly intermediate between Pakicetus and modern whales; it still had front and hind legs. Basilosaurus cetoides was a whale that lived about 40 million years ago. Its hind legs were becoming vestigial: they were only two feet (0.6 m) long compared to the animal’s body length of 60 feet (18 m). Modern whales do not have hind legs at all, although they have vestigial hip bones. These animals form a perfect series of intermediates in whale evolution. By the end of the Paleogene, both lineages of modern whales (baleen and toothed) had differentiated. The toothed whale Squalodon used echolocation, like modern whales and dolphins. Aetiocetus cotylaveus was a baleen whale, but its blowhole was only halfway up its face rather than on the top of the head as in modern whales.

Continental life.  Plants and animals thrived and diversified in the worldwide forests of the continents: ●●

●●

Plant life.  Many modern genera of trees were in existence in the worldwide forests. All modern groups of conifers, including pines, existed by this time. Bananas grew in what is now Oregon. There were not any extensive grasslands or deserts until the Neogene period, but species of cactus and grass existed during the Paleogene: the grasses probably lived along disturbed riversides, and cactuses may have been epiphytes, as many are today. Invertebrates. All major groups of terrestrial invertebrates, such as ants and butterflies, had evolved by the Paleogene period.

xviii+598_Biodiversity_F.indd 399

Multicellular Biodiversity   in the Paleogene Period Conditions Atmospheric oxygen

30% above modern level

Atmospheric carbon dioxide

40% above modern level

Global temperature

7°F (4°C) above modern level

Sea level

180 feet (110 m) higher than today

Approximate number of families* Continental

1,200

Marine

1,000

Total

2,200

Examples of marine animals Acanthonemus sp.

bony fish

Aetiocetus cotylaveus

baleen whale

Aturia sp.

cephalopod mollusk

Basilosaurus cetoides

whale ancestor

Enoploclytia gardnerae

crustacean

Heliobatis radians

ray

Notorynchus serratissimus

shark

Rodhocetus balochistanensis

whale with legs

Squalodon sp.

toothed whale

Examples of continental animals Ambulocetus natans

whale ancestor

Aquilavis hypogaeus

hawk

Arfia opisthotoma

small carnivorous mammal

Borealosuchus formadibilis crocodile Brontotherium gigas

large grazing mammal

Champsosaurus gigas

freshwater reptile

Folisaurus boutersemensis

lizard

Gastornis giganteus

large predatory ground bird

Hyracotherium leporinum

horse ancestor

Leptoganga sepultus

dove

Mesohippus latidens

primitive horse

Miacis rosei

carnivore mammal

Monotrematum sudamericanum

monotreme mammal (continues)

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400 Paleogene period, biodiversity in  400 Multicellular Biodiversity   in the Paleogene Period (continued) Necrobyas harpax

owl

Oxyaena lupina

small carnivorous mammal

Pakicetus inachus

whale ancestor

Palaeochiropteryx tupaiodon

bat

Paraceratherium transouralicum

large grazing mammal

Patriofelis ferox

small carnivorous mammal

Priscacara serrata

freshwater bony fish

Protochelydra zangerli

turtle

Pseudoloris godinoti

primate

Ptilodus sp.

multituberculate mammal

Simimys simplex

rodent

Titanoboa cerrejonensis

snake

Tritemnodon agilis

small carnivorous mammal

Vanessa amerindica

butterfly

Xenopus romeri

frog

Examples of land plants Acacia mahengense

acacia

Alnus parvifolia

alder

Betula leopoldae

birch

Ensete oregonense

banana

Eopuntia douglassii

cactus

Fagus pacifica

beech

Ginkgo dissecta

ginkgo

Juglans clarnensis

walnut

Larix altoborealis

larch

Macginitiea gracilis

sycamore

Metasequoia occidentalis

redwood

Pharus sp.

grass

Pinus andersoni

pine

Populus cinnamomoides

poplar

Quercus nevadensis

oak

Ulmus woodii

elm

  *Based on Benton

xviii+598_Biodiversity_F.indd 400

first entry ●●

Vertebrates.  Modern groups of freshwater fishes, amphibians, and reptiles continued to diversify (see figure). The snake Titanoboa was as long as a bus and weighed as much as a car. At the beginning of the Paleogene, most of the mammals were in groups that are now extinct, such as the multituberculates. The ferretlike Tritemnodon, the doglike Arfia, the catlike Patriofelis, and the hyenalike Oxyaena were not related to modern ferrets, dogs, cats, or hyenas, but were all creodonts—an evolutionary lineage that is now extinct. The largest land mammals to ever exist, such as the rhinoceros-like Brontotherium, evolved into the role vacated by the extinction of the dinosaurs. The largest was Paraceratherium, which was 16 feet (five meters) tall at the shoulder; its head was 25 feet (7.5 meters) above the ground, and its skull was almost four and a half feet long (1.3 meters). The earliest horses evolved— Hyracotherium in the early Paleogene and Mesohippus in the late Paleogene. By the end of the Paleogene, modern mammal groups had evolved, including bats, rodents, and doglike carnivores. In addition to some modern types of birds such as pigeons, hawks, and owls, there were large predatory birds that ran on the ground. There were swifts, but small hummingbirds (their close relatives) had not yet evolved.

See also Cretaceous extinction; greenhouse effect. Further Reading Bains, S., et al. “Termination of global warmth at the Palaeocene/Eocene boundary through productivity feedback.” Nature 407 (2000): 171–174. Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Dickens, G. R., et al. “A blast of gas in the latest Paleocene: Simulating first-order effects of massive dissociation of oceanic methane hydrate.” Geology 25 (1997): 259–262. Gingerich, Philip D., et al. “Hind limbs of Eocene Basilosaurus: evidence of feet in whales.” Science 249 (1990): 154–157. ———, et al. “New whale from the Eocene of Pakistan and the origin of cetacean swimming.” Nature 368 (1994): 844–847. Head, J. J., et al. “Giant boid snake from the Palaeocene neotropics reveals hotter past equatorial temperatures.” Nature 457 (2009): 715–717. Jahren, A. Hope. “The Arctic forest of the Middle Eocene.” Annual Review of Earth and Planetary Sciences 35 (2007): 509–540.

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parasitism 401 Janis, christine. “Victors by default: the mammalian succession.” in The Book of Life: An Illustrated History of the Evolution of Life on Earth, edited by Stephen J. Gould. new york: norton, 2001. Katz, M. e., et al. “Uncorking the bottle: What triggered the Paleocene/eocene thermal maximum methane release.” Paleoceanography 16 (2001): 667. Köhler, M., and S. Moyà-Solà. “a finding of oligocene primates on the european continent.” Proceedings of the National Academy of Sciences USA 96 (1999): 14,664–14,667. labandeira, conrad c., et al. “a dendroctonous bark engraving (coleoptera: Scolytidae) from a Middle eocene Larix (coniferales: Pinaceae): early or delayed colonization?” American Journal of Botany 88 (2001): 2,026–2,039. Shellito, cindy J., and lisa c. Sloan. “Reconstructing a lost eocene paradise: Simulating the change in global floral distribution at the initial eocene thermal maximum.” Global and Planetary Change 50 (2006): 1–17. Simmons, nancy B., et al. “Primitive early eocene bat from Wyoming and the evolution of flight Two mammals of the Paleogene period. (A) Uintatherium was a large and echolocation.” Nature 451 browsing mammal, one of the largest mammals that ever lived. (B) (2008): 818–821. Eurotamandua had adaptations for eating ants, even though it was probSluijs, a., et al. “Subtropical arctic ably not an ancestor of the modern anteater. Ocean temperatures during the Palaeocene/eocene thermal maximum.” Nature 441 (2006): 610–613. parasitism  Parasitism occurs when individuals thewissen, J. G. M., et al. “Skeletons of terrestrial cetaof one species (the parasite) obtain their living from ceans and the relationship of whales to artiodactyls.” individuals of another species (the host). Parasites Nature 413 (2001): 277–281. have a negative impact on the host, either by conthomas, D. J., et al. “Warming the fuel for the fire: evisuming directly from it, by consuming some of its dence for the thermal dissociation of methane hydrate food (as when intestinal worms harm the host’s during the Paleocene-eocene thermal maximum.” nutrition), by producing toxic waste products (as Geology 30 (2002): 1,067–1,070. do many bacterial and viral parasites such as cholZachos, J. c., and l. R. Kump. “carbon cycle feedbacks era and bubonic plague), or by causing the host’s and the initiation of antarctic glaciation in the earliest own immune system to have harmful effects on the Oligocene.” Global and Planetary Change 47 (2005): host. it is sometimes difficult to distinguish para51–66. sitism from other kinds of ecological interactions. ———, et al. “Rapid acidification of the ocean during the For example, aphids insert their mouthparts into Paleocene-eocene thermal Maximum.” Science 308 the pressurized sugar sap of plant phloem; are they (2005): 1,611–1,615. parasites or herbivores? an organism that entirely ———, et al. “an early cenozoic perspective on greenconsumes another is a predator. an organism that house warming and carbon-cycle dynamics.” Nature makes its living off a host without harming the host 451 (2008): 279–283. is a commensal. the distinctions among parasite,

xviii+598_Biodiversity_F.indd 401

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402 parasitism  402 predator, and commensal are sometimes unclear. A predator may not consume the entire body of its prey, and a parasite can kill its host. A commensal that takes just a little too much from its host may shift into becoming a parasite. The evolution of parasites has been strongly influenced by the hosts. For example, the life cycles of fleas that live on rabbits are coordinated with hormone levels in the rabbits’ blood, which ensures that the young fleas hatch at the same time as the baby rabbits are born. The evolution of the hosts has been influenced by parasites; the very existence of immune systems may be considered proof of this. Because parasite and host species influence one another’s evolution, parasitism is an example of coevolution. It is also, along with commensalism and mutualism, an example of symbiosis in which two species do not merely influence one another’s evolution but are intimately connected with one another. In parasitism, the parasite harms the host; in commensalism, the commensal has no effect on the host; in mutualism, the two mutualists benefit one another. Parasitism has contributed to biodiversity in at least three ways. First, many thousands of species are parasites. Some entire animal phyla (Myxozoa, Orthonectida, Nematomorpha, and Acanthocephala) consist of parasites. Second, parasitism—either parasites finding new hosts, or hosts finding new ways to avoid parasites—has often been the stimulus for speciation. Adaptations of parasites and hosts are among the most complex in the natural world. Third, parasitism may be the principal force behind some kinds of sexual selection. According to many evolutionary scientists, colorful feathers on male birds may be fitness indicators that demonstrate to the female that they are free of parasites. Sexual selection, in turn, leads to even more speciation. Parasites make their living off hosts in numerous ways. Many parasites live inside of their hosts. Nearly all infectious diseases of plants, animals, and humans are examples of this, as in the following examples: ●●

●●

Most bacteria are harmless to multicellular organisms, although the list of bacterial diseases in animals is long and depressing, such as bubonic plague and cholera. Perhaps because plant tissues are mildly acidic, something that most bacteria cannot tolerate, bacteria cause relatively few plant diseases. Most fungi are harmless to multicellular organisms as well, although many of them

xviii+598_Biodiversity_F.indd 402

first entry

●● ●●

●●

●●

cause plant diseases, such as smuts and rusts. Relatively few fungi cause animal diseases, and these usually occur only in weak animals. Many protists also cause diseases, such as malaria in animals and late blight in potatoes. Viruses do not have their own molecular machinery for replication, and must infect many kinds of multicellular organisms. Animal examples include influenza and AIDS. Viruses called bacteriophages even infect bacteria, replicating inside of them and eventually causing them to burst open, releasing hundreds of new viruses. Parasitic worms such as tapeworms live in various parts of animal bodies. Many live in the digestive system, where they have undergone evolutionary simplification. They attach to the host gut lining and absorb the food that the host digests. Others get into organs such as eyes, causing blindness. Worms that live in the lymph system may block the passages and cause swelling. An example is elephantiasis, which causes extensive swelling of the legs and scrotum (see figure). Some parasitic worms even live in brain tissue. A few kinds of flowering plants live entirely inside the tissues of other flowering plants. Plants in the genus Rafflesia have no leaves

Elephantiasis is caused by a parasitic worm that stimulates the human immune system to produce massive swelling.  (Centers for Disease Control and Prevention; Public Health Image Library)

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parasitism  403 own sugar, but obtain water and minerals from the xylem of their host trees. Many herbaceous plants attach to the roots of other plants, often grasses, and obtain water and minerals from them. Examples include Asian sandalwood tree (genus Santalum) and its North American herbaceous relative, the bastard toadflax (Comandra). Many members of the toadflax family, such as Indian paintbrushes (Castilleja) and witchweed (Striga), are root parasites. Witchweed parasitizes large grasses, including maize, and can completely kill cornfields in Africa.

This spherical gall on a post oak leaf was produced by an insect larva. The larva produced a waste product that functioned as a plant growth hormone; the oak leaf produced the spherical structure, which protected and fed the grub. The main defense that oak trees have against gall-producing insects is to shed the infected leaves.  (Stanley A. Rice)

●●

or roots and live entirely within grape vines of the genus Tetrastigma. Their presence can be seen only when the large flowers emerge from the host vine. Some insects lay their eggs in plant tissue. When the larval insect hatches, it releases a chemical that induces the plant to produce a gall that both feeds and protects the larval insect (see photograph above).

Some parasites live on the outside of their hosts. Examples include the following: ●●

●●

●●

Ticks, fleas, and lice are arthropods that drink blood from the skin of vertebrates. They have structures that allow them to attach very firmly to the host, and their bodies are flattened, which makes it difficult for the host to scratch them away. Some plants are partly or entirely parasitic upon other plants. Examples include the dodder (genus Cuscuta), Indian pipe (Monotropa), and some orchids (Corallorhiza). They have no chlorophyll and obtain water, minerals, and sugar from the xylem and phloem of their host plants. Some plants are partly parasitic upon other plants. Examples include mistletoe species, which have chlorophyll and make their

xviii+598_Biodiversity_F.indd 403

Some parasites only occasionally visit their hosts, usually to obtain blood from mammals. Examples include mosquitoes and vampire bats. Surprisingly, blood (which transports but does not store nutrients) is not a very nutritious food source. Female mosquitoes use vertebrate blood to promote egg development. Vampire bats must drink blood daily; successful bats share blood with unsuccessful ones. There are even some finches on the Galapagos Islands that peck the feet of other birds to obtain blood. Hosts have numerous ways of responding to parasites. Some hosts tolerate them by continuing to function despite a parasite load. Others resist the parasites by means such as an immune system, in which white blood cells attack microbes. In many cases, hosts use a combination of tolerance and resistance. Genomic studies have shown that mouse adaptations conferring tolerance are different from those conferring resistance; mice that are more tolerant are less resistant, and vice versa. Parasites usually have very effective methods of dispersing to new hosts. This includes extremely high reproductive rates. Intestinal parasite bacteria or eggs can fill polluted waters. A single witchweed plant can produce 50,000 seeds. But parasites often have other ways of enhancing their dispersal. Many contagious diseases spread because the parasites cause the host to cough, thus projecting droplets of saliva that contain millions of bacteria or viruses. Often the disease is most contagious prior to the stage when symptoms become obvious, and the host continues to mingle with other members of its species. Parasites can even change the bodies and behavior of their hosts. Some parasitic worms cause mollusks, normally reclusive, to climb out on the tips of leaves where birds will see and eat them, while others cause ant abdomens to swell and become red, resembling berries, which birds eat (see photograph on page 404). The virus that causes rabies

11/17/11 1:13 PM

404 parasitism  404 causes the ­vertebrate host to become very aggressive, spreading the virus by its bites. In many cases, animal vectors spread the parasite. Usually the vectors are themselves parasites. Examples include mosquitoes. Viral and protist parasites live in mosquito salivary glands and spread to new hosts when the mosquitoes bite them. Fleas and ticks are also disease vectors. Sometimes more than one vector species is involved in spreading a disease. For example, the mosquito Culex tarsalis spreads West Nile viruses in bird populations, while C. pipiens spreads the virus to humans. In California, the deer tick Ixodes spinipalpis spreads the Lyme disease bacterium Borrelia burgdorferi among rodents, but I. pacificus spreads the bacteria to humans. Epidemiologists are focusing much of their attention upon stopping the spread of diseases by interfering with the activity of the vector. The bacterium Wolbachia kills Aedes aegypti mosquitoes, which spread malaria, but does not do so right away. But since it is usually the older mosquitoes that spread most of the malaria, infecting mosquito populations with Wolbachia may reduce the amount of malaria that they spread. Many multicellular parasites have complex life cycles, some examples of which are provided in the entry about animals. They change form as they travel from one host to another and sometimes a third. Parasites may also have adaptations that allow them to escape from the host species’

first entry behavioral protection. Some arthropods live in ant nests. Some, such as the caterpillars of Maculinea butterflies, have skin surface chemicals that entice the ants to take care of them. Some spiders, which have eight legs and no antennae, imitate the behavior of ants, which have six legs and antennae, by walking along with their front legs held up like antennae. Parasites can adapt to new host species or populations, often in conjunction with a genetic mutation that alters their host preference or effects. Several human diseases (known as zoonotic diseases) have come from livestock. One of the worst human diseases in history, smallpox (which has been eradicated from human populations by vaccination), apparently evolved from cowpox. A few diseases have transferred the other way; apparently cattle caught tuberculosis from humans. The bacterium Treponema pallidum causes both syphilis and yaws. Researchers found a variant form of yaws (T. p. pertenue) in a remote South American tribe that had characteristics similar to syphilis (T. p. pallidum). Apparently, Europeans carried the variant form of yaws to Europe, where it evolved into syphilis. Some birds, most notably cowbirds and cuckoos, are nest parasites: They lay their eggs in the nests of other bird species (see photograph on page 405). The parent birds of the host species feed the parasitic nestlings as if they were their own. The host birds do not recognize that the parasitic nestling is not their own, even when it is much larger and a different color than their own offspring and the parasite pushes the host offspring out of the nest.

Parasitism and Commensalism

A parasite has caused this Cephalotes aratus ant to have a bright red abdomen. Birds, mistaking the ant for a berry, will consume the ants and ingest the parasite. The parasite develops into a new form and lives inside the bird. Parasite eggs in bird droppings are ingested by foraging ants.  (Steve Yanoviak; University of Arkansas)

xviii+598_Biodiversity_F.indd 404

Commensal populations living on hosts often help to protect the host from parasites. Most of the trillions of bacteria on or in the host body are commensals, and their populations often crowd out the populations of parasites. Commensalistic bacteria in chicken intestines usually crowd out deadly Salmonella bacteria, and chicks obtain these commensalistic bacteria from their mothers. Chickens raised in vast industrial populations, however, usually do not have an opportunity to inherit commensalistic bacteria from the mothers who laid the eggs. Parasites also spread more readily through dense populations of hosts. Huge “factory” populations of chickens therefore suffer from Salmonella infections more than do “free-range” chickens that grow up in smaller populations with their mothers. The distinction between parasitism and commensalism is a shifting border. Normally commensalistic microbes can become parasitic under certain

11/17/11 1:13 PM

parasitism  405 conditions. Probably all commensalistic microbes are prevented from becoming parasites by the host immune system, as in these examples: ●●

●●

●●

The human mouth, throat, and bronchial passages are filled with millions of bacteria and also some protists. The only harm they normally cause is to produce acid under anaerobic conditions, leading to tooth decay, which can be prevented by proper hygiene. These bacteria do not normally infect the lungs because the host immune system prevents them from doing so. When the host immune system is weakened after a long bout of influenza or during infection with HIV, they can become parasitic and cause potentially deadly pneumonia. The human skin is covered with millions of bacteria, including staph. These bacteria are harmless if they remain on the outside of the skin, where they consume dead cells and oils. Their worst effect is to produce body odor, once again controllable by hygiene. If they get inside the skin, when the skin is cut, they can cause serious and potentially deadly skin infections. The human intestine is filled with trillions of harmless (or in some cases beneficial) bacteria. If these bacteria get into the lining of the intestine, they can cause an infection. Infection of the appendix causes appendicitis, which can cause the appendix to burst and spread deadly bacteria throughout the body cavity. Gunshot and stab wounds can release bacteria from the intestines into the blood, causing blood poisoning, or into tissues, causing gas gangrene.

The border between parasitism and commensalism is also an evolutionary one. Natural selection often favors the parasites that have the least effect upon the host as well as the hosts that are most resistant to the parasites. That is, natural selection often leads to milder bacteria and stronger hosts, a process known as balanced pathogenicity. This process occurs mostly with parasites that spread by direct contact from one host to another, because the parasites that spread most effectively are those that allow their hosts to mingle with the rest of the population. People tend to stay away from others who display severe disease symptoms. Microbes that spread by insect vectors or sewage, however, do not evolve to become milder. This is because relatively deadly and relatively mild microbes spread equally well in these cases. Humans cannot stay away from water or mosquitoes that carry virulent

xviii+598_Biodiversity_F.indd 405

A common cuckoo laid an egg in the nest of a great reed warbler, Acrocephalus arundinaceus. The cuckoo egg hatched before those of the warbler, and the cuckoo nestling pushed warbler eggs out of the nest.  (Image from Anderson et al., PLoS ONE)

microbes any better than they can from those that carry mild microbes.

Parasitism and Environment Several human practices increase the parasite load of natural populations. Parasitic diseases often spread through fish raised on fish farms, and when these fish escape into the wild they carry the parasites with them. It is also very likely that the greenhouse effect will cause parasitic diseases to spread, a fact that has caught the attention of many public health experts. Some diseases such as dengue fever are tropical mainly because the mosquitoes that serve as their vectors live only in tropical climatic zones. As temperatures increase, so will the tropical zones, allowing the mosquitoes (and the parasites) to spread to locations previously free of them. Cholera bacteria persist in resting stages when they are not actively moving through human populations but can become active again under warmer conditions. Global warming might, in this way, encourage the spread of cholera. Newly introduced parasites are less likely to spread through intact ecosystems. Apparently biodiversity itself is an important component of ecosystems that helps to prevent the spread of diseases. See also animals; coevolution; commensalism; greenhouse effect; mutualism; sexual selection.

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406 parasitism  406 Further Reading Anatolin, Michael F. “Unpacking β: Within-host dynamics and the evolutionary ecology of pathogen transmission.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 415–437. Anderson, Michael G., et al. “Egg eviction imposes a recoverable cost of virulence in chicks of a brood parasite.” PLoS ONE 4 (2009): e7725. Andersson, Anders F., and Jillian F. Banfield. “Virus population dynamics and acquired virus resistance in natural microbial communities.” Science 320 (2008): 1,047–1,050. Blanford, Simon, et al. “Fungal pathogen reduces potential for malaria transmission.” Science 308 (2005): 1,638–1,641. Burdon, Jeremy J., and Peter H. Thrall. “Coevolution of plants and their pathogens in natural habitats.” Science 324 (2009): 755–756. Cantor, Norman F. In the Wake of the Plague: The Black Death and the World it Made. New York: Free Press, 2001. Carrell, Jennifer Lee. The Speckled Monster: A Historical Tale of Battling Smallpox. New York: Penguin, 2003. Chambouvet, Aurelie, et al. “Control of toxic marine dinoflagellate blooms by serial parasitic killers.” Science 322 (2008): 1,254–1,257. Crawford, Dorothy H. Deadly Companions: How Microbes Shaped Our History. Oxford, U.K.: Oxford University Press, 2007. Davies, Nicholas B., and Justin A. Welbergen. “Social transmission of a host defense against cuckoo parasitism.” Science 324 (2009): 1,318–1,320. Desowitz, Robert S. The Malaria Capers: More Tales of Parasites and People, Research and Reality. New York: Norton, 1991. Duplaix, Nicole. “Fleas: Lethal leapers.” National Geographic, May 1988, 67–94. Fenner, Frank, et al. Smallpox and Its Eradication. Geneva, Switzerland: World Health Organization, 1988. Finlay, B. Brett. “The art of bacterial warfare.” Scientific American, February 2010, 56–63. Fisher, Jeffrey A. The Plague Makers: How We Are Creating Catastrophic New Epidemics—and What We Must Do to Avert Them. New York: Simon & Schuster, 1994. Fox, Maggie. “Parasite makes ants into ‘berries’ to entice birds.” Reuters, January 16, 2008. Available online. URL: http://uk.reuters.com/article/2008/01/16/uk-antberry-idUKN1662901820080116. Accessed August 8, 2011. Garrett, Laurie. The Coming Plague: Newly Emerging Diseases in a World Out of Balance. New York: Farrar, Straus and Giroux, 1994. Hayes, K. S., et al. “Exploitation of the intestinal microflora by the parasitic nematode Trichuris muris.” Science 328 (2010): 1,391–1,394.

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first entry Henig, Robin Marantz. A Dancing Matrix: Voyages along the Viral Frontier. New York: Knopf, 1993. Kambris, Zakaria, et al. “Immune activation by life-shortening Wolbachia and reduced filarial competence in mosquitoes.” Science 326 (2009): 134–136. Krkošek, Martin, et al. “Epizootics of wild fish induced by farm fish.” Proceedings of the National Academy of Sciences USA 103 (2006): 15,506–15,510. Leroy, E. M., et al. “Fruit bats as reservoirs of Ebola virus.” Nature 438 (2005): 575–576. Li, Jianxiong, and Michael P. Timko. “Gene-for-gene resistance in Striga-cowpea associations.” Science 325 (2009): 1,094. Li, W. D., et al. “Bats are natural reservoirs of SARS-like coronaviruses.” Science 310 (2005): 676–679. Lyon, Bruce E., and John McA. Eadie. “Conspecific brood parasitism in birds: A life-history perspective.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 343–363. Marriott, Edward. Plague: A Story of Science, Rivalry, and the Scourge that Won’t Go Away. New York: Henry Holt, 2002. Matossian, Mary Kilbourne. Poisons of the Past: Molds, Epidemics, and History. New Haven, Conn.: Yale University Press, 1989. May, Robert M. “Population biology of infectious diseases.” Nature 280 (1979): 361–367. McCormick, Joseph B., and Susan Fisher-Hoch. Level 4: Virus Hunters of the CDC. Atlanta: Turner, 1996. McMeniman, Conor J., et al. “Stable introduction of a life-shortening Wolbachia infection into the mosquito Aedes aegypti.” Science 323 (2009): 141–144. Summarized by Read, Andrew F., and Matthew R. Thomas. “Mosquitoes cut short.” Science 323 (2009): 5–52. Nash, David R., et al. “A mosaic of chemical coevolution in a large blue butterfly.” Science 319 (2008): 88–90. Parker, Ingrid M., and Gregory S. Gilbert. “The evolutionary ecology of novel plant-pathogen interactions.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 675–700. Preston, Richard. The Demon in the Freezer. New York: Random House, 2002. Råberg, Lars, Derek Sim, and Andrew F. Read. “Disentangling genetic variation for resistance and tolerance to infectious diseases in animals.” Science 318 (2007): 812–814. Rabsch, W., et al. “Competitive exclusion of Salmonella enteritidis by Salmonella gallinarum in poultry.” Emerging Infectious Diseases 6 (2000): 443–448. Scholte, Ernst-Jan, et al. “An entomopathogenic fungus for control of adult African malarial mosquitoes.” Science 308 (2005): 1,641–1,642. Schutt, Bill. Dark Banquet: Blood and the Curious Lives of Blood-Feeding Creatures. New York: Harmony, 2009. Tucker, Jonathan B. Scourge: The Once and Future Threat of Smallpox. New York: Atlantic Monthly Press, 2001.

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Permian extinction  407 Worobey, Michael, et al. “Point, counterpoint: The evolution of pathogenic viruses and their human hosts.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 515–540. Zimmer, Carl. “Isolated tribe gives clues to the origin of syphilis.” Science 319 (2008): 272.

Permian extinction  The Permian extinction was the biggest mass extinction event in the history of life and as such the greatest challenge to Earth’s biodiversity. It has been known since the work of geologist John Phillips in the 1840s that the end of the Permian period was marked by a major turnover in marine animal species; only recently, however, have the magnitude and the causes of this turnover become apparent. The Permian extinction occurred 252 million years ago and marked the end of the Permian period and the Paleozoic era. Paleontologist Douglas Erwin called it the “mother of all extinctions.” Approximately 90 percent of species died during and immediately after this event in the early Triassic period. In contrast, the Cretaceous extinction, which exterminated the dinosaurs and many other species, killed only about 50 percent of the species on Earth. Life on Earth recovered from the Permian extinction, but it took between 50 and 100 million years to regain its former diversity. Though the major groups of organisms that had dominated the Earth during the Permian (such as seed plants, mollusks, fishes, amphibians, and reptiles) survived, most of the species did not. The Triassic period began with a vastly impoverished set of species, and the later Triassic had an almost entirely new set of species within these groups. In fact, in some of the earliest Triassic deposits, a single species constitutes 90 percent of the vertebrates: a pig-sized, mammal-like reptile, Lystrosaurus. In the earliest Triassic marine deposits, only a brachiopod called Lingula remained abundant. The Permian extinction was the only mass extinction to have significantly affected insects. About half of insect families became extinct. The Paleozoic assemblage of insects went into decline, and modern groups of insects began to predominate in the Mesozoic era. The Permian extinction has left a permanent mark on biodiversity today. Geological deposits that span the boundary between the Permian and Triassic periods are found in China, the Karoo Basin of South Africa, and in Russia. The interpretation of the information from these deposits needed to await the refinement of radiometric dating methods. There was worldwide evidence of a massive turnover in species makeup, but only by precise radiometric dating could scientists be sure that this turnover had happened at the

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same time all over the world at or immediately after the Permo-Triassic boundary. It also awaited geopolitical developments that allowed scientific teams from Russia and America, and China and America, to work together on detailed studies. Consider the geological evidence of what happened at the end of the Permian, as indicated in the following paragraphs: Anoxic deposits. One geological indicator is the dark-colored deposits at the Permo-Triassic boundary. The dark color is an indicator of the lack of oxygen gas (O2) at the time and place the sediments were deposited: The iron is dark green instead of bright red, and undecomposed organic matter darkens it further to black. Such deposits occur today at the bottoms of many ponds and swamps. Some of the deposits at the PermoTriassic boundary contain pyrites, an iron-sulfur mineral that forms only in the absence of oxygen. The worldwide black slime layer suggests worldwide anoxia, a radical event in Earth’s history. Today, oxygen levels in the atmosphere remain very steady at about 21 percent. Some estimates put the atmospheric oxygen content as high as 35 percent during the Carboniferous. Toward the end of the Permian period, however, the oxygen content may have dropped as low as 15 percent. According to geologists Raymond Huey and Peter Ward, this would have restricted vertebrates to very limited habitats at low elevation, where air pressure was highest. Almost half of the land area of the Earth would have been, they claim, uninhabitable by large animals. The black “death bed” layer at the end of the Permian represents between 10,000 and 60,000 years of time. Moreover, the Permo-Triassic boundary is also characterized by a “chert gap.” Chert is a rock formed from the ooze of billions of microscopic shelled animals accumulating on the ocean floor. The ooze from which chert forms is found somewhere in the deposits of almost every geological age—except at the PermoTriassic boundary. Coarse sediments. Another geological indicator is the deposit, during the very early Triassic, of coarse sediments that were washed down violent rivers; this sometimes includes very large boulders that were moved several hundred miles or kilometers from their point of origin. The structure of river channels also suggests that rapid erosion was taking place, more rapid than practically anyplace on the Earth now, and it was occurring everywhere. This would indicate a worldwide reduction of forest cover. Evidence from isotopes. Another geological indicator is the worldwide shift in oxygen and carbon isotope ratios. The ratio of oxygen isotopes acts

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408 Permian extinction  408 as a permanent record of temperature. The seemingly worldwide decrease in oxygen isotope ratio suggests a massive global warming, averaging 9°F (16°C). There was also a global shift in carbon isotope ratios. Plant photosynthesis prefers one carbon isotope over another as it removes carbon dioxide from the air to make sugar; thus organic matter has a different carbon isotope ratio from inorganic carbon-containing molecules. The worldwide decrease in carbon isotope ratios at the Permian boundary suggests a worldwide decrease in plant growth. Death of terrestrial forests. During the Permian, there had been fossils of plant parts from the ferns and conifers that were the dominant plants at that time. Fossil pollen was most abundant, since pollen is produced in large quantities and spreads far from the source plant and has a coat that resists decay. But at the Permo-Triassic boundary, fungus spores are very abundant. This may mean that the world was rotting. Something had killed most of the plants, and mold was growing all over them. During the early Triassic recovery period, plant pollen reappeared, but it was mostly pollen from small plants such as club mosses that could grow in recently ravaged landscapes. Usually, in every geological period (until recently), coal was forming from vast swamps of plants somewhere in the world. The sediments of the first 20 million years of the Triassic, however, stood out for the absence of coal deposits. The “spike” of fungus spores and the “coal gap” are biotic indicators of a severe devastation of forest growth. Reappearance of stromatolites. Stromatolites reappeared in the fossil record immediately after the Permo-Triassic boundary. Stromatolites are layers of cyanobacteria and were common in Precambrian time but became scarce after the evolution of aquatic grazing animals. Today stromatolites are found only in shallow seas where the water is too salty for most of the animals that would otherwise eat them. The reappearance of stromatolites at the end of the Permian suggests that many aquatic grazing animals had died. The Permo-Triassic deposits in China were formed under shallow marine (continental shelf) conditions. They contain a record of what happened to marine organisms. Most species of marine organisms that are preserved as fossils are microscopic plankton with calcium or other hard shells. Their shells preserve well, and the organisms themselves were already living in or near the sediments. When scientists reconstructed the durations of more than 300 marine animal species from the Chinese rocks, they found that 94 percent of them vanished from the record soon before, at, or soon after the boundary. Furthermore, the deposits right before the bound-

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first entry ary show evidence of extensive burrowing by a large number of marine worms; no such evidence occurs at or immediately after the boundary. Therefore, toward the end of the Permian and at the beginning of the Triassic, there was a collapse in marine life. Scientists who studied the Chinese deposits have pointed out that many species may appear to have vanished before the end of the Permian, simply because, by chance, their fossils were not preserved during the last few thousand years of their existence; and that many species may appear to have vanished after the end of the Permian, simply because, by chance, their fossils were washed upward from the shallow ocean floor and got mixed in with later Triassic deposits. These arguments would suggest that the Permian extinction was a relatively sudden event, rather than spread out over a long period. Regardless of how sudden the event was, it had a drastic effect on marine animal life. A Permian seafloor community full of coral reefs, plankton, and many invertebrate animals, including the last of the fading dynasty of trilobites, was replaced by an early Triassic seafloor community consisting of very few species. For example, whole early Triassic rocks are formed from small shells of just a few species of mollusks that lived right after the disaster. One of the types of animals that survived was the Lingula brachiopod shell mentioned earlier. Its survival tells a story. It has survived 500 million years and survives today because it burrows deep in the mud, and can survive long periods with severely restricted food and oxygen. Among the swimming animals, many species of bony fishes and sharks also died, to be replaced by other, smaller fish species. Both among the mollusks and the fishes, the survivors were smaller than those that had dominated the Permian seas. In short, according to paleontologist Michael Benton, the survivors appeared to be those that, partly because they were small, may have needed less oxygen. Paleontologist Douglas Erwin disputes the correlation between ability to tolerate anoxia and success at surviving the Permian extinction. Meanwhile, what was happening on land? The Karoo Basin deposits in South Africa formed from shallow lake sediments that washed northward from a mountain range, now worn away, in what is now Antarctica. The vertebrate fossils in the latePermian Karoo deposits include two amphibian and 72 reptile species. These diverse reptiles included some that ate plants, some that ate insects, some that ate one another; some large, some small; all part of a complex community of interacting reptile species. However, the early Triassic deposits have only 28 terrestrial vertebrate species. Since most of them are not the same species that existed in the late

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Permian extinction  409 Permian, this represents a drastic turnover of species composition. And rather than a diverse community of interacting species, many of the vertebrate skeletons from the early Triassic are of one kind of reptile mentioned earlier: Lystrosaurus, whose generalist eat-anything niche has led some scientists to call it the pig of the ancient reptile world. The Karoo animal world soon after the Permian extinction was crawling with Lystrosaurus and had a few other rare reptiles. This pattern is seen in deposits not only from South Africa, but also from South America, Antarctica, India, China, and Russia. A complex Permian community of interacting species that specialized on their means of living was replaced by a worldwide Triassic landscape dominated by one kind of animal that did a little bit of everything. Overall, 27 of 29 reptile families and six of nine amphibian families became extinct. There was a similar turnover in plant species: 140 plant species, in 11 families, from the Permian were replaced by fewer than 50 species, in only three families, during the Triassic. Therefore, at the end of the Permian, something killed most of the plants; partly as a result, the atmosphere nearly ran out of oxygen, and the landscape eroded severely. What could have caused such a severe event? Several causes have been suggested: Loss of continental shelf area. One early suggestion, from the 1950s, was that smaller continents collided together to form the world supercontinent of Pangaea. Since many species of organisms known from the fossil record lived in shallow water, the collision of several continents into one would have drastically reduced the amount of coastline environment in which they lived. A massive continent, furthermore, would have had more severe terrestrial climates. Oceans ameliorate temperature extremes, which is why the summers are hotter and winters are colder in Minneapolis than in Seattle. The interior of Pangaea, then, would have had extreme climatic conditions that would have caused at least some extinctions. Finally, species that had evolved separately might have been thrown together into a cosmopolitan mix, in which a few “winners” would outcompete “losers” that had formerly been dominant in their own separate lands. While it is beyond dispute that Pangaea formed during Permian times, many scientists have concluded that the resulting changes in terrestrial climate and marine habitat would not have been great enough to cause the Permian extinction. It certainly would not account for the worldwide loss of oxygen and massive death of vegetation. Asteroid impact. Could the Permian extinction have been caused by an asteroid, as was the case with the Cretaceous extinction? Scientists are much

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less likely to discover evidence of such an impact in deposits 250 million years old than in deposits 65 million years old, which is the time at which an asteroid almost certainly hit the Earth, causing the Cretaceous extinction. However unlikely it might seem, evidence of what may have been a large asteroid impact was recently found: the Bedout Crater off the coast of Australia. The date of this crater corresponds closely to the time of the Permian extinction. Most scientists are not, however, convinced that Bedout is an impact crater. Volcanic eruptions. A massive set of volcanic eruptions known as the Siberian Traps occurred at the Permo-Triassic boundary. (Traps comes from the Swedish for staircase or steps, referring to the successive layers of lava flow.) These eruptions continued for a few million years. They cover an area of Siberia larger than the entire European Community: 77,200 square miles (20,000 square km). The gases ejected from these eruptions could have caused worldwide devastation. Sulfur dioxide (SO2) reacts with water to produce sulfuric acid, a component today of acid rain. Severe acid rain may have killed much of the vegetation on land and photosynthetic organisms in the oceans, causing the collapse of food chains in both. Other large volcanic eruptions during Earth’s history were not associated with mass extinctions, but the Siberian Traps eruptions may have had a worldwide impact because they ejected more sulfur than other volcanic eruptions. The lava from these eruptions is rich in sulfur minerals, suggesting that these eruptions would have ejected even more sulfur dioxide than most volcanic eruptions observed today. Volcanoes also eject large amounts of carbon dioxide (CO2), a greenhouse gas that leads to global warming. The resulting death of plants could have contributed to the worldwide plunge in oxygen levels and increase in CO2 . Some scientists even suggest that there was enough CO2 in the water to poison aquatic animals directly. Release of methane. Paleontologist Michael Benton suggests, though without direct evidence, that the moderate global warming caused by the volcanoes caused yet another set of catastrophes to occur: gigantic global burps. Deep underneath continental shelf sediments, especially in polar regions, there are today (and may have been during the Permian) very large deposits of methane hydrate, which is an icelike combination of water and natural gas. Pressure and cold temperature keep the methane in a solid state, but if the ocean waters became warm, the methane might have evaporated explosively, bubbling quickly through the ocean and into the atmosphere. There is evidence that such methane releases have occurred in the geologically recent past: A Paleocene eruption 55 million years ago apparently caused a global

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410 Permian extinction  410 warming of about 3–4°F (5–7°C) over a 10,000-year period. Methane, though short-lived in the atmosphere, is a strong greenhouse gas. By enhancing the global warming that was already going on, these methane eruptions could have started a positive-feedback loop in which more global warming caused the release of even more methane. Methane reacts with oxygen, and this would have worsened the already dire problem of anoxia. When methane reacts with oxygen, it produces carbon dioxide, which is also a greenhouse gas. The Permian extinction had some permanent effects on the history of life. During the Permian, brachiopod shells were relatively common and mollusk shells were relatively rare. However, a few million years after the extinction event, bivalve mollusk shells evolved into an explosive radiation of new species, while the brachiopods remained, and remain, rare. This occurred not because, under normal seafloor conditions, mollusks were superior to brachiopods, but because mollusks either got lucky or because most of them were better adapted to the postdisaster world of the earliest Triassic. The implications of the Permian extinction for the future of life on Earth are both good and bad. Many biologists believe that human activity is causing a sixth mass extinction. Humans are causing species to become extinct at a rate as great as what occurred in previous mass extinctions. The bad news is that (1) continued destruction of vegetation can, in fact, lead to massive soil erosion and, if this destruction continues yet further, can even contribute to a depletion of oxygen from the atmosphere. At the end of the Permian, fossil evidence of plants (e.g., pollen) nearly vanished and so did oxygen. There is no need to speculate that life on Earth is strongly dependent on the work of plants: The “experiment” has in fact been done. The bad news is also that (2) events in the history of the Earth—as, in this case, normal volcanic activities—can have a severe impact on life. It does not take an asteroid to kill almost everything off. The good news is that the Earth can recover from an almost total extinction event. No matter what humans do to the Earth—and probably no matter what happens to it from other causes except for the final explosion of the Sun several billion years from now—the Earth will recover. But this good news is also bad. It would take, from the viewpoint of human history, forever for the Earth to recover. The human economy is dependent upon the continued stability and smooth operation of natural systems. For humans, even a slight change in global temperature would spell agricultural and economic disaster. Because civilization depends upon the exploitation of natural resources, even the slightest interruption of these resources would send humankind, very

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first entry few of whom know how to survive in the wild, into a desperate tailspin. Humans would probably not have survived the Permian extinction. See also greenhouse effect; mass extinctions; Paleogene period, biodiversity in; Permian period, biodiversity in. Further Reading Becker, Luann, et al. “Bedout: A possible end-Permian impact crater offshore of northwestern Australia.” Science 304 (2004): 1,469–1,476. Benton, Michael J. When Life Nearly Died: The Greatest Mass Extinction of All Time. London: Thames and Hudson, 2003. ———, and R. J. Twitchett. “How to kill (almost) all life: The end-Permian extinction event.” Trends in Ecology and Evolution 18 (2003): 358–365. Brayard, Arnaud, et al. “Good genes and good luck: Ammonoid diversity and the end-Permian mass extinction.” Science 325 (2009): 1,118–1,121. Erwin, Douglas H. Extinction: How Life on Earth Nearly Ended 250 Million Years Ago. Princeton, N.J.: Princeton University Press, 2006. Huey, Raymond B., and Peter D. Ward. “Hypoxia, global warming, and terrestrial late Permian extinctions.” Science 308 (2005): 398–401. Knoll, Andrew H., et al. “Comparative Earth history and late Permian mass extinction.” Science 273 (1996): 452–456. Looy, C. V., et al. “Life in the end-Permian dead zone.” Proceedings of the National Academy of Sciences USA 162 (2005): 653–659. Payne, J. L., et al. “Large perturbations of the carbon cycle during recovery from the end-Permian extinction.” Science 305 (2004): 506. Retallack, Gregory J., et al. “Vertebrate extinction across Permian-Triassic boundary in Karoo Basin, South Africa.” Bulletin of the Geological Society of America 115 (2003): 1,133–1,152. ———, et al. “Search for evidence of impact at the Permian-Triassic boundary in Antarctica and Australia.” Geology 26 (1998): 979–982. Visscher, H., et al. “The terminal Paleozoic fungal event: Evidence of terrestrial ecosystem destabilization and collapse.” Proceedings of the National Academy of Sciences 93 (1996): 2,155–2,158. Ward, Peter D. Under a Green Sky: Global Warming, the Mass Extinctions of the Past, and What They Can Tell Us about the Future. New York: HarperCollins, 2008. ———. “Impact from the deep.” Scientific American, October 2006, 64–71. ———, et al. “Altered river morphology in South Africa related to the Permian-Triassic extinction.” Science 289 (2000): 1,740–1,743. ———, et al. “Abrupt and gradual extinction among late Permian land vertebrates in the Karoo Basin, South Africa.” Science 307 (2005): 709–714.

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Permian period, biodiversity in  411 White, R. V. “Earth’s biggest ‘whodunnit’: Unravelling the clues in the case of the end-Permian mass extinction.” Philosophical Transactions of the Royal Society of London 360 (2002): 2,963–2,985.

Permian period, biodiversity in  The Permian period (290 to 250 million years ago) was the sixth and final period of the Paleozoic era. It followed the Carboniferous period. At the beginning of the Paleozoic era, almost all life was aquatic; by the end of the Paleozoic era, forests filled with vertebrates and insects covered large areas of dry land. It ended with the Permian extinction, the most important of the mass extinctions in the history of the Earth. Climate. The climate of the Permian was cooler and drier than that of earlier periods of the Paleozoic, especially in the center of the massive continent of Pangaea. Today, deserts with extreme temperatures are found in the middle of the Eurasian continent and were probably found in the middle of Pangaea as well. Glaciation occurred in the southern portions of Pangaea. Then global warming, caused initially by volcanic eruptions, occurred near the end of the Permian Period, which contributed to massive extinctions (see table). In connection with the Permian extinction, atmospheric oxygen levels became low enough that, according to some investigators, large terrestrial animals had difficulty breathing. Continents. All of the continents collided to form one massive continent called Pangaea. Marine life. Diversity of marine animal species remained as high as it had been during the Carboniferous period, but declined rapidly with the onset of the Permian extinction. The groups of organisms that recuperated from the extinction more rapidly became the dominant groups up through the present time. The Permian extinction therefore largely determined the pattern of biodiversity for the entire subsequent history of the Earth. ●●

Invertebrates. Some invertebrates that are now rare, such as stalked echinoderms, shelled cephalopods, and brachiopods, were common in the Permian period, but their diversity was strongly reduced by the extinction event. Bivalves, cephalopods without shells, and echinoderms without stalks became common after the Permian extinction, while brachiopods, shelled cephalopods, and stalked echinoderms did not. The trilobites had gradually declined from being the dominant marine invertebrates from the Cambrian period onward and did not survive the extinction event.

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Multicellular Biodiversity   in the Permian Period Conditions Atmospheric oxygen

15% above modern level before extinction event

Atmospheric carbon dioxide

2.5 times modern level

Global temperature

3°F (2°C) above modern level

Sea level

170 feet (60 m) higher than today before extinction event

Approximate number of families* Continental

200

Marine

450

Total

650

Examples of marine animals Acropyge sp.

trilobite

Caricula salebrosa

brachiopod

Cheirolepis sp.

bony fish

Cyclolobus walkeri

ammonite mollusk

Helicoprion bessonovi

shark

Mamayocaris sp.

crustacean

Myalina lamellosa

bivalve mollusk

Panduralimulus babcocki

horseshoe crab

Platycrinites omanensis

crinoid echinoderm

Vermiforinchus sp.

annelid

Examples of continental animals Apthoroblattina sulcata

cockroach

Archosaurus rossicus

archosaur-like reptile

Dimetrodon grandis

mammal-like reptile

Ectosteorhachis nitidus

lobe-fin fish

Eryops megacephalus

amphibian

Gnathorhiza sp.

lungfish

Permocoleus wellingtonensis

beetle

Permotipula patricia

fly

Zygosaurus lucius

amphibian

Examples of land plants Cassinisia orobica

conifer

Crossozamia sp.

cycad

Emplecopteris triangularis

seed fern

Ginkgo baiera

ginkgo

Glossopteris sp.

seed fern

Majonica alpina

conifer

Titea singularis

tree fern

*Based on Benton.

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412 permian period, biodiversity in 412 ●

Vertebrates. Diversity continued to be high among the fishes. Sharks were abundant and diverse, including Helicoprion, which had a coil of teeth in its lower jaw. Bony fishes continued to diversify.

Continental life. Forests and wetlands covered much of the land surface at the beginning of the Permian period. ●



Plants. the tree-sized horsetails and club mosses that had characterized the “coal swamps” of the carboniferous were close to extinction by the middle of the Permian, replaced by seed ferns (a type of plant now extinct) and by conifers, which fi rst became abundant during the Permian. this probably occurred because the conifers were better adapted to the cooler, drier conditions of the Permian. the seed fern Glossopteris dominated entire forests. Some seed ferns were woody vines. the fi rst cycads evolved during the Permian, as did the ginkgoes, although both groups became much more abundant and diverse during the Mesozoic era. there were no flowering plants. Invertebrates. among the most abundant terrestrial invertebrates were cockroaches. large dragonfl ies remained common, as in the preceding carboniferous period. though they were rare, the fi rst beetles and fl ies evolved during the Permian.

first entry ●

Vertebrates. Freshwater bony fishes, lungfishes, and amphibians continued to evolve. Eryops was a large Permian amphibian. the drier conditions encouraged the diversification and spread of reptiles, which had first appeared in the carboniferous (see figure). there were two major groups of Permian reptiles: the synapsids and the diapsids. there were no dinosaurs, but some of the reptiles of the Permian were rather large. none of these reptiles were of recognizably modern groups; however, the diapsids were the ancestors of most of the modern animals commonly called reptiles, as well as extinct reptiles such as archosaurs and dinosaurs. the diapsids were also the ancestors of birds. the synapsids are today extinct except for one line of descendants: mammals. Some Permian synapsids grew as large as hippos. the most famous Permian synapsid was Dimetrodon, whose ribs formed a huge “sail” along its back. Some synapsids had many mammal-like characteristics; for example, unlike diapsids and modern reptiles, they had several kinds of specialized teeth. they may also have had whiskers: their skulls have small nerve openings where these whiskers would have been. if they had whiskers, they had hair, and therefore were probably warm-blooded. the dissipation of body heat may have been the main function of the sail along the back of Dimetrodon. in other words, although these synapsids were not mammals, they closely resembled them. a nearly complete set of synapsid transitional forms has been found between reptiles and mammals.

Dimetrodon was a large mammal-like reptile that lived during the Permian period. The large sail of skin tissue may have allowed Dimetrodon to absorb heat from sunlight during cold weather and radiate body heat during warm weather.

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Extinctions. the Permian extinction brought many evolutionary lineages to an end and severely reduced the abundance of many others. Scientists will never know what might have happened if evolution could have continued uninterrupted. Would the synapsids have developed into the dominant vertebrates, ushering in the age of mammals 250 rather than 65 million years ago? Would this have prevented the evolution of the dinosaurs? these questions will never be answered. See also Permian extinction.

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Pinchot, Gifford Further Reading Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. ———. “Four feet on the ground.” In The Book of Life: An Illustrated History of the Evolution of Life on Earth, edited by Stephen J. Gould. New York: Norton, 2001. Brayard, Arnaud, et al. “Good genes and good luck: Ammonoid diversity and the end-Permian mass extinction.” Science 325 (2009): 1,118–1,121. Krings, Michael, et al. “How Paleozoic vines and lianas got off the ground: On scrambling and climbing Carboniferous–early Permian pteridosperms.” Botanical Review 69 (2003): 204–224.

Pinchot, Gifford  (1865–1946)  American  Con-

servationist  Gifford Pinchot was born August 11, 1865, into a wealthy Pennsylvania family that had made its fortune from clear-cutting the eastern deciduous forest. It is ironic that he became one of the major figures in forest and biodiversity conservation. It was at the suggestion of his father, who regretted the damage his family had done to the land, that Gifford Pinchot attended Yale University and studied forestry. Gifford Pinchot became chief of the Division of Forestry in the Department of the Interior in 1898. The Pinchot family endowed the Yale School of Forestry in 1900 to train professional forest managers. At that time, the U.S. federal government owned thousands of square miles of western forests that had recently been taken from Native American ownership and was engaged primarily in giving forest lands to private railroad, lumber, and mining corporations at minimal charge. When progressive Republican Theodore Roosevelt became president in 1901, after the assassination of William McKinley, he decided to end the practice of wholesale public support of private corporations. Both Roosevelt and Pinchot extensively toured western forests and were acquaintances of conservationist John Muir. Based on field information, Pinchot and Roosevelt selected thousands of square miles of forestland to set aside in permanent federal ownership. In 1905, Roosevelt established the U.S. Forest Service of the Department of Agriculture to manage these forests by leasing them to private corporations, who could make a profit from the renewable resources in return for paying a fee to the government. Pinchot was its head. Although Pinchot is considered one of the founding figures in American conservation, his approach was quite different from that of preservationists such as John Muir. Unlike Muir, Pinchot was not interested so much in the preservation of natural habitats and wildlands as in the management of federal

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413

lands for sustainable production of timber and other industrial resources. Muir’s view was that conservation was the right thing to do; Pinchot’s view was that it could be profitable in the long term. This was perhaps best illustrated by Pinchot’s support for the damming of Hetch Hetchy Valley near Yosemite in the Sierra Nevada of California, creating a reservoir for San Francisco, which Muir vigorously opposed. Nevertheless, Pinchot had a passion, not merely a business appreciation, for conservation: He deplored the destruction of forests as what he called a gigantic massacre, in which waste was a virtue. Largely because of Pinchot’s early leadership, the Forest Service has proven to be an invaluable force in support of conservation and biodiversity, not just of sustainable timber production. Although Pinchot and Roosevelt set aside much land for the express purpose of leasing it to private timber and mining corporations, these corporations and the politicians whom they funded wanted to cut down all the forests and sell the products as quickly as possible. Roosevelt and Pinchot, progressive Republicans, received much political opposition from the reactionary branch of the Republican Party, who led vigorous efforts to restrict funding to the Forest Service. In 1907, a congressional bill forbade the further creation of government forest preserves. In the last days before the bill took effect, Roosevelt and Pinchot set aside 16 million acres (65,000 square km) of forestland. Under Pinchot’s leadership, Yale forestry graduates received not only scientific but also practical and physical training. Nevertheless, these forestry graduates from the eastern states were not entirely prepared for the bars-and-brothels culture of the frontier towns of Idaho and Montana. The miners and lumberjacks did not take the foresters or the professors who trained them seriously. A hunter shot and killed a government forester in Montana in 1907. One congressman called the Forest Service “googleeyed, bandy-legged dudes from the East and sadeyed, absent-minded professors and bugologists.” Furthermore, private lumber and mining corporations continued to take control of government forestlands by two means: First, they simply trespassed, knowing that an underfunded Forest Service would not be able to document the illegal exploitation of government land; second, they paid homesteaders to take possession of tracts of land (which remained legal on government property) and immediately sell the land to the corporations. The foresters, who were nearly powerless to do their jobs, as well as the administrators of the Forest Service sometimes had to depend on personal contributions from Pinchot’s family wealth in order to get paid. Pinchot himself worked without a salary.

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414 placental mammals  414 Theodore Roosevelt did not run for reelection in 1908. His handpicked successor, William Howard Taft, who had promised to continue the work of conservation, won the election. Taft, however, did not carry through on his promise, but instead supported the politicians who wanted the Forest Service to be made as powerless as possible. Congress even passed a law in 1910 forbidding the Forest Service from publicizing itself. Pinchot published articles critical of Taft, who fired him in 1910. The U.S. Forest Service seemed destined for obscurity. Then, in summer 1910, a huge forest fire broke out in the mountains of Montana and Idaho, rapidly burning hundreds of square miles and threatening all of the major cities of the region. It was up to the Forest Service, with some help from a contingent of black soldiers, to bring the fire under control and protect the human inhabitants. Both the foresters and the soldiers undertook heroic efforts to prevent the spread of the fire and to evacuate the inhabitants. About 100 foresters lost their lives in the fire. Once the fire was contained, publicity of the foresters’ heroism raised the esteem of the Forest Service and may have guaranteed the survival of the agency. The heroism of the black soldiers is also credited with advancing racial equality in the United States. A few critics of the Forest Service, and of conservation in general, remained. Senator Weldon Heyburn, who had long been the Forest Service’s most bitter enemy, said that there would have been no fire at all if the lumber corporations had been allowed to cut down all of the trees. Gifford Pinchot may have been the first prominent person to articulate a philosophy of conservation from a government perspective. The whole point of conservation, to Pinchot, was to protect natural resources from immediate plunder by a few, so that they would be available for succeeding generations. The Earth, said Pinchot, “belongs of right to all its people, and not to a minority, insignificant in numbers but tremendous in wealth and power.” Later, Theodore Roosevelt expanded Pinchot’s view, referring to “the central task of leaving this land even a better land for our descendants than it is for us.” Conservation, said Roosevelt, “is a great moral issue!” Their political adversary, Senator William A. Clark, openly proclaimed the opposite view: “Those who succeed us can well take care of themselves.” President Taft said that Pinchot was “championing the cause of the oppressed and the downtrodden, and harassing the wealthy and the greedy and the dishonest.” Taft apparently intended this as a criticism, but Pinchot’s view prevailed. Pinchot remained active throughout his life as a speaker and writer in support of conservation. Pinchot, largely from his experience with the Big

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first entry Burn of 1910, believed that all forest fires were bad and had to be stopped, an approach that ecologists now know was mistaken. Nevertheless, his influence remained powerfully important, and he advised President Franklin Delano Roosevelt about conservation. He proposed, and Franklin Roosevelt approved, plans for an international conservation conference, to take place during the reconstruction after the Second World War. Both Roosevelt and Pinchot died before these plans could be put into action. Pinchot twice became governor of Pennsylvania. He died October 4, 1946. See also disturbances, ecological; federal government role in conservation (United States); Muir, John; succession, ecological. Further Reading Balogh, Brian. “Scientific forestry and the roots of the modern American state: Gifford Pinchot’s path to Progressive reform.” Environmental History 7 (2002): 198–225. Egan, Timothy. The Big Burn: Teddy Roosevelt and the Fire That Saved America. Boston: Houghton Mifflin, 2009.

placental mammals  See mammals. Pleistocene epoch  See Quaternary period, biodiversity in.

Pleistocene extinction  During the latter part, or immediately after, the Pleistocene epoch of the Neogene period, many species of large mammals became extinct at various locations around the world. Not without controversy, this extinction event has been attributed at least in part to hunting by humans. At the end of the most recent ice age, North America was the home of a much greater range of large mammals than is known from historical times (see table on page 415). For example: ●● ●●

●●

●●

In addition to grizzly, black, and brown bears, there was also a short-faced bear. In addition to cougars, there were lions and cheetahs resembling African species and a saber-toothed cat. In addition to the extant species of beavers, bison, and wolves, there was a larger species of each. There were large mammal species otherwise known only from the Old World, such as camels and horses.

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Pleistocene extinction  415 Some North American Mammals That Became Extinct   at the End of the Pleistocene Epoch Category

Common Name

Scientific Name

Bear

Short-faced bear

Arctodus simus

Beaver

Giant beaver

Castoroides ohioensis

Bovines

Shrub ox

Eucerotherium collinum

Harlan’s muskox

Boötherium bombifrons

Yesterday’s camel

Camelops hesternus

Large-headed llama

Hemiauchenia macrocephala

Saber-toothed cat

Smilodon fatalis

American lion

Panthera atrox

American cheetah

Miracinonyx trumani

American mastodon

Mammut americanum

Columbian mammoth

Mammuthus columbi

Jefferson’s ground sloth

Megalonyx jeffersonii

Shasta ground sloth

Nothrotheriops shastensis

Harlan’s ground sloth

Glossotherium harlani

Mexican horse

Equus conversidens

Western horse

Equus occidentalis

Pig

Flat-headed peccary

Platygonus compressus

Pronghorn

Diminutive pronghorn

Capromeryx minor

Wolf

Dire wolf

Canis dirus

Camels

Cats

Elephant-like

Ground sloths

Horses

●●

There were large mammal species different from their modern relatives, such as mammoths, mastodons, gomphotheres, and giant sloths.

The disappearance of these large mammals had a tremendous effect on the ecology of North America. In particular, numerous plant species produce fruits that can no longer be eaten in their entirety by any extant species of animal. There are several reasons that these extinctions are blamed on human hunting: ●●

●●

The extinctions were overwhelmingly of large mammals that would have been prime targets of hunters. Small mammals suffered far lower extinction rates. The extinctions occurred mainly in Australia and North and South America, which had not been previously inhabited by humans

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●●

●●

(see table on page 416). The large mammals would not have evolved, or learned, the fear of humans, which would have made them irresistibly easy targets. The humans who arrived in Australia and North and South America were fully modern and had advanced hunting capabilities. In Eurasia and Africa, in contrast, humans and large mammals had coevolved for thousands or millions of years, and the first humans in those regions had only primitive hunting capabilities. The timing of the extinctions corresponded closely to the first arrival of humans: about 50,000 years ago in Australia, and about 11,000 years ago in North and South America. Similar extinctions have occurred within historical times as a result of the first contact of humans with inexperienced large mammals and birds, such as the eradication

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416 Pleistocene extinction  416 of the moa birds by the first Polynesians in New Zealand, the eradication of elephant birds and giant lemurs by the first immigrants to Madagascar, and the eradication of passenger pigeons and near-eradication of bison by white Americans. Difficulties have been noted, and some responses formulated, regarding this Pleistocene overkill hypothesis: ●●

●●

●●

In North America, the arrival of humans was not the only thing that was happening 11,000 years ago. The most recent ice age was also ending, accompanied by rapid climatic changes. Tundra and grasslands retreated, and spruce forests spread. Fires also became more frequent. Defenders of the overkill hypothesis point out that the climate was becoming warmer, which should have encouraged the survival, not the extinction, of animals. The abundance and diversity of animals during the ice ages, however, suggest that a warmer climate was not necessarily an improvement for these animals. Any climatic change that would have altered the food base for these animals may have undermined their populations. Evidence is lacking for massive kills of large mammals. Arrowheads have been found in mammoth bones, but only occasionally, and mass grave sites of large animals are very uncommon. Native Americans, on whom the Pleistocene overkill in the New World is blamed, do not have a mass-slaughter approach to hunting. In fact, some Native American traditions are famous for spiritual preparation and gratitude before killing an animal and careful use of the animal carcass. However, the Native Americans that the Europeans encountered beginning just before the 16th century were perhaps very different from those that arrived in America at the end of the last ice age. In particular, Native Americans may have developed a conservation ethic in response to the collapse of the hunting stock caused by their careless ancestors.

Paleontologist Anthony Barnosky performed a thorough analysis of the Pleistocene extinctions around the world. He confirmed that large mammals died in disproportionately large numbers and at times that corresponded (within a thousand years) to human arrival. He concluded that neither climate change nor overhunting could by themselves

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first entry

Percent of Mammal Genera Becoming Extinct upon Arrival   of First Humans* Continent

Extinction

Africa

18%

Australia

88%

Eurasia

36%

North America

72%

South America

83%

*From Barnosky

have caused the extinctions. Together, however, they could have produced the Pleistocene extinctions. It would not have been necessary for either climate or hunters to have killed every last animal. Once a population becomes sufficiently small, it becomes vulnerable to extinction. Overhunted animal populations were vulnerable to extinction from climate changes, and climate changes may have reduced animal populations to the point that hunting could send them spiraling to oblivion. In 2008, some scientists announced the discovery of diamond fragments in Pleistocene sediments. They claimed that only an impact such as that of an asteroid could have produced such diamonds. This evidence raised the possibility that an asteroid impact may have contributed to the Pleistocene extinction. Although this event, if it occurred, may have had considerable local impact and may have been responsible for a sudden reversal of warming at the end of the last ice age, it is unlikely to explain the worldwide pattern described by Barnosky. After the initial publication, further evidence of a Pleistocene asteroid was not forthcoming, and most scientists have lost interest in it. All of the above processes depend upon the assumption that the precipitous decline in large mammal populations began after the climate and vegetation began to change and after the arrival of modern humans that had advanced stone tools for hunting, in particular the Clovis arrowhead points (named after a site in New Mexico). Research published by paleoecologist Jacquelyn Gill and associates in 2009, however, took a careful look at the sediment deposits in lakes in the eastern United States. They quantified three components of the sediments: pollen, an indicator of vegetation type; charcoal, an indicator of fire; and spores of the fungus Sporormiella, an indicator of the abundance of grazing mammals. This fungus is known to grow only in the dung of herbivorous mammals. The research-

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pollination  417 ers found that the decline in mammal abundance began before the changes in vegetation, not after, and it began before the arrival of the Clovis people. They concluded that it was the decline of the mammoths and mastodons that caused the vegetation change, not the other way around. The mammoths and mastodons were keystone species that had kept the trees browsed down, while grasses could readily sprout back after grazing. They also speculated that the decline in large mammals was caused by hunting, but not by the Clovis people. Their predecessors had killed many large mammals. The Clovis people developed advanced arrowheads and more efficient hunting because the large mammals were becoming rare, not the other way around. As the Earth enters into what many scientists consider the sixth mass extinction as a result of human activity, the lessons of the Pleistocene extinctions may be essential. Now, as then, it is not necessary to kill many animals to drive them to extinction. At the end of the Pleistocene, climate change reduced their habitats and made them vulnerable to hunting. Today, habitat destruction for agriculture and human habitation is the principal threat to the survival of most endangered species. See also mass extinctions; Neogene period, biodiversity in. Further Reading Barnosky, Anthony D. “Assessing the causes of late Pleistocene extinctions on the continents.” Science 306 (2004): 70–75. Donlan, C. J., et al. “Pleistocene rewilding: An optimistic agenda for twenty-first century conservation.” American Naturalist 168 (2006): 660–681. Gill, Jacquelyn L., et al. “Pleistocene megafaunal collapse, novel plant communities, and enhanced fire regimes in North America.” Science 326 (2009): 1,100–1,103. Summarized by Johnson, Christopher. “Megafaunal decline and fall.” Science 326 (2009): 1,072–1,073. Guthrie, R. Dale. “Rapid body size decline in Alaskan Pleistocene horses before extinction.” Nature 426 (2003): 169–171. Harris, John M. “Bones from the tar pits.” Natural History, June 2007, 18–22. Kennett, Douglas J., et al. “Shock synthesized hexagonal diamonds in Younger Dryas boundary sediments.” Proceedings of the National Academy of Sciences USA 106 (2009): 12,623–12,628. Martin, Paul S. Twilight of the Mammoths: Extinctions and the Rewilding of America. Berkeley: University of California Press, 2005. ———, and Christine R. Szuter. “Revising the ‘wild’ west: Big game meets the ultimate keystone species.” Chapter 3 of The Archaeology of Global Change: The Impact of Humans on Their Environment, edited by

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Charles L. Redman et al. Washington, D.C.: Smithsonian Institution Press, 2004. Miller, Gifford H., et al. “Ecosystem collapse in Pleistocene Australia and a human role in megafaunal extinction.” Science 309 (2005): 287–290. Mosimann, J. E., and Paul S. Martin. “Simulating overkill by Paleoindians.” American Scientist 63 (1975): 304–313. Pielou, E. C. After the Ice Age: The Return of Life to Glaciated North America. Chicago: University of Chicago Press, 1992. Steadman, David W., et al. “Asyncronous extinction of late Quaternary sloths on continents and islands.” Proceedings of the National Academy of Sciences USA 102 (2005): 11,763–11,768.

Pliocene epoch  See Neogene period, biodi-

versity in.

pollination  Pollination occurs when pollen is carried from the male cones or stamens of one seed plant to the female cones or stigmas of another plant. Seed plants benefit from cross-pollination for the same reasons that all species benefit from cross-breeding within genetically diverse populations. Even though the pollen may land on the female reproductive structures of the same plant, pollen will often not germinate and grow unless it lands on the female reproductive structures of a genetically different individual. Cones of most conifers, and flowers that are pollinated by the wind, often release their pollen in the early springtime before the leaves of most plant species have expanded. For example, in trees such as cottonwood and oak, flowers emerge from buds first, and leaves emerge only after pollination is completed. In this way the leaves do not block the movement of pollen to the stigmas. Male cones and wind-pollinated flowers must produce massive amounts of pollen, as the wind does not carry the pollen in any particular direction. Animal-pollinated flowers, in contrast, have a more reliable vector for pollination, as animals can consciously direct their movement from one flower to another of the same species. Because they do not waste as much pollen, these flowers do not produce as much pollen. Animal-pollinated flowers have petals, often brilliantly colored, and attract animals with nectar and pollen for food. The flowers may have conspicuous lines (sometimes visible only in the ultraviolet) that guide the pollinating insect to the middle of the flower where the nectar is located (see photograph on page 418). Wind-pollinated flowers do not generally produce nectar or have petals, which would only block the movement of pollen.

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418 pollination  418

first entry

It is important that pollen be carried from one flower to another of the same species. If flowers of many species were indiscriminately pollinated by animals, much of a flower’s pollen would be wasted on the stigmas of other species. Some species of flowers have characteristics that make them available to a wide range of pollinators. These characteristics include a round shape (radial symmetry), reproductive organs that are easily accessible, and a horizontal orientation. But many other species of plants have evolved flowers that mainly attract specialized pollinators. For example: ●●

Some flowers consist of a long tube too narrow for bees to climb into; the nectar can be reached only by animals with long tongues, such as butterflies or hummingbirds.

Cactus flowers are often pollinated by bats.  (Merlin D. Tuttle, Bat Conservation Society)

●●

●●

●●

Many flowers have nectar guides, which are colored lines directing the attention of pollinators to the center of the flower, where pollen and nectar are found. The beetle visiting this Geranium viscosissiumum in the Black Hills of South Dakota may be a pollinator or may just be drinking nectar without carrying pollen to another flower.  (Stanley A. Rice)

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Many flowers that hummingbirds specialize on are bright red, a color that attracts hummingbirds. The tubular petals of some flowers consist of an upper and lower lip that remain tightly closed unless a bee lands on the lower lip, pushing the tube open with its weight. A small fly would not weigh enough to push such a tube open. Flowers pollinated by moths or bats open at night and are light colored to reflect light (see figure).

These specializations are not perfect, however. The red, tubular flowers of Silene virginica look perfectly like hummingbird flowers, but it turns out that bumblebees are their most common pollinators. Animals, by specializing on certain flowers, are able to exploit a reliable source of nectar and pollen. Therefore pollinator specialization benefits both the plant and the animal. Natural selection has favored plants whose flowers successfully attract pollinators as well as pollinators that successfully obtain food from flowers, resulting in coevolution. Many flowers can be pollinated by more than one kind of animal. Bees have been observed to remove pollen from protruding stamens at the same time that moths obtained nectar from deep inside the flowers of the evening primrose Oenothera rhombipetala in Oklahoma. Flowers often have intricate adaptations to assure that pollen gets properly carried by animals. For example: ●●

●●

In some flowers, the weight of the pollinator causes the stamens to bend over and rub pollen onto the insect’s back. In some species of plants, the flowers come in two forms. In one form, the stamens are

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pollination



short and the styles are long; in the other form, the stamens are long and the styles are short (see figure). a flower with long stamens places pollen on the rear of the insect, while a flower with short stamens places pollen on the front of the insect. When the insect visits first a flower with short stamens and then a flower with short styles, the front of the insect will rub pollen onto the second flower’s short style. if the insect visits first a flower with long stamens and then a flower with long styles, the rear of the insect will rub pollen onto the second flower’s long style. Some flowers have pollen in packets, which they attach to the pollinator insect.

animal pollinators would benefit from flowers that provide copious amounts of nectar. However, flowers do not typically do this. the reproductive interests of the flowers are best served by keeping the pollinators on the move. not fi nding quite enough nectar in one flower, the pollinator moves on to the next, perhaps on a different plant. the nectar of some flowers contains chemicals that irritate the pollinator. For example, the wild tobacco Nicotiana attenuata produces nectar with benzylacetone, which attracts pollinators, and nicotine,

419

which repels them. the nicotine keeps the pollinators from staying too long at one flower. nectar is not the only floral product that pollinators use. Bees scrape much of the pollen off their bodies and use it to make bee bread. Bees that pollinate a central american bucket orchid, Coryanthes panamensis, gather wax that is a component of their own sex attractants. Flowers and pollinators do not always benefit one another. Some animals are nectar thieves, and some plants have evolved floral mimicry. Nectar thieves. animals visit flowers to obtain food; they pollinate the flowers more or less by accident. in some cases, insects will bore holes into the backs of flowers to obtain nectar that would be unavailable to them had they tried to crawl in from the front. Such “nectar thieves” consume a large share of the nectar in many species of flowers. natural selection favors pollinators that successfully obtain food from flowers, whether they pollinate them or not. in some cases, an insect may be both a pollinator and a thief. nectar-thief bumblebees have been observed to pierce the bases of Oenothera rhombipetala flowers in Oklahoma and drink the nectar. But because they approached the flowers from the front, their abdomens came in contact with the stamens and stigma anyway.

Some species of flowers have two or more forms. In this example, short stamens deposit pollen on the back of the bee, which carries it to a flower that has short pistils. The short-pistil flowers have long stamens, which deposit pollen on the bee’s abdomen. When the bee visits a short-stamen flower, its abdomen deposits pollen on the long pistils.

xviii+598_Biodiversity_F.indd 419

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420 pollination  420 Floral mimicry. Sometimes flowers deceive animals into transporting their pollen without rewarding them. For example: ●●

●●

●●

●●

Flies are attracted by the stench of rotting meat, and fly-pollinated flowers produce nectar with just such an aroma. Many flypollinated flowers open near the ground and have markings that resemble those of a carcass. The flies visit and pollinate these flowers, but receive no food. Numerous flower species, representing several unrelated plant families, have evolved this mode of pollination. Several species of orchids are pollinated by male wasps. The flowers of most of these orchids visually resemble female wasps and even produce nectar that resembles the female wasp’s sex attractant. A young male wasp copulates with the orchid, believing it to be a female wasp, and gets dusted with pollen. The wasp then makes the same mistake again, copulating with another orchid, delivering pollen from the first orchid to the stigma of the second. In some orchids, the flowers resemble hovering male wasps, and these are pollinated by the real male wasps that attack them. Some species of orchids, which themselves do not produce nectar, resemble lilies that do produce nectar. Young bees, which have not yet learned the details that distinguish the flowers that have nectar from those that do not, will often visit these orchids. The small, drab flowers of the lily, Scoliopus bigelovii, grow in dark, moist forests. They smell like mushrooms and are pollinated by fungus gnats.

These are called floral mimicry because the flowers imitate the appearance and even chemistry of corpses, female insects, or other flowers. This process is reminiscent of the evolutionary mimicry by which one animal species mimics another. Natural selection favors flowers that successfully attract pollinators, whether they reward them or not. In some cases, the bad luck of the deluded pollinator may contribute yet further to the benefit of the flowers. Male Lyssopimpla excelsa wasps eject sperm into Cryptostylis tongue orchids. When these males subsequently mate with female wasps, little or no sperm remain. In the reproductive system of many ants, bees, and wasps, unfertilized eggs develop into males. The female wasps therefore lay eggs that develop into males, which hatch and seek out more tongue orchids.

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first entry

The Study of Pollination Pollination is one of the most intensively studied natural phenomena. The traditional method of studying pollination is for a human observer to watch a flower and record data about how many pollinators, of which species, visit a flower during a period of time. A pollinator visit does not mean successful pollination, however. In many pollination studies, the investigator captures the pollinator as it leaves and microscopically examines it to estimate how much pollen, and of which plant species, it carries. In some cases, as in the study by Karen Bowers, the investigator uses fluorescent powder in place of pollen, thereby tracing the exact route of the pollinator. The effectiveness of pollination can be experimentally manipulated by surrounding flowers with a mesh bag that keeps the pollinators away. More recently, researchers have begun to use genetically modified plants to study pollination. Ecologist Danny Kessler and associates used genetically modified wild tobacco plants (Nicotiana attenuata) that either produced or did not produce benzylacetone (an attractant) or nicotine (a repellant) (see above). As a control, they used genetically modified plants that had normal production of these two chemicals. In this way, they experimentally demonstrated the effectiveness of the two nectar components.

Pollination and Evolution Pollination has had a tremendous impact upon the evolution of biodiversity. The flowering plants evolved near the beginning of the Cretaceous period. This event opened up new possibilities for coevolution. Flowering plants and pollinating insects (especially the hymenopterans and lepidopterans) underwent explosive speciation. The conifers, which dominated many landscapes prior to the origin of flowering plants, are usually pollinated by the wind, but scorpion flies pollinated some early conifers as long as 320 million years ago, 200 million years before the origin of flowering plants. The origin of flowering plants was not the origin of animal pollination, but of countless new pollination symbioses. Pollination may also contribute to speciation. A slight change in floral nectar chemistry might cause a small population of flowers to be attractive to a different pollinator, thus isolating it from other members of its species. Fig populations that are pollinated by different species of wasps are reproductively isolated from one another.

Pollinators in Agriculture and Conservation Pollination is not just something that happens out in the wild. Many important agricultural crops (such

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pollination  421 as fruits and nuts) depend on pollinators. About every third bite of food comes from a domesticated plant that depends on animal pollination. The honeybee Apis mellifera, a species introduced from the Old World, pollinates most American crops. In 2007, many honeybee hives suffered colony collapse disorder (CCD), in which the workers left and did not return, leaving the queen and grubs to starve. A significant association was found between CCD and a type of virus from Eurasia, but it was not clear whether the virus causes CCD or whether CCD was caused by parasitized honeybees that were already suffering from some other stress. Because honeybee hives are trucked all over the United States (about half of them are taken to California during the almond pollination season), diseases can spread rapidly among their populations. An alternative to reliance on Eurasian honeybees is to encourage wild pollinator species to take the place of honeybees. Wild pollinators can be more effective than honeybees because they are often specialists, while honeybees are generalists. For example, about 750 blue orchard bees (Osmia lignaria) can pollinate the same number of apple or almond trees as roughly 100,000 honeybees. The leaf-cutting bee (Megachile rotundata) is a very effective pollinator of alfalfa, and the bee Osmia ribifloris is especially effective in pollinating blueberries. Furthermore, wild pollinators work in a greater range of weather conditions than do honeybees. Nearly every animal-dependent crop species, even those not native to North America, is visited by a native (wild) pollinator. Honeybees will remain the major agricultural pollinator. They have strength in numbers, as there can be 100,000 bees in one hive, compared to wild pollinators, which may be solitary breeders. On the other hand, diseases are less likely to spread among wild pollinators, and there is less chance that any one disease can disrupt crop production if many wild pollinator species are available. However, to increase reliance upon wild pollinators, it will be necessary to reduce the use of pesticides. Pesticides do not harm honeybees as much as wild pollinators, since honeybee hives can be closed up and moved out of the way when pesticides are applied. Other relatively simple measures can be taken to promote the populations of wild bees. The bee Centris tarsata pollinates wild cashews but not cashews in commercial orchards. This bee needs floral oils that cashew trees cannot provide. But if Caribbean acerola cherries (which produce a lot of vitamin C and are themselves a commercial crop) are interspersed with the cashews, the wild bees survive very well. Wild pollinators can also be encouraged by having smaller, more diverse farms. Wild species perform up to 62 percent of the

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pollination on the small farms of the Delaware River Valley in the northeastern United States, but are very rare in the Central Valley of California, where fields are large and drenched with pesticides. Populations of wild pollinators can be supported by the presence of hedgerows and wildflower belts around farm fields. Smaller and more diverse farms offer many economic and ecological benefits, such as reduced dependence on pesticides, in addition to the encouragement of wild pollinators. Wild pollinators are also essential for the survival of many wild plant species. Conservationists have preserved giant cactuses in national parks in the southwest, but their pollinators have become rare. The survival of these cactuses into their next generation, therefore, is endangered. See also coevolution; flowering plants (angiosperms); mutualism; speciation. Further Reading Beismeijer, J. C., et al. “Parallel declines in pollinators and insect-pollinated plants in Britain and the Netherlands.” Science 313 (2006): 351–354. Bowers, Karen A. W. “The pollination ecology of Solanum rostratum.” American Journal of Botany 62 (1975): 633–638. Buchmann, Stephen L., and Gary Paul Nabhan. The Forgotten Pollinators. Covelo, Calif.: Island Press, 1997. DeWeerdt, Sarah. “Pollinator panic.” Worldwatch, November/December 2008, 24–29. Dunn, Robb. “Love is in the air.” National Geographic, December 2009, 120–133. Fenster, Charles B., et al. “Pollination syndromes and floral specialization.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 375–404. Galen, Candace. “Why do flowers vary? The functional ecology of variation in flower size and form within natural plant populations.” BioScience 49 (1999): 631–640. ———, and J. Cuba. “Down the tube: Pollinators, predators, and the evolution of flower shape in the Alpine sky pilot Polemonium viscosum.” Evolution 55 (2001): 1,963–1,971. Gaskett, Anne C., et al. “Orchid sexual deceit provokes ejaculation.” American Naturalist 171 (2008): E206–E212. Goulson, Dave. “Effects of introduced bees on native ecosystems.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 1–26. James, Rosalind, and Theresa L. Pitts-Singer, eds. Bee Pollination in Agricultural Ecosystems. New York: Oxford University Press, 2008. Kearns, C. A., et al. “Endangered mutualisms: The conservation of plant-pollinator interactions.” Annual Review of Ecology, Evolution, and Systematics 29 (1998): 83–112.

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422 pollution  422 Kessler, Danny, et al. “Field experiments with transformed plants reveal the sense of floral scents.” Science 321 (2008): 1,200–1,202. Reviewed by Raguso, Robert A. “The ‘invisible hand’ of floral chemistry.” Science 321 (2008): 1,163–1,164. Knight, Tiffany M., et al. “Pollen limitation of plant reproduction: Pattern and process.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 467–497. Pollan, Michael. “Love and lies: Orchids.” National Geographic, September 2009, 100–121. Proctor, Michael, Peter Yeo, and Andrew Lack. The Natural History of Pollination. Portland, Ore.: Timber Press, 1996. Raguso, Robert A. “Wake up and smell the roses: The ecology and evolution of floral scent.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 549–569. Ratnieks, Francis L. W., and Norman L. Carreck. “Clarity on honey bee collapse?” Science 327 (2010): 152–153. Ren, Dong, et al. “A probable pollination mode before angiosperms: Eurasian, long-proboscid scorpionflies.” Science 326 (2009): 840–847. Summarized by Ollerton, Jeff, and Emma Coulthard. “Evolution of animal pollination.” Science 326 (2009): 808–809. Richards, A. J. “Does low biodiversity resulting from modern agricultural practice affect crop pollination and yield?” Annals of Botany 88 (2001): 165–172. Ricketts, T. H. “Tropical forest fragments enhance pollinator activity in nearby coffee crops.” Conservation Biology 18 (2004): 1,262–1,271. Sessions, Laura A., and Steven D. Johnson. “The flower and the fly.” Natural History, March 2005, 58–63. Steffan-Dewenter, I., and T. Tscharntke. “Effects of habitat isolation on pollinator communities and seed set.” Oecologia 121 (1999): 432–440. Whitney, Heather M., et al. “Floral iridescence, produced by diffractive optics, acts as a cue for animal pollinators.” Science 323 (2009): 130–133. Wilcock, C., and R. Neiland. “Pollination failure in plants: Why it happens and when it matters.” Trends in Plant Science 7 (2002): 270–277.

pollution  Despite decades of national legislation, pollution by toxic chemicals remains an important problem, not just in areas with dense human populations, but also in protected areas and for endangered species. Below are some examples of serious pollution problems. Pesticide residues. About 5.7 billion pounds (2.6 billion kg) of pesticides are released into the environment every year worldwide. The crop on which the most pesticide is used is cotton, in which (since it is not eaten by people) pesticide residues are not considered an important problem. The United States imports many vegetables and fruits from Mexico.

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first entry The warmer climate in Mexico allows vegetables and fruits to be produced during the winter season. Mexico also has less stringent policies regarding the use of, and exposure of farm workers to, pesticides. Sociologist Angus Wright explains how the American demand for winter vegetables and fruits results in the exposure of Mexican children and adults to levels of pesticide that can cause nerve damage and death. The evolution of insect resistance to pesticides has prompted the owners of large Mexican farms to increase their application of pesticides. This has made some Mexican produce, including from the highly productive Culiacán region, unacceptable to the American market. Many consumers now demand organic produce, which is grown without the use of pesticides or inorganic fertilizers. Feedlot runoff. Many livestock feedlots produce as much sewage as a large city of humans. Feedlot sewage treatment is often less careful than the treatment of human sewage: Bacterial decomposition occurs in open pools from which floods can wash the sludge into streams and rivers. In addition to these specific point sources of pollution, pollution from generalized nonpoint sources may occur in runoff from livestock ranches. Even when properly treated, feedlot runoff is high in phosphates, which promotes eutrophication in freshwaters. Oklahoma sued Arkansas in 2005, claiming that poultry feedlot runoff was damaging Oklahoma rivers. In 2009, a federal judge recognized that the Cherokee Nation, into whose traditional territory much of the pollution drained, also had a legal interest in this ongoing suit. Litigation continues at press time. Mining runoff. Mining companies have traditionally left mine tailings piled up without containment, allowing acid and metal ions (such as cadmium and zinc) to leach into nearby creeks and groundwater. The contaminated water is often in primarily Native American communities, such as the notorious case of Picher, Oklahoma, most of whose residents are Miami and Cherokee, and where Tar Creek flows orange with acidic mine runoff. In the case of gold mines, it is not the minerals present in the ore so much as the cyanide and mercury used to extract the metal that is a cause of serious contamination. Persistent organic pollutants (POPs). Many organic contaminants decompose quickly, but some of them resist oxidation and decomposition long enough to contaminate whole food chains as a result of biomagnification. Many of these chemicals are fat-soluble and accumulate in animal bodies. Some of them mimic hormones, suppress immune function, and harm the nervous system. In the Gulf of St. Lawrence, the poisoned corpses of beluga whales were themselves considered to be toxic waste because of organic contamination.

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population biology  423 Pharmaceutical wastes. Normally, antibiotic resistance evolves in populations of bacteria that live in the bodies of people who overuse antibiotics. However, six times as much antibiotic is used for livestock as for people. Populations of bacteria can evolve resistance in the livestock, and feedlot runoff can contaminate freshwaters with these resistant bacteria—which can, in turn, transfer resistance genes to bacteria that infect humans. Bacteria resistant to antibiotics used by humans are routinely found in streams and rivers. In addition, pharmaceutical hormones (such as estrogen used for birth control) can persist in and contaminate freshwaters, even after sewage treatment. Estrogen can sterilize male trout at concentrations as low as 10 parts per trillion. Feminized fish are frequently found downstream from wastewater treatment facilities. The herbicide atrazine can feminize male frogs at a concentration thousands of times lower than occurs in agricultural runoff and even at a concentration 400 times lower than is found in rainwater in some agricultural areas. Because atrazine, at concentrations that might possibly be found in water supplies, can cause human fetuses to grow more slowly and to deliver early, this herbicide is banned in France, Germany, Italy, Sweden, and Norway. Pollutants permeate regions in which humans live and the natural areas surrounding them. Ecological processes such as biomagnification can make the problems even worse for humans. See also biomagnification; resistance, evolution of; rivers, streams, ponds, and lakes. Further Reading Badgley, C., and Ivette Perfecto. “Can organic agriculture feed the world?” Renewable Agriculture and Food Systems 22 (2007): 80–85. Bank, M. S., et al. “Mercury bioaccumulation in northern two-lined salamanders from streams in the northeastern United States.” Ecotoxicology 14 (2005): 181–191. Batty, Lesley C., and Kevin B. Hallberg. Ecology of Industrial Pollution. New York: Oxford University Press, 2010. Blauenstein, A. R., et al. “UV repair and resistance to solar UV-B in amphibian eggs: A link to population declines.” Proceedings of the National Academy of Sciences USA 91 (1994): 1,791–1,795. ———, et al. “Ultraviolet radiation, toxic chemicals, and amphibian population declines.” Diversity and Distributions 9 (2003): 123–140. Chavez, Will. “Cherokee Nation appeals to join lawsuit against poultry industry.” Cherokee Phoenix, December 30, 2009. Available online. URL: http://www.cher okeephoenix.org/20991/Article.aspx. Accessed August 14, 2010.

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Damsgaard, I., et al. “Persistent pesticides in human breast milk and cryptorchidism.” Environmental Health Perspectives 114 (2006): 1,113–1,118. Gosling, P., et al. “Arbuscular mycorrhizal fungi and organic farming.” Agriculture Ecosystems and Environment 113 (2006): 17–35. Green, R. E., et al. “Farming and the fate of wild nature.” Science 307 (2005): 550–555. Hayes, T. B., et al. “Herbicides: Feminization of male frogs in the wild.” Nature 419 (2002): 895. ———, et al. “Hermaphroditic, demasculinized frogs after exposure to the herbicide atrazine at low ecologically relevant doses.” Proceedings of the National Academy of Sciences USA 99 (2002): 5,476–5,480. Hole, D., et al. “Does organic farming benefit biodiversity?” Biological Conservation 122 (2005): 113–130. Lotter, D., et al. “The performance of organic and conventional cropping systems in an extreme climate year.” American Journal of Alternative Agriculture 18 (2003): 146–154. Mäder, P., et al. “Soil fertility and biodiversity in organic farming.” Science 296 (2002): 1,694–1,697. Oklahoma Department of Environmental Quality. “Tar Creek Native American issues final report.” Available online. URL: http://www.environment.ok.gov/ documents/TarCk/NAIssuesFinalReport.pdf. Accessed August 14, 2010. Pierce, B. “The effects of acid precipitation on amphibians.” Ecotoxicology 2 (1993): 65–77. U. S. Water News Online. “Oklahoma readies for another court fight, blaming river’s decline on poultry.” Available online. URL: http://www.uswaternews.com/archives/ arcrights/5oklaread7.html. Accessed August 14, 2010. Wright, Angus. The Death of Ramón González: The Modern Agricultural Dilemma. Rev. ed. Austin: University of Texas Press, 2005.

population biology  A population is all of the individuals of a species within a defined area, within which the individuals could potentially interbreed. A population consists of demes. Within each deme, interbreeding is not only possible but occurs with some regularity. The delimitation of a population is somewhat arbitrary in practice. One can speak of the human population of the Earth, or of California, or of San Diego. One could study the population of dandelions in one yard or in all the yards in the country. To preserve biodiversity, it is necessary to rescue the small populations of rare species, making population biology an intensely important subject for conservationists. All individuals in a population are members of the same species, but that is where the uniformity ends. There are several sources of diversity within populations:

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424 population biology  424 ●●

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Populations usually contain individuals of many different ages and sizes. Adult individuals reproduce, while juveniles do not; and adults may produce and/or consume more resources than do juvenile individuals. Thus two populations of one species may differ from one another even if the population size is the same: One of the populations may have many small, young individuals, while the other has many large, older ones. A population that consists of 1,000 buffalo of which 300 are calves may consume less grass than a population of 1,000 buffalo of which only 50 are calves. In plant populations, individuals can differ greatly in size even though they have the same age. This occurs in part because plants are capable of surviving on very limited resources for months or years; therefore some old plants are frequently smaller than young plants in the same population. Among most animals, populations consist of a mixture of males and females, usually but not always in roughly equal proportions. In plants, the sexual characteristics of a population can be much more complex. In some species of plants the populations consist of individual plants that have bisexual flowers. In other species, some plants have flowers that have only male parts, while others have flowers with female parts. Many other sexual combinations exist in plant species. Populations almost always consist of individuals of many different genotypes, resulting in a diversity of phenotypes. Often a human observer cannot see the differences among individuals in a population. Scientists can detect genetic differences among individuals in plant and animal populations only by comparing the enzymes or DNA of the individuals.

The fact that crop and domesticated animal populations contain heritable diversity has been known since ancient times. Ancient herdsmen assumed livestock offspring would have characteristics like those of the parents. Charles Darwin recognized that if populations of domesticated species have heritable diversity, then populations of wild species probably do also, for all domesticated species were once wild. As a result, he was able to explain that the process of evolution was caused largely by means of natural selection, just as the evolution of domesticated species was caused by artificial selection, or breeding, imposed by humans. Darwin studied animal breeding, particularly pigeon breeding. The various breeds

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first entry of pigeon that Darwin studied differed strikingly from one another in appearance. Some had hoods of feathers, others had fanlike tails; some did aerial somersaults, some made unusual sounds. One had an “enormously developed crop, which it glories in inflating, [and which] may well excite astonishment and even laughter,” as he wrote in the first chapter of The Origin of Species. Darwin then wrote, Altogether a score of pigeons might be chosen, which, if they were shown to an ornithologist, and he were told that they were wild birds, would certainly be ranked by him as well-defined species.

Despite these enormous differences between breeds of pigeon, Darwin was convinced (as were most of his fellow scientists, even before he proposed the general theory of evolution) that they had all been derived from a single ancestral species of wild pigeon. Wild pigeons may all look alike to humans. Certainly wild pigeons do not have fanlike tails or inflatable throats. Yet the genetic basis for big tails and inflatable throats existed and probably still exists within the wild pigeon populations. The wild pigeon populations, like nearly all populations, contain a great deal of hidden genetic variation. In some species, what appear to be individual members of the population are asexually propagated copies of one individual—that is, they are a clone. Some such clones can be extremely large. The largest organisms in the world may be clones of aspen trees, in which many trunks are connected by underground stems that can form a network over hundreds of acres.

How Populations Grow New individuals are added to a population by birth and by the immigration of individuals from other populations. Individuals are removed from the population by death and when individuals leave the population (emigration). Populations grow if more individuals are added than removed; populations decline if fewer are added than removed. Imagine a pond in which frogs live. This imaginary frog population doubles in size every day and fills the pond after 30 days of growth. On what day is the pond half-filled with frogs? The pond is half full of frogs on the 29th day. On the 29th day, a frog could look around the pond and see that there is still a lot of free, open water not yet filled. An optimistic frog would say that the pond is still half empty. Yet the crisis of the pond being completely filled is only one day away from happening. This story depicts quite accurately the way populations can grow. In the simplest case, one bacterial

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population biology  425 cell (in generation 0) divides to become two cells (in generation 1), and these two cells divide to become four (in generation 2), and so forth. In this example, the bacterial population grows from a single cell to over a billion in just 30 generations. In some bacterial species, under ideal conditions, such population growth can occur overnight in a laboratory. In another 30 generations, this number could rise to more than a billion billion (1018) cells. This kind of growth is called exponential, because the superscript, called an exponent, indicates how many times the base number (in this case 2) is multiplied by itself. On a graph of population size as a function of time, exponential growth produces a curve in which not only the size of the population but also the rate of increase increases. In contrast, linear growth would occur if the population increased at a constant rate, resulting in a straight line on a population growth graph. All populations are capable of exponential growth. The exponential growth of populations can take humans by surprise because the human mind generally thinks in linear terms. Most populations are more complex than those of bacteria. For instance, most animals reproduce in pairs, not as individuals. Furthermore, in bacteria the parent “dies” because it splits in half and literally becomes the offspring, whereas in animal and plant populations the parents persist and perhaps continue to reproduce even after their offspring reach adulthood. These circumstances make the mathematical calculations of population growth for animals and plants more complex than for bacteria. However, these complexities do not alter the exponential shape of the growth curve. Even a very slow reproductive rate can result in exponential population growth. One of the first people to write about the fact that human populations cannot grow indefinitely was economist Thomas Malthus in 1798. After reading his writings, Darwin applied the same principle to plant and animal populations: It is the doctrine of Malthus applied with manifold force to the whole animal and vegetable kingdoms.  .  .  . Although some species may be now increasing . . . in numbers, all cannot do so, for the world would not hold them.

A mathematical equation that describes population growth is: N 2 = N1ert ●● ●● ●●

N1 is the population size at time 1. N 2 is the population size at time 2. e is the natural base of logarithms.

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r is the rate of increase as a decimal fraction, per year. This variable is also called the Malthusian parameter after Thomas Malthus. t is the amount of elapsed time.

Exponential population growth can occur temporarily when a few plants or animals enter a new habitat in which there is a superabundance of food and space for them. This has often happened when humans have carried plants or animals away from their native habitat and introduced them into new regions. Darwin noticed this also: Still more striking is the evidence from our domestic animals of many kinds which have run wild in several parts of the world; if statements of the rate of increase of slow-breeding cattle and horses in South America, and latterly in Australia, had not been well authenticated, they would have been incredible.

Two male and six female pheasants were introduced to an island off the coast of Washington. Within five years, there were 1,325 pheasants—an increase of 180 percent per year. Sheep populations also increased rapidly when they were introduced to Tasmania. The human population has experienced an exponential increase in recent centuries. Within the last few years, the growth rate of the human population is no longer increasing as fast as it once was (see below), even though it is still increasing. As a result, the exponential phase of human population growth may be coming to an end—but not any time soon. A population with a higher fertility rate can grow faster than a population with a lower fertility rate. The fertility rate is the average number of offspring per reproductive individual or, in many animals, per female. A Princess Anne tree (Paulownia tomentosa) can easily produce 50,000 small wind-blown seeds in a single year. A population of such trees has a very high average fertility rate, and its population would grow very fast if all of its seeds fell in an area with unlimited space, light, water, and minerals. Contrast this with a black walnut tree (Juglans nigra), which can produce only a few hundred seeds at a time. This species has a much lower average fertility rate, and its population would grow much more slowly in a region with unlimited resources. Not only do different species have different average fertility rates, but different populations within a species may have different fertility rates. Consider human populations as an example. As of 2011, the world average fertility rate is 2.5. That is, the ­average

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426 population biology  426 woman in the world has 2.5 children during her lifetime. The fertility rate in Niger is 7.0 children per female, almost three times the world average, while in Belgium the fertility rate is 1.4 children per female. Partly as a result, Niger’s population has been growing 18 times faster than Belgium’s: Niger’s population is 3.6 percent bigger each year, while in Belgium it is only 0.2 percent bigger each year. All around the world, human fertility rates are declining slightly. For example, the fertility rate in Bangladesh was 6.7 in 1953, while it was 2.4 in 2010. As a result, the world population growth rate is declining as well. Among the reasons for this appear to be: ●●

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Greater availability and reliability of food and medicine. This has resulted in a worldwide reduction in infant mortality. When parents have a greater assurance that their offspring will survive, they often choose to have fewer offspring. Greater availability of birth control options. This allows parents (especially mothers) to translate their desire to have fewer offspring into practice. Greater availability of education and opportunities for women. In most countries, women now have more choices as alternatives to childbearing.

Despite this decline in birth rate, world population is still growing rapidly. The current rate of world population increase, 1.2 percent, in a world population of 7 billion people means that each year the world contains about 84 million more people than the year before! A population with a lower age at first reproduction can grow more rapidly than a population that has a higher age at first reproduction. Most farm weeds, such as velvetleaf, ragweed, and foxtail, are annuals, which reproduce during their first and only year of life. Perennial plants live for two or more years. Princess Anne trees have a much later age of first reproduction than weeds. Not surprisingly, annual weed populations can grow more rapidly than tree populations, even though a Princess Anne tree can produce, in a given year, more seeds than most annual weeds. Moreover, many trees do not reproduce heavily every year. They may produce few or no seeds for several years, saving up for a mast year during which they dump seeds all over the ground. The human age at which reproduction first becomes possible has decreased in some countries. In Europe, the average age of first menstruation was 17 in the mid-1800s, while today it is 13. This has

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first entry probably occurred because children receive better nutrition today than in the past. Fertility rate and age at first reproduction both affect population growth. A female cockroach can lay a hundred eggs in a single egg case and therefore has a higher fertility rate than a bacterium in which the “parent” can produce only two “offspring.” However, the bacterial population can grow faster because the bacteria can divide every half hour, while at least two weeks is required for a female cockroach to produce an egg case. Some species are adapted to live and grow in places in which some disturbance such as fire or human activity has removed the plant cover. Weeds that live in these disturbed areas grow quickly, produce many offspring, and have short life spans. This allows them to grow abundantly in habitats that persist for only a short time. Weeds cannot compete against the bushes and trees that later grow in these disturbed areas. Natural selection has favored rapid growth and early reproduction in weeds because their populations are usually well below the number that the resources can support. Other species, such as walnut trees, are adapted to live in stable conditions. Evolution has favored slower growth and later reproduction in these plants, allowing them to compete well against other species, because their populations are usually at or near the number that the resources can support. Small, juvenile individuals generally do not reproduce, nor do very old individuals. Therefore, to understand a population’s growth rate, one must know the size and age differences among individuals within the population. Consider an example from human populations. Niger has about 16.1 million people and Belgium has about 11 million people. In Belgium, 17 percent of the population is under the age of 15, and 17 percent of the population is over the age of 65. This represents a stable population. In Niger, however, 49 percent of the population is under 15 and only 2 percent of the population is over 65 years of age. Thus, when we compare the age structure of the two populations, we see that a large number of youngsters in Niger will soon be entering their reproductive years, whereas in Belgium this is not the case. Even if both countries had low fertility rates, Niger would soon experience an explosive population growth and Belgium would not. Because of the very large number of children in the world (27 percent of the world population is under age 15), world population will continue to grow rapidly for many years, despite the decline in the world average fertility rate. Some organisms produce a large number of small offspring, most of which die. Small offspring—for

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population biology  427 instance, the small seeds from a Princess Anne tree, which may weigh 7-millionths of an ounce (200 μg)—have very little chance of survival. There is very little food stored in the seed to nourish the seedling as it germinates. If this seed lands in a thick sward of grass or underneath bushes or trees, it has very little chance of surviving even if it germinates. The Princess Anne tree, however, produces a large number of these seeds. Perhaps one of these seeds will land in a suitably open, sunny, fertile spot. The parent tree can easily afford to produce many seeds, since each seed requires few resources and is “cheap” to produce. Other organisms produce a small number of large, expensive offspring, more of which survive. Walnut trees produce large fruits, each one with a large embryo, a dense hard shell, and a thick husk. Each one can weigh more than three ounces (100 g), 500,000 times as much as a Princess Anne tree seed. Such a large seed has a greater food reserve that allows it to survive as it germinates amidst a dense growth of other plants. The seedling itself is large enough to outgrow many of its neighboring seedlings. The walnut tree, however, cannot afford to produce very many such “expensive” seeds. Both trees make investments that may be equally successful. The Princess Anne tree is gambling: Each seed is a lottery ticket that is almost guaranteed to lose, but the plant invests in a very large number of tickets. The walnut is making fewer, safer investments. Animal examples also abound. Some insects, for example, lay a large number of eggs, most of which die. These animals produce a large number of cheap offspring. Cattle, in contrast, produce very few offspring, but take very good care of them. Most of their offspring survive. Humans are among the most extreme examples of animals that put much investment into each individual offspring. Each offspring is carried in the mother’s womb for nine months, is quite large when born, is fed and protected for years of helpless childhood, and educated for many more years. Darwin also recognized that a species with a high fertility rate could end up having a population growth rate no greater than a species with a low fertility rate: The condor lays a couple of eggs and the ostrich a score, and yet in the same country the condor may be the more numerous of the two; the Fulmar petrel lays but one egg, yet it is believed to be the most numerous bird in the world. One fly deposits hundreds of eggs, and another, like the hippobosca, a single one; but this difference does not determine how many individuals of the two species can be supported in a district. It would

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suffice to keep up the full number of a tree, which lived on an average for a thousand years, if a single seed were produced once in a thousand years, supposing that this seed were never destroyed, and could be ensured to germinate in a fitting place. So that, in all cases, the average number of any animal or plant depends only indirectly on the number of its eggs or seeds.

The number of surviving offspring that are produced by an organism is a measure of its fitness. This term fitness as used by population and evolutionary ecologists should not be confused with the term physical fitness as used by physiologists and exercise scientists.

Limits to Population Growth Exponential population growth cannot continue in a world with limited food, space, and other resources. Economists sometimes assume that population growth and resource use can continue essentially forever. As economist Kenneth Boulding wrote, “Anyone who believes exponential growth can go on forever in a finite world is either a madman or an economist.” Recently, ecological economics, which recognizes the limits to growth, has become more widely accepted. Survivorship is how many offspring survive from the total number born and how this number of survivors changes over time. Populations differ from one another in their patterns of survivorship. In some populations, most individuals survive until old age; in others, a relatively constant proportion of individuals die at all ages; in others, most deaths occur among the youngest individuals. Humans are an example of the first pattern, in which most deaths are of old individuals. Around the world, only 4.6 percent of human infants die within their first year. In some countries without adequate nutrition, sanitation, and medical care, up to 15 percent of the infants die during their first year. In most industrialized countries, such as the United States and Japan, infant mortality rate is less than 1 percent. The third pattern seems to be the most common in nonhuman species, because the youngest and smallest individuals are the ones least capable of responding to the dangers of the environment, such as drought, disease, or crowding. In plants, seedlings are also close to the ground, which can be very hot and dry, yet at the same time they have very small roots. It is the young plants also that are most tender and vulnerable to fungal infection. Darwin not only noticed this but actually counted the numbers of seedlings that died: Seedlings .  .  . are destroyed in vast numbers by various enemies; for instance on a piece of

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ground three feet long and two wide, dug and cleared, and where there could be no choking from other plants, I marked all the seedlings of our native weeds as they came up, and out of 357 no less than 295 were destroyed, chiefly by slugs and insects.

Many plant populations contain a large number of seeds that lie dormant in the soil for months, years, or centuries. They form a seed bank from which a few seeds may germinate every few years or which may remain dormant until some event, such as a forest fire, removes the vegetation that has been shading them. A plant population can therefore begin growing again even if all above­ ground evidence of its existence has disappeared. In other plant species, such as in some tropical trees, many seedlings will germinate in the shade, grow a few centimeters, then wait for years without growing very much, until the branches above them are cleared away by a disturbance. When bright light becomes available, these small seedlings will quickly grow. Some of the factors that limit population growth are unaffected by the size or density of the population—for instance, a flood or a freeze. Such a factor may destroy more organisms in a large population than in a small population, for the simple reason that a larger population has more individuals to get in the way. However, the factor itself is densityindependent, for it occurs regardless of the presence of populations. Many other factors, however, reduce the growth of populations with high density much more than populations with low density. If a factor has a greater effect at higher population densities, it is densitydependent. Examples include: ●●

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Intraspecific competition. Individuals that are far apart have no effect on one another, and each individual has access to an unlimited amount of resources. Competition results when crowded individuals do not have access to unlimited resources (see figure). In this case, the competition is intraspecific (within a species). Competition can have many effects on a population, one of which is a reduction in the number of offspring that the average individual produces. Attack by animals. Sphinx moths look for tomato plants, on which they lay eggs that hatch into voracious hornworm caterpillars. A dense grouping of tomato plants may be easier for a sphinx moth to find than a single, isolated tomato plant. A big herd of animals may be more easily visible

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to a predator than is an isolated individual; a herd cannot as easily hide. Crowded populations may therefore suffer more from attacks by animals that eat them. Insect pest populations can grow more rapidly in large, dense crop populations than in small, sparse populations. Modern agriculture requires large, dense populations of crops, with the inevitable result that pest populations explode. Infectious disease. Diseases will spread much more rapidly through a dense human population, as individuals come in contact with one another directly or with each other’s breath or wastes. Some human diseases require a certain minimum population size to persist. Smallpox was eradicated not because literally everybody in the world was vaccinated, but because there were so few unvaccinated people in any given locality that the population of viruses could no longer spread. The chestnut blight, a fungal disease that destroyed all of the adult chestnut trees in the forests of eastern North America, did not spread to isolated chestnut trees that had been planted in other parts of the country before the outbreak of the blight. Individuals in dense populations may experience stress and therefore be more susceptible to disease. Diseases spread more rapidly in large, dense populations of crop plants than in small, sparse populations, just as is the case with insect pests.

Cones of bishop pines (Pinus muricata) open only after a fire and produce a thick growth of seedlings the next year. In this photograph, taken seven years after a fire in the Purísima Hills of coastal California, the seedlings have grown into a dense population of trees, each much smaller than trees that grow at lower density.  (Stanley A. Rice)

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population biology  429 Although most density-dependent factors are biological, some physical factors can also be influenced by density. A fire, for instance, is more likely to start and spread in a dense than in a sparse plant population, particularly if the dense plant population has much litter or many dead or dying stems. Darwin realized that such density-dependent factors customarily prevented populations from having exponential growth: A plant which annually produces a thousand seeds, of which only one of an average comes to maturity, may be . . . said to struggle with plants of the same and other kinds which already clothe the ground. . . . Lighten any check, mitigate the destruction ever so little, and the number of the species will almost instantaneously increase to any amount.

While very high densities can have negative effects on individuals within populations, there can also be beneficial effects of moderate crowding. While a large population of prey might be more easily spotted by a predator, it might also be able to defend itself more effectively than an isolated individual. For example, a herd of animals can carry out defensive maneuvers to ward off predators and protect the young. Among plants, an isolated individual in a bare field might suffer the consequences of soil erosion and hot dry winds, from which a moderate density of other plants might be able to shield it. The benefits of moderate population density, relative to low population density, were first pointed out by ecologist Warder C. Allee and are called the Allee effect. The maximum number of individuals that can survive, given the available resources at a particular time and place, is called the carrying capacity. Density-dependent factors may cause populations to grow more slowly as they approach the carrying capacity. If the population exceeds its carrying capacity, density-dependent factors may cause the population to decrease back down to the carrying capacity. In agricultural situations, the ideal density is that which allows each individual to reproduce at its maximum level, resulting in optimum yield. It is not always possible to calculate an exact carrying capacity, because the carrying capacity will be higher if the average individual in the population uses fewer resources. This is especially true of the carrying capacity of humans. Americans use about one-third of the energy and material resources of the world. If everybody in the world used as many resources as Americans, the carrying capacity of the human species would be less than 900 million people. Clearly, the world cannot support a human

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population of several billion people living at American standards. Occasionally, populations increase until they reach the carrying capacity, at which density the population levels off. Sheep were first introduced to Tasmania about 1820. Their population density was low, and there were no native mammals that were able to compete with them for food. The sheep population underwent exponential growth, then leveled off at about 2 million, where it has remained ever since. It appears that 2 million is their approximate carrying capacity in Tasmania. Examples of such smooth population growth patterns are, however, very rare. It is more frequent to find drastic fluctuations from year to year. Populations that grow far beyond their carrying capacity may suffer a severe crash. In some cases, populations rise and fall in a cyclical pattern, for reasons that are not entirely clear. Darwin noticed that populations underwent dramatic fluctuations: We behold the face of nature bright with gladness, we often see superabundance of food;  .  .  . we do not always bear in mind, that, though food may be now superabundant, it is not so at all seasons of each recurring year.

Population growth can level off at the carrying capacity in several ways. Density-dependent factors may cause the death of individuals. Density-dependent factors may cause fertility rates to decline, without necessarily causing death. If birth rates decline, while organisms continue to die at the same rate, the population growth will decline as surely as if the organisms suffered increased death. Finally, individuals may emigrate from dense populations. As noted above, the human population growth rate is declining slowly because there are more opportunities for reliable food, medicine, education, and opportunity. In this way, humans are different from most animal species, whose population growth rates decline mainly due to death and emigration. Some observers, such as biologist Garrett Hardin and economist Kenneth Boulding, expected the human population to respond to resources the same way as populations of other animal species. In 1964, Boulding published his “utterly dismal theorem”: “If the only thing which can check the growth of population is starvation and misery, then the ultimate result of any technological improvement is to enable a larger number of people to live in misery than before and hence to increase the total sum of human misery.” Fortunately, this has proven to not be the case. Because modern agriculture promotes dense populations of single crop species, the eruption of

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430 population genetics  430 pest population outbreaks is nearly inevitable. By reducing the density of any one crop species, for example by planting alternating strips of each crop species rather than entire fields of each crop, pest outbreaks can be reduced in frequency and severity. This reduces the need for the heavy use of pesticides. In this way, human activities such as agriculture would follow the same laws of nature (in this case, of population biology) as do the activities of all other species. See also Darwin, Charles; natural selection; population genetics. Further Reading Brown, Lester R., Gary Gardner, and Brian Halwell. Beyond Malthus: Sixteen Dimensions of the Population Problem. Worldwatch Paper 143. Washington, D.C.: Worldwatch Institute, 1998. Cohen, Joel E. “Ten myths of population.” Discover, April 1996, 42–47. Darwin, Charles. “The struggle for existence.” Chap. 3 in The Origin of Species by Means of Natural Selection or the Preservation of Favored Races in the Struggle for Life. New York: New American Library, 1958. Hardin, Garrett. Living within Limits: Ecology, Economics, and Population Taboos. New York: Oxford University Press, 1993. Livi-Bacci, Massimo. A Concise History of World Population. 3rd ed. London: Blackwell, 2001. Population Reference Bureau. “2011 World Population Data Sheet.” Available online. URL: http://prb.org/ pdf11/2011population-data-sheet_eng.pdf. Accessed August 8, 2011. United States Census Bureau. “International Data Base.” Available online. URL: http://www.census.gov/popu lation/international/data/idb/informationGateway.php Accessed August 8, 2011.

population genetics  A population is defined as a set of organisms, all of the same species, that can interbreed with one another because there are no reproductive barriers and because they all live in the same place. A local population in which interbreeding is not only possible but frequent is considered a deme. The genes of the organisms in a deme, or in a population, are therefore considered to be a single gene pool. Population genetics is the study of genetic variation in populations. Genes, encoded in DNA, are the only information that passes from one generation to the next in most species, although many animal species, especially humans, transmit cultural information from one generation to the next. In cells of eukaryotes, most of the genes are in the nucleus, although there are also many cytoplasmic factors (genes in chloroplasts and mitochondria). Genes (the

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first entry genotype) affect the characteristics of organisms (the phenotype); however, phenotype changes that occur during the life of an organism cannot be transferred back to the genotype. That is, acquired characteristics cannot be inherited. Evolution occurs in populations. Therefore, the study of genetic variation in a population is the study of the raw material available for evolution in that population. The only evolution that can occur is what the genetic variation permits. The study of population genetics is essential to the preservation of biodiversity, because a species can only survive if enough of its populations survive, and a population can survive only if there is enough genetic variation.

Populations Have Genetic Variability In most species, an individual organism can have at most two alleles for a given locus (plural loci) or location on a chromosome: It has two copies of one allele if it is homozygous, and one copy of each of two alleles if it is heterozygous for that locus. A population can have many alleles for each locus. In many laboratory populations, one allele predominates (the wild type) over a few rare mutant alleles, which produce defects in the phenotype. In many wild populations, for many loci, there is more than one common allele (a polymorphism). In contrast, populations of agricultural crops and livestock have very little genetic variability (see figures on page 431). Populations can differ from one another in the types of alleles that they have for a locus. Even if they have the same alleles, they can differ in the relative frequencies of these alleles. For example, in the MN blood protein group in humans, the N allele strongly predominates in Australian aboriginal populations, and the M allele in Navaho populations, while the two alleles occur at approximately equal frequency among Caucasians in the United States. The three populations differ genetically, even though all of them have the same two alleles for the locus. Because evolution depends upon the variation in the gene pool, one would expect that evolution would proceed more rapidly in a population that has greater genetic variability. This is the idea behind the fundamental theorem of natural selection proposed by evolutionary biologist R. A. Fisher. Fruit flies (genus Drosophila) have a short generation time and can be raised easily in the laboratory. Geneticists such as Thomas Hunt Morgan and Theodosius Dobzhansky pioneered the use of fruit flies for genetic and evolutionary studies. Experiments with Drosophila indicate that populations that have greater genetic variability grow faster than populations with less genetic variability when that population is exposed to new environmental conditions (for

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population genetics  431 example, a change in temperature), which is consistent with Fisher’s theorem. One difficulty that geneticists often encounter when studying populations is how to define an individual. The etymology of the word itself suggests that an individual is an entity that cannot be divided without killing it. With vertebrates, it is easy enough to recognize an individual. With plants and some invertebrates, however, it is not as easy, as in these examples: ●●

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Plants and starfish can be cut up into pieces, and a new organism can grow from each piece. Are plants and starfish individuals? Many plants and invertebrates produce seeds and eggs asexually, resulting in numerous organisms that are genetically identical. Should these clonal organisms be considered individuals? Some plants spread by asexual means, for example by underground branches. In this way, an entire field of goldenrod plants (ramets) might be a single genetic individual (genet). The connections among the ramets might be maintained or might not, depending upon the species and circumstances. Should ramets be considered individuals? It may make more sense for a tree to be considered a population of branches rather than an individual. Somatic mutations can occur in buds. A branch that grows from a bud that has a somatic mutation is genetically different from the other branches of the tree. Each branch of a tree may differ in its ability to resist herbivores. Insect herbivores, which have several generations in a single year, can evolve much faster than trees. It has been suggested that the generation of somatic mutations allows trees to keep up with the evolutionary pace of the insects that eat their leaves. If this branch produces seeds, the genetic differences can be passed on to the next generation. Does a tree function as a genetic and even as an evolutionary population?

Measuring Genetic Variability in Populations It has often proven very difficult to measure variability for any given gene or overall genetic variability in populations. Several approaches have been used: Phenotypic traits. One approach is to estimate variability of a measurable phenotypic trait (e.g., area of a leaf or length of a bird’s beak). This variability can be expressed as a variance, as a standard

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Every wild population contains genetic variability. This variability is usually invisible. Genetic variation for the production of floral pigment, however, is visible in this population of Sabatia campestris in Oklahoma (top). Agricultural populations, in contrast, contain very little genetic variability. This entire field of onions in California may be genetically identical (bottom).  (Stanley A. Rice)

deviation, as a standard error, or as a coefficient of variation. This variability among individuals, however, is caused partly by genetic differences among the individuals (the heritability) and partly by differences among the individuals in the environmental conditions they have experienced. Variance, as originally defined by R. A. Fisher, is the average squared deviation from the average value; because of the square component, variance is symbolized as s2 . The heritability component of the variance is symbolized as h2 . Genetic and ­environmental

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432 population genetics  432 variability is also symbolized by the letter V. Thus, total phenotypic variability (V P) consists of genetic variability (VG) and environmental variability (V E). Genetic variability can itself be divided into two components: the variability that results from diversity of alleles (additive genetic variability, VA) and the variability that results from one allele being dominant over another (dominance variability, V D). Therefore VG = VA + V D. Heritability can be expressed as either broad-sense or narrow-sense heritability: ●●

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Broad-sense heritability is VG /V P = VG / (VG+V E), the proportion of phenotypic variation that is genetic. Narrow-sense heritability quantifies only the additive genetic variation and is therefore VA /V P = VA /(VA+V D+V E). Narrow-sense heritability can also be quantified as the proportion of total variability in offspring that can be explained by the variability in the parents in a statistical analysis.

Heritability calculations assume that parental and offspring environments are uncorrelated; if they are correlated, environmental effect can be mistaken for genetic inheritance. Researchers can sometimes avoid this problem experimentally. They can, for example, switch eggs among bird nests, with the result that the offspring of each parent experiences each of the nest environments. This is what Peter and Rosemary Grant did to establish heritability for beak traits in populations of Darwin’s finches on the Galápagos Islands. This cannot, however, be done in all experimental systems. Heritability is a measure of genetic variation among members of a population; it is not the same as inheritance. If there is only one allele for a locus in the entire population, and that allele has a strong effect on a trait, then the trait is very strongly inherited but has a heritability of zero. Heritability is not a fixed number for a population, since it depends upon the amount of plasticity. Consider a genetic disease that is caused by a single allele and that is invariably fatal; the heritability would be 100 percent. But as soon as a medicine is discovered that cures the disease, the heritability drops to 0 percent. Proteins. Another approach is to measure the variability of proteins. Differences among proteins can be very important, as enzyme proteins control all the chemical reactions in an organism. Different forms of the same enzyme, determined by different alleles at the same locus, are called allozymes. An individual that is homozygous for one of the alleles of the gene that encodes this protein will produce

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first entry just one allozyme; an individual heterozygous for this gene can produce two allozymes; the individuals in the population can collectively produce more than two allozymes. However, two allozymes, while they differ in structure, may not differ in function. That is, they may have exactly the same effect on the phenotype of the organism and on its ability to survive and reproduce. Therefore, the study of allozymes may reveal greater variability than the study of phenotypic traits. Proteins can be separated from one another by electrophoresis. A mixture of proteins is placed at one end of a gelatinlike sheet (usually composed of the complex sugar agarose). An electric current creates positive and negative poles on this sheet. Proteins, which have a slight negative charge, diffuse through the molecules of the gel toward the positive pole. Because they must diffuse through an obstacle course of agarose molecules, the smaller proteins move faster than the larger proteins. Therefore, electrophoresis separates proteins on the basis of size as well as of charge. If a type of protein from an individual is placed on a gel, the protein will show up as a band, after the appropriate staining is used to make it visible. If the individual is homozygous for that allozyme, one band shows up; an individual heterozygous (producing two allozymes) will have two bands. Electrophoresis was first used to study the protein variability of populations by geneticists Richard Lewontin and John Hubby in the 1960s. DNA. Another approach is to measure the variability of the DNA itself. Measuring the overall variability of the DNA itself would seem to be an ideal quantification of genetic variability. However, since most of the DNA in a eukaryotic cell is noncoding DNA, a measure of overall DNA variability may be meaningless as an indicator of how much evolution may be possible in that population. Even measuring the variability in the DNA of a specified gene may not be very meaningful, as much of this variability may not produce differences in proteins. However, differences between populations, or differences between species, in their DNA (whether it codes for proteins or not) is routinely used as a measure of how much evolutionary divergence has occurred between them. Measurements of genetic variability can be used to reconstruct population and species history. For example, biologists took blood samples from 20 birds representing six of the 13 species of Darwin’s finches on the Galápagos Islands. They measured the number of alleles in these 20 birds for a single locus, for the MHC II B class 1 gene. In 20 birds, there can be at most 40 alleles. These birds had 21 alleles. Because the rate at which this gene mutates

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population genetics 433 has been estimated, the researchers concluded that the common ancestor of all these birds lived at least 10 million years ago. But the islands are not that old. the original immigrant fi nches may have lived on one of the islands that has eroded away and migrated to their current locations. Furthermore, for the fi nches on the Galápagos islands to have this much genetic variability, the original population would have had to contain at least 40 genetically distinct individual birds.

GENETIC ChaNGES IN populaTIoNS to determine whether or not natural selection is occurring in a population, biologists need to determine what the frequency of each allele (for a given locus) would be in the absence of natural selection, that is, if the population was at equilibrium rather than being influenced by natural selection. consider a simple example in a species of animal, such as a kind of fish, that has external fertilization and in which a certain locus has just two alleles, A and a. Of the sperm and eggs released into the water by the fish in this population, 40 percent carry allele A, while 60 percent of the sperm and eggs carry allele a. the frequency of allele A is p = 0.4, and the frequency of allele a is q = 0.6. Because there are only two alleles, p + q = 1. if the eggs and the sperm come together randomly, you would expect the following results (see figure): 1. Because 40 percent of the eggs and 40 percent of the sperm carry allele A, there is a 40% × 40% = p2 = 16% chance that the zygote will have the homozygous AA genotype. 2. Because 60 percent of the eggs and 60 percent of the sperm carry allele a, there is a 60% × 60% = q2 = 36% chance that the zygote will have the homozygous aa genotype. 3. there is a 40% × 60% = pq = 24% chance that a sperm carrying allele a will meet an egg carrying allele A; there is also a 24 percent chance that the opposite will happen: a sperm carrying allele A will meet an egg carrying allele a. there is therefore a 24% + 24% = 2pq = 48% chance that the zygote will have the homozygous Aa genotype. 4. all of the zygotes will have one of the three genotypes

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AA, Aa, or aa. therefore p2 + 2pq + q2 = 16% + 48% + 36% = 100%. in a population that is at equilibrium, one would expect these results simply due to genetic recombination: 16% AA, 48% Aa, and 36% aa. this principle was first explained by G. H. Hardy, a mathematician, and W. Weinberg, a biologist, and is therefore called the Hardy-Weinberg equilibrium. if the population differs from this pattern, the departure from equilibrium could be caused by a number of possibilities: 1. the population may not be very large. Random departures from equilibrium can occur in small populations. this is called genetic drift. 2. the mixture of gametes may not be occurring randomly among individuals in the population. this could be caused by nonrandom mating patterns, in which individuals within the population prefer to mate with one genotype more than with another. 3. Mutations have occurred. 4. Migration (of one genotype more than another) has occurred into or out of the population. 5. natural selection has occurred. in this last possibility, one of the alleles may be less frequent than its equilibrium value because

If allele A is present in 40 percent of the gametes (eggs and sperm) of a population and allele a is in 60 percent of the gametes, the resulting frequencies of the organisms under conditions of Hardy-Weinberg equilibrium will be 16 percent AA, 48 percent Aa, and 36 percent aa.

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­ atural selection has “selected against” individuals n that carry this allele. The Hardy-Weinberg equilibrium is the background against which natural selection, defined as changes in allele frequencies in a population, might be detected. If natural selection operates against an allele, the allele will become less common in the population. Strong selection against a dominant allele (an allele whose presence always shows up in the phenotype) may quickly eliminate that allele. (This rarely occurs, because an allele that produces an inferior phenotypic trait would probably never have become dominant in the first place.) Strong selection against a recessive allele (such as a lethal mutation), however, may never eliminate the allele from the population. This is because the recessive allele can hide in the heterozygotes; the heterozygotes are therefore carriers of this allele. A lethal recessive will decline in frequency according to this formula: q0 qn = — 1 + nq 0 in which q is the frequency of the lethal recessive allele, q 0 is the initial frequency of the allele, and qn is the frequency after n generations. Starting with a frequency of 25 percent, the allele will decline to a frequency of 8 percent after eight generations. Even after a hundred generations, the frequency of this recessive allele will still be just under 1 percent. When the allele is at very low frequency, it may be lost from the population by random events such as genetic drift. Sometimes, a recessive allele might be lethal in the homozygous form, but might actually confer a survival or reproductive advantage in the heterozygous form. This can lead to a balanced polymorphism that maintains both alleles because the balance between advantage and disadvantage can cause more than one form of the allele (a polymorphism) to be maintained in the population. The most famous example is sickle-cell anemia in humans, which is caused by a recessive mutation in one of the hemoglobin genes. The mutation causes anemia, because the blood cells that have this hemoglobin are sickle-shaped and are destroyed. However, the malaria parasite cannot reproduce in these blood cells. Therefore, in regions (usually central Africa) where malaria is common, people who are homozygous for the mutant die from anemia, but people who are homozygous for normal hemoglobin often die of malaria. People who are heterozygous for the mutation strike a balance between anemia and malaria, avoiding malaria and having relatively mild anemia. Natural selection therefore favors this mutation, because there are many more

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heterozygous people than homozygous recessive people. Another possible example of a balanced polymorphism involves cystic fibrosis. Individuals homozygous for this mutation usually die at a young age; the carriers of the mutation, however, are largely unaffected. Population geneticists have been puzzled as to why this mutation is so common in certain (often northern European) populations. They concluded that there must be a heterozygote advantage, and it probably is connected with resistance to certain diseases.

Why Do Populations Have So Much Variability? When natural selection began to gain popularity as the mechanism of evolution, geneticists were attracted to the idea that natural selection maintained this genetic variability. Diversifying selection in a heterogeneous environment would be able to do so. They considered that there had to be a good evolutionary reason why there was so much genetic variation. The reason cannot be that populations need it so that they can evolve. Natural selection can produce only those characteristics that provide a benefit to individuals, not to whole populations. The primacy of natural selection in producing and maintaining genetic variability was central to the contributions of mathematicians R. A. Fisher and J. B. S. Haldane to the modern synthesis. In contrast, geneticist Sewall Wright emphasized random events such as genetic drift in the course of evolution. With the advent of electrophoresis, it became apparent that there was a lot more genetic variability in populations than could be seen in the phenotype. Populations appeared to accumulate neutral variation—genetic variation that was neither beneficial nor harmful. Beginning in the late 1960s, the neutral theory of evolution, proposed by geneticist Moto¯ Kimura, emphasized the primacy of neutral genetic variation in populations. This offered a challenge to the selectionist arguments of Fisher and Haldane and was more consistent with the genetic drift of Wright.

Inbreeding Inbreeding occurs when close genetic relatives interbreed. Most individual organisms have a few lethal recessive mutations that originated in relatively recent ancestors. In the heterozygous state, these mutations have no effect on the phenotype. So long as the individual does not mate with another individual that carries the same mutation (that is, a close relative descended from the recent ancestor that had the mutation), the mutation will not appear in the homo-

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population genetics  435 zygous form. When two carriers interbreed, there is a one-in-four chance that the offspring will receive a double dose of the mutation and die as a result. Small populations often have reduced genetic variability. There is a greater risk that individuals in these small populations will crossbreed with another individual that carries the same lethal mutation. This is one of the principal problems with species that are close to extinction. Even if they are rescued and given a safe habitat in which to live, these species (such as the Hawaiian goose) will have poor reproductive success. The genetic variability that they lost is impossible to replace in the short run and perhaps forever. This is one of the major problems in rescuing endangered species. Inbreeding may occur in humans for cultural reasons. In isolated villages, populations are often founded by a small number of people with limited genetic variability. Most people mate with other people in their village, with the result that they often share lethal recessive mutations with their mates. One example comes from the Dominican Republic village of Salinas (population about 4,000), where about one out of every 90 girls turns into a boy when reaching puberty. This happens so frequently that the villagers have a name for it: guevedoche, or “penis at twelve.” A similar phenomenon occurs among the Sambia tribe of Papua New Guinea, where they call it kwolu-aatmwol in their native tongue or “turnim-men” in pidgin. Women have two X chromosomes, while men are XY. Gender, however, turns out to be due to more than just sex chromosomes. The guevedoche and kwolu-aatmwol boys had Y chromosomes and produced testosterone like regular boys; however, they lacked an enzyme called 5-α-reductase. The gene encoding this enzyme was defective. This enzyme changes testosterone into a related molecule (DHT) that stimulates genital development in the fetus. Therefore, during gestation and childhood, these boys had genitals that appeared female. However, at puberty, testosterone itself stimulates and maintains masculinity; therefore, at puberty, the boys developed male genitalia. All of the guevedoche boys in the Dominican Republic can trace their ancestry to one woman, Altagracia Carrasco; she was probably the person who carried the mutation. Inbreeding can also occur in religious communities that remain apart from the rest of society. Some religious sects such as the Amish have elevated levels of occasionally lethal genetic diseases.

Summary Natural populations have genetic variability. Even those species that produce offspring without sexual recombination have at least some genetic variability

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due to mutation. Genetic variability in populations can be measured on phenotypic traits or on proteins. The Hardy-Weinberg equilibrium expresses the mixture of genes that will result in the absence of natural selection. Recessive lethal mutations can be eliminated only slowly from populations; lethal mutations may be selected if they provide a benefit to heterozygotes; and lethal mutations can show up more frequently in small populations, often of endangered species, than in large populations. Inbreeding in small populations, which have less genetic variability, is one of the major problems in the survival of endangered species. See also Darwin’s finches; founder effect and genetic drift; natural selection. Further Reading Avise, John C. Population Genetics in the Wild. Washington D.C.: Smithsonian, 2002. Ayala, Francisco J. Population and Evolutionary Genetics: A Primer. Menlo Park, Calif.: Benjamin-Cummings, 1982. Bradshaw, Corey J. A., et al. “Low genetic diversity in the bottlenecked population of endangered non-native banteng in northern Australia.” Molecular Ecology 16 (2007): 2,298–3,008. Fallon, Sylvia M. “Genetic data and the listing of species under the U.S. Endangered Species Act.” Conservation Biology 21 (2007): 1,186–1,195. Freeman, Scott, and Jon C. Herron. “Mechanisms of evolutionary change.” Part 2 of Evolutionary Analysis. 4th ed. Upper Saddle River, N.J.: Pearson Prentice Hall, 2007. Ge, Song, et al. “Comparisons of genetic diversity in the endangered Adenophora lobophylla and its widespread congener, A. potaninii.” Conservation Biology 13 (1999): 509–513. Gibson, J. Phil, Stanley A. Rice, and Clare M. Stucke. “Comparison of population genetic diversity between a rare, narrowly distributed species and a common, widespread species of Alnus (Betulaceae). American Journal of Botany 95 (2008): 588–596. Godoy, José A., et al. “Phylogeography, genetic structure, and diversity in the endangered bearded vulture (Gypaetus barbatus L.) as revealed by mitochondrial DNA.” Molecular Ecology 13 (2004): 371–390. Hughes, Jennifer B., Gretchen C. Daily, and Paul R. Ehrlich. “Population diversity: Its extent and extinction.” Science 278 (1997): 689–692. Kaneko, Shingo, et al. “Genetic differentiation among populations of an oceanic island: The case of Metrosideros boninensis, an endangered endemic tree species in the Bonin Islands.” Plant Species Biology, 23 (2008): 119–128. Lawrence, Hayley A., et al. “New genetic approach to detecting individuals of rare and endangered species.” Conservation Biology 22 (2008): 1,267–1,276.

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436 predation  436 LeRoi, Armand. Mutants: On Genetic Variety and the Human Body. New York: Viking, 2003. Lewontin, Richard. The Genetic Basis of Evolutionary Change. New York: Columbia University Press, 1974. Liu, P., et al. “Ecological risk assessment using RAPD and distribution pattern of a rare and endangered species.” Chemosphere 68 (2007): 1,497–1,505. Ruder, Kate. “Genomics in Amish Country.” Genome News Network. Available online. URL: http://www. genomenewsnetwork.org/articles/2004/07/23/sids. php. Accessed August 8, 2011. Williams, Barry L. “Conservation genetics, extinction, and taxonomic status: A case history of the regal fritillary.” Conservation Biology 16 (2002): 148–157.

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predation  A predator is an organism that kills

another organism, its prey, in order to consume part or all of it. Most familiar examples of predation are of predatory animals eating other animals. However, an animal can be a predator even when it eats plants. Animals that eat and digest seeds are often considered to be “seed predators,” since the seed contains an entire embryonic plant. Plants such as the Venus flytrap can be predators upon animals. Predatory animals have evolved numerous adaptations that allow them to pursue their prey (see photograph on page 437). In general, predators have the swiftest movement, sharpest eyesight, and most intelligence in the animal kingdom. Not only do predators have keen eyesight, but their brains allow them to instantly recognize the movement of prey distinct from the movement of, for example, leaves in the wind. Nocturnal predators have particularly keen senses. Some populations of predators, such as wolves, work together in packs to locate and capture prey.

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Coevolution of Predators and Prey Prey species have numerous defenses against predators. Examples include the following: ●● ●●

Some prey species have camouflage. They may have coloring that resembles the leaves, stems, litter, or rocks of their environment. For example, a certain species of insect in Madagascar is bright red and forms clusters on branches, thereby resembling flowers and escaping the notice of predators. Prey may hide themselves not only visually but by olfactory means as well. Some California ground squirrels have been observed to chew on rattlesnake skins and smear the scent on their fur, which masks their own scent from predators.

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In contrast, some prey animals have colors that make them very conspicuous to predators. Rather than making them likely targets for predation, such coloration protects them, because this warning coloration announces the fact that the prey is poisonous. Poisonous frogs, unlike other frogs, are brightly colored and are active during the day rather than the night. Warning coloration usually evolves in poisonous prey, because the poison confers no benefit on the prey if the ignorant predator eats it and discovers too late that it is poisonous. The adult monarch butterfly retains the poisons that it consumed from milkweeds when it was a caterpillar. It has orange and black warning coloration. The prey may use a startle display to temporarily confuse the predator while they escape. Some insects have large eyespots on their bodies that can briefly make them appear to be a large animal. Some prey produce chemicals that irritate or even endanger predators. Skunks are notorious for this defense. Many amphibians are famous for having poisons in their skins. The only poisonous bird (Pitohni dichrous) has the same kind of toxin in its feathers as do certain poisonous frogs. Whip scorpions produce a spray that contains oily caprylic acid that penetrates the skin or exoskeleton of a predator and watery acetic acid that burns it. An insect known as the devil’s rider walking stick sprays streams of terpenes at its attackers. Some millipedes produce progesterones, which reduce the fertility of vertebrates that eat them. Some prey animals have structural defenses such as the quills of the porcupine or the poison glands of the zebra fish. Certain lizards have tails that detach when a predator grabs them by the tail. Some animals such as the hippopotamus and the elephant are safe from predation because of their large size. Large size may have evolved in these species because the larger individuals in the populations were more resistant to attack by predators. Prey animals may even individually attack predators, if they can outmaneuver them. It is a common sight to see small birds attacking crows and hawks by diving on them from above. Some prey animals are protected by large numbers. Prey animals are often found in large single-species groups such as schools

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Ospreys (Pandion haliaetus) prey upon fish in North America.  (Dunedin Osprey Cam)

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of fish or herds of grazing animals. A lion is less likely to attack a whole group of wildebeest than an isolated individual. Some herds have sentries that watch for predators and sound an alarm if one is sighted. Flocks of birds make rapid coordinated movements that may startle the predator. When a large number of prey animals is born in one year, the predators cannot possibly eat all of them; this predator satiation allows many of the prey to survive. The 17-year cicada hatches in massive numbers every 17 years; because 17 is a prime number, predator population cycles have not adjusted to the time of emergence of this prey. Though, in general, prey animals have less intelligence than predators, they still have adaptations that allow them to detect the presence of predators and react quickly. They, too, have eyes and brains that allow them to recognize the movement of a predator against a background of leaves in the wind.

Some researchers have even suggested that migration is a prey adaptation to escape from predators. They suggest that some birds fly all the way up into the Arctic during the summer because there are fewer predators to disturb their nests. Perhaps the most important adaptation that prey species have is reproduction. Prey animals are notorious for producing large numbers of small offspring, most of which die by predation and by many other means. Prey animals also reproduce at a young age, often in their first year of life. In the

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presence of predators, natural selection favors a life history of early and abundant reproduction. In the absence of predators, these same animals may have later reproduction and produce fewer, larger offspring. A population of opossums (Didelphus virginiana) became isolated on an island off the coast of eastern North America, without predators. These opossums lived longer and reproduced when older, compared to mainland populations of opossums susceptible to predator attack. On the island of Trinidad, most freshwater pools contain guppies (Poecilia reticulata). In some of these pools, there are also predatory fishes; in other pools, the predators are absent. The guppies that live in pools without predators live longer and reproduce when they are older. The old and young prey animals, along with any that are inferior in their defenses, are most often caught by predators. In this way, predators unintentionally help to maintain the health of the prey population. This results in natural selection for prey that defend themselves well against predators as well as for predators that successfully catch prey. In some cases, both predators and prey have evolved tricks that maximize their success. These adaptations are called mimicry because one species has characteristics or behavior patterns that resemble (mimic) those of another species. Examples include the following: ●●

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The angler fish attracts smaller fish with an extension from its head that resembles a worm. One species of spider eats female moths and then uses their scent to attract male moths. Certain spiders can enter ants’ nests with impunity because they can imitate the touch responses and the chemical signals that the ants use to recognize the other members of their own colony. Sometimes the prey species has warning coloration, even though it is not poisonous. The viceroy butterfly, for instance, looks very much like the poisonous monarch butterfly; even though it is not poisonous, most predatory birds avoid eating it.

Adaptations such as camouflage and mimicry do not need to be perfect in order to be favored by natural selection. Natural selection has produced some adaptations that appear almost perfect to human observers—for example, a stick-insect that really looks like a stick. However, even an adaptation that only partially camouflages an animal, or gives it only a partial mimicry of another species, can be

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438 predation  438 favored by natural selection. Camouflage and mimicry that appear unconvincing to a human observer may be perfectly convincing to a predatory insect with a small brain or to a predator with imperfect eyesight or under conditions of limited visibility (such as dusk). Plants and even fungi can be predators: ●●

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The leaf of the Venus flytrap closes around an insect when its movement triggers tiny hairs on the leaf; once the insect is inside, the leaf secretes digestive enzymes. In the pitcher plant, insects fall into a pool of water and digestive enzymes and cannot escape, partly because hairs inside of the pitcher point downward. In the sundew plant, insects adhere to the sticky hairs on the leaves, where enzymes digest them. There is even a fungus (Arthrobotrys oligospora) that captures and consumes nematodes.

Carnivorous plants live in bogs, in which the plants have access to very few mineral nutrients. The plants make their own energy compounds by photosynthesis, and they use the insects solely as a source of fertilizer, especially nitrogen compounds. Predation is a good source of high quality food. In contrast to fruits and leaves and even seeds, animals are rich in protein and fat. Most birds will feed insects to their nestlings, even if they primarily eat seeds. Even herbivores will occasionally eat meat if the opportunity presents itself; they are simply not well adapted to catch prey. Many people have seen squirrels eating roadkill, even of other squirrels. People who raise chickens know that they have to protect them from deer and even cows will eat birds that are trapped in ornithologists’ mist nets. The coevolution of predators and prey can lead to an “evolutionary arms race.” For example, some populations of newts (a type of amphibian) contain enough toxin in their skins to kill dozens of predators. This would seem to be an excessive expenditure. But they are not defending themselves against predators in general but against garter snakes. Some garter snakes produce a large amount of enzyme that detoxifies the newt’s defensive chemical. The more poisonous the newts become, the better the snakes become at detoxifying them, in a spiral of coevolution. There is a price to pay. The garter snakes that can detoxify the newts are more sluggish than other garter snakes. In some cases, a predator can use the prey’s defensive chemicals to defend itself. The snake Rhabdophis tigrinus consumes venomous toads but uses the toad’s toxin to make its own skin poisonous.

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first entry

Predation and Populations Predation plays an immensely important role in controlling prey populations. The number of insects eaten by birds and bats is virtually incalculable. The extinction of a top predator (which is an example of a keystone species) can result in a prey population explosion. Some conservationists claim that the hunting of wolves and mountain lions has resulted in explosions of deer populations in the mountains of western North America, although this interpretation remains controversial. Perhaps the most famous example of predators affecting populations of prey is the story of the Canada lynx (Lynx canadensis) and the snowshoe hare (Lepus americanus). Approximately once a decade, the hare populations explode. A few years later, the lynx populations also increase, in response to the increased availability of their food. The hare population then declines. The lynx populations also decline, in response to a lack of food. These cycles of explosion and decline have been going on for many decades, according to data from companies that buy furs of both species from trappers. What is unclear is whether the predators are actually in control of the prey population cycles. Does the lynx population bring the hare population back down, or do the hares experience a population crash due to disease or because they run out of food? It is possible that the lynx are merely responding to, rather than controlling, the hare populations.

Humans As Predators The earliest members of the human lineage were gatherers with brains no larger than those of the chimpanzee relatives from which they had recently diverged. A rapid evolutionary increase in human brain size occurred at the same time as the development of stone tools and the consumption of other animals. The stone tools of early members of the human genus (such as Homo habilis and H. ergaster) were probably not used for hunting. Archaeological evidence indicates that these early members of the genus Homo were scavengers. Only later, with the development of thrusting spears by Neanderthals and of bows and arrows by early modern humans, did hunting became a major source of food. Even then, meat constituted a smaller portion of the diet than did seeds, fruits, and roots, and small animals made up most of that portion. Many evolutionary scientists believe that hunting evolved because it rewarded successful hunters with social status and therefore more mating opportunities. In regions where humans and their prey animals evolved together for thousands or millions of years, humans did not threaten most prey populations with extinction. However, in places where fully

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predation  439

In the 1870s, white Americans shot huge numbers of bison, partly in a deliberate attempt to destroy the food source of unconquered Native American tribes. In this image, a pile of bison skulls is waiting to be ground for fertilizer.  (Burton Historical Collection; Detroit Public Library)

modern humans arrived with advanced hunting technologies such as bows and arrows, prey extermination sometimes resulted. The major example is the Pleistocene extinction in North America at the end of the most recent ice age, probably caused by overhunting of prey that had not evolved the instinct to run from humans. (Recent evidence has called this theory into question.) The evidence that overhunting caused extinctions in Australia and Madagascar is better. After a few thousand years, humans in these regions developed social traditions that allowed a rough equilibrium of prey populations to develop. Even if their Pleistocene ancestors had caused mass extinctions, Native Americans were excellent managers of prey populations at the time of European contact. Before European contact, Native Americans hunted many animals (such as bison and passenger pigeons) and caught a lot of fish. European diseases decimated Native populations, often even before they came in contact with the Europeans. This may have been the reason that, during the 18th century, some of these prey animals experienced population explosions. The huge populations of bison and passenger pigeons of the 18th and 19th centuries are legendary. They were probably also unnatural. When botanist William Bartram traveled in what is now the southeastern United States in the late 18th century, he saw huge populations of fishes, and large numbers of alligators eating them. It did not occur to him, nor to virtually anyone else until recently, that this may have resulted from the plagues that depopulated Native villages.

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White American hunters proceeded to celebrate the enormous populations of prey animals by shooting as many of them as possible. Billions of passenger pigeons had darkened the skies of the eastern United States in the 19th century, but by the early 20th century, the last passenger pigeon had died in a zoo. Many white American hunters of the 19th century aspired to “shoot the last buffalo” (see photograph). The extermination of the bison was part of a deliberate, government-backed campaign to undermine the livelihood of the last Native American tribes and bring them into subjugation. This goal was achieved before the bison became extinct, and today bison populations are growing in wildlife preserves (such as Badlands National Park in South Dakota and The Nature Conservancy’s Tallgrass Nature Preserve in Oklahoma) and on private ranches.

Predators and Conservation Wildlife management developed in the 20th century as a way of making hunting sustainable, allowing it to continue without depleting prey populations. In this way, humans once again play an important role in stabilizing prey populations, because hunters are allowed only a limited number of prey, a limit that is adjusted each year. The role of hunters is now essential, since hunters in the late 19th and early 20th centuries nearly exterminated other large predators such as wolves and bears that had previously kept prey populations in check. Populations of large predators are now recovering, in some cases after the deliberate reintroduction of animals from zoos (in the case of European bears) or from other areas in which the animals were still numerous (as in the case of wolves in the Rocky Mountains). These large predators normally stay away from livestock, due to a fear of humans, but not always, and ranchers often oppose the return of wild predators. Because of the “ten percent law” of the transfer of energy and matter through the food chain, predator populations tend to be smaller than prey populations. Herbivorous prey animals consume food that does not move, but predators often need to search a large area for their prey. For both of these reasons, it is often the critical area for a viable predator population that determines the area of a nature preserve. Because their populations grow relatively slowly, predator species are often the most vulnerable to environmental disruptions. Because predators are at the top of the food chain, they are the most frequent victims of the biomagnification of toxic materials. Together with the primordial human reverence for predators, these reasons make predators the “poster children” of many conservation campaigns. It is not without reason that conservationists believe that the health of a predator

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440 predation  440 population is a good indicator of the health of the entire ecosystem of which it is a part. See also biomagnification; camouflage and mimicry; carnivorous plants; coevolution; conservation biology; ecosystems; keystone species; life history, diversity of; Pleistocene extinction. Further Reading Austad, Steven N. “Retarded senescence in an insular population of Virginia opossums (Didelphus virginiana).” Journal of Zoology 229 (1993): 697–708. Barbosa, Pedro, and Ignacio Castellanos, eds. Ecology of Predator-Prey Interactions. New York: Oxford University Press, 2005. Brodie, Edmund D., Jr., et al. “The evolutionary response of predators to dangerous prey: Hotspots and coldspots in the geographic mosaic of coevolution between garter snakes and newts.’ Evolution 56 (2002): 2,067–2,082. Brodie, Edmund D., III, et al. “Parallel arms races between garter snakes and newts involving tetrodotoxin resistance as the phenotypic interface of evolution.” Journal of Chemical Ecology 31 (2005): 343–356. Brodie, Edmund D., III, and Edmund D. Brodie, Jr. “Evolutionary response of predators to dangerous prey: reduction of toxicity of newts and resistance of garter snakes in island populations.” Evolution 45 (1991): 221–224. ———. “Predator-prey arms races.” Bioscience 49 (1999): 557–568. Carlson, S. M., et al. “Does variation in selection imposed by bears drive divergence among populations in the size and shape of sockeye salmon?” Evolution 63 (2009): 1,244–1,261. ———, et al. “Predation by bears drives senescence in natural populations of salmon. Public Library of Science ONE 2 (2007): e1,286. Corcoran, Aaron J., et al. “Tiger moth jams bat sonar.” Science 325 (2009): 325–327. Dicke, Marcel, and Paul Grostal. “Chemical detection of natural enemies by arthropods: An ecological perspective.” Annual Review of Ecology and Systematics 32 (2001): 1–23. Eisner, Thomas E. “Beetle’s spray discourages predators.” Natural History 75 (1966): 42–47. Feldman, C. R., et al. “The evolutionary origins of beneficial alleles during the repeated adaptation of garter snakes to deadly prey.” Proceedings of the National Academy of Sciences USA 106 (2009): 13,415–13,420. Genovart, M., et al. “The young, the weak, and the sick: Evidence of natural selection by predation.” Public Library of Science ONE 5 (2010): e9,774. Godeau, J.-F., et al. “Reaction of ants to, and feeding biology of, a congeneric myrmecophilous and non-

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first entry myrmecophilous ladybird.” Journal of Insect Behavior 22 (2009): 173–185. Gosler, A. G., et al. “Predation risk and the cost of being fat.” Nature 377 (1995): 621–623. Kenward, R. E. “Hawks and doves: Factors affecting success and selection in goshawk attacks on woodpigeons.” Journal of Animal Ecology 47 (1978): 449–460. McKinnon, L., et al. “Lower predation risk for migratory birds at high latitudes.” Science 327 (2010): 326–327. Summarized by Gilg, Olivier, and Nigel G. Yoccoz. “Explaining bird migration.” Science 327 (2010): 276–277. Møller, Anders Pape, and J. Erritzøe. “Predation against birds with low immunocompetence.” Oecologia 122 (2000): 500–504. Neves, R., et al. “Does a shell matter for defence? Chemical deterrence in two cephalaspidean gastropods with calcified shells.” Journal of Molluscan Studies 75 (2009): 127. Nilsen, Erlend B. “A slow life in hell or a fast life in heaven: Demographic analyses of contrasting roe deer populations.” Journal of Animal Ecology 78 (2009): 585–594. Nordbring-Hertz, Birgit, and Bo Mattiasson. “Action of a nematode-trapping fungus shows lectin-mediated host-microorganism interaction.” Nature 281 (1979): 477–479. Osborn, Karen J., et al. “Deep-sea, swimming worms with luminescent ‘bombs.’ ” Science 325 (2009): 964. Pafilis, Panayiotis, et al. “Tail shedding in island lizards (Lacertidae, Reptilia): Decline of antipredator defenses in relaxed predation environments.” Evolution 63 (2009): 1,262–1,278. Penteriani, V., et al. “Owls and rabbits: Predation against substandard individuals of an easy prey.” Journal of Avian Biology 39 (2008): 215–221. Reznick, David, and John A. Endler. “The impact of predation on life history evolution in Trinidadian guppies (Poecilia reticulata).” Evolution 36 (1982): 160–177. Servedio, M. R. “The effects of predator learning, forgetting, and recognition errors on the evolution of warning coloration.” Evolution 54 (2000): 751–763. Sih, Andrew. “Evolution, predator avoidance, and unsuccessful predation.” American Naturalist 125 (1985): 153–157. Stanford, Craig B. Chimpanzee and Red Colobus: The Ecology of Predator and Prey. Cambridge, Mass.: Harvard University Press, 1998. Stenseth, Nils C., et al. “Population regulation in snowshoe hare and Canadian lynx: Asymmetric food web configurations between hare and lynx.” Proceedings of the National Academy of Sciences USA 94 (1997): 5,147–5,152. Stolzenburg, William. Where the Wild Things Were: Life, Death, and Ecological Wreckage in a Land of Vanishing Predators. New York: Bloomsbury, 2008.

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primates  441 Svensson, E. I., and M. Friburg. “Selective predation on wing morphology in sympatric damselflies.” American Naturalist 170 (2007): 101–112. Williams, Becky L., et al. “A resistant predator and its toxic prey: Persistence of newt toxin leads to poisonous (not venomous) snakes.” Journal of Chemical Ecology 30 (2004): 1,901–1,919. Young, Kevin V., et al. “How the horned lizard got its horns.” Science 304 (2004): 65.

primates  Primates constitute the class of mammals that includes lemurs, monkeys, and apes. Humans are apes, therefore primates. The term primate, used by scientists since the time of Carolus Linnaeus, suggests that this group, which includes humans, is the most important among mammalian classes. While scientists no longer rank classes by their importance relative to humanity, the term primate continues in use. Biologists classify primates into approximately 230 living species of prosimians, tarsiers, and anthropoids (see figure on page 442). Primates, in general, share these characteristics: ●● ●●

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They have the largest brains among mammals, after adjustment for body size. They often live in large, complex social groups. Large brains aid survival but are considered to be most important for social interactions. They take a longer time to reach maturity than most other mammals, a characteristic related to the evolution of intelligence.

The first primates lived in trees, and most still do, except for a few groups such as baboons and humans that have (independently from one another) evolved the ability to live on the ground. This adaptation is complete enough that in humans, uniquely among primates, the lower limbs (legs) are relatively long. Some, like galagos, have remarkable leaping abilities: Though less than a foot and a half (50 cm) in length, galagos can leap more than six feet (2 meters). Leaping from branch to branch in trees has encouraged the evolution of important characteristics that primates possess more than most other mammals: ●●

The ability to grasp. This results primarily from an opposable thumb, which is rare in other mammals. Primates not only have the ability to grasp branches in trees, but the juvenile primates can efficiently cling to the fur of their mothers. Most primates also have opposable big toes, although primates

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that have evolved a ground-based existence have lost this characteristic. Nonhuman apes have opposable big toes; humans do not; the australopithecines (human ancestors) had big toes that were intermediate in their adaptation for grasping branches. Excellent vision. Nocturnal primates have big eyes. For example, each of the tarsier’s eyes is larger than its brain. Diurnal primates have inherited big eyes from nocturnal ancestors. Visual acuity is important not only for night vision, but for jumping around in trees. For prosimians, smell remains an important sense, while most anthropoids rely primarily on vision. Depth perception. Primates have both eyes on the front of the face, a characteristic most people notice immediately in all primates. This allows binocular vision and depth perception, which allows primates to grasp branches while leaping. Color vision. While not the only mammals with color vision, primates (primarily anthropoids) benefit from color vision because it allows some primates to recognize ripe fruits in colors such as red against a background of green leaves, in the absence of a well-developed sense of smell.

Prosimians  are the more primitive group of primates and are generally smaller than anthropoids. Most prosimians are lemurs that live in Madagascar, but others live on the African continent and in southeast Asia. Lemurs range in size from the pygmy mouse lemur (weighing about an ounce, or 30 g) to the indri (weighing about 20 pounds, or 9 kg). Some lemurs are diurnal, others nocturnal. Galagos and lorises live on the African continent; lorises also live in India and Southeast Asia. Many zoologists classify prosimians into the subclass Strepsorhini. Tarsiers (see photograph on page 443) are small, nocturnal primates that live in Southeast Asia. Though they look to many people very similar to the prosimians, they share some features with the anthropoids, such as skull characteristics, and big hands and feet. Many zoologists classify tarsiers together with anthropoids into the subclass Haplorhini. Anthropoids (monkeys and apes) have the largest brains among primates and include two families of New World monkeys, found in the tropical rain forests of Central and South America, as well the Old World monkeys, the lesser apes, and the great apes, all of which originated in Africa or Asia. Most monkeys and apes have longer arms than do

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442 primates 442

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smaller thumbs (spider monkeys have none at all) than Old World monkeys and apes. the marmosets and tamarins of South america differ from other new World monkeys in having only two, rather than three, molars and are classified separately. the Old World monkeys and the apes are catarrhines, so named because their nostrils are narrow and face downward. Old world monkeys live primarily in trees, except baboons, but spend part of their time on the ground. they are much less likely to have long tails, and these tails are not prehensile. their rump skin pads help them sit on the ground but are also useful in sexual signaling: colors indicate species and estrus, which is the female readiness for mating. the colobine subfamily of Old World monkeys includes the langurs of asia and the colobus monkeys of africa. they have relatively longer legs, tails, and thumbs than other Old World monkeys. although they eat a variety of foods, their large multichambered stomachs allow the digestion of leaf material. a diet of leaves, most of which are toxic, requires the assistance of microbes in mammals such as the colobus monkey, the cow, and the marsupial koala; even the marine iguanas of the Galápagos islands, which live on seaweed, require microbial symbionts. the cercopithecine subfamily of Old World monkeys includes the macaques of africa and asia (some extend their range a little bit into europe) and the baboons and mangabeys of africa. cercopithecines have less complex stomachs and eat less leaf material. the Japanese macaque monkeys live farther north than any other nonhuman primate. their intelligence and cultural propagation of knowledge has been studied as a model for the evolution of intelligence. Apes have no tails and have larger brains than other anthropoids. apes have at least a limited ability to walk on two legs (bipedalism). Lesser apes include the gibbons and siamangs of Southeast asia, which have extremely long arms with which they brachiate. “lesser” refers to the smaller size of these apes than the great apes. lesser apes, unusual among animals, have a lifelong monogA commonly accepted classification system (which does not include all the families) amous mating system. Great

prosimians, which allow them to not merely jump around in trees but to swing from branches, a unique kind of locomotion called brachiation. Most anthropoids are diurnal. Most have highly developed social patterns, which may be the principal reason for their braininess. For example, when howler monkeys of the amazon recognize a threat (for instance, in the form of a human intruder), they may form into a circle in the branches over the intruder’s head, and it is time for the human to leave. new World monkeys have evolved separately from other primates for at least 20 million years, largely as a result of the separation of the african and South american continents. all live in trees. their nostrils are flat and face sideways, which is why they are called platyrrhines (flat-nosed). the most noticeable distinction is that they have long prehensile tails that have muscles and even fi ngerprint skin that allows these monkeys to grasp branches with their tails. new World monkeys have

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primates  443

The Philippine tarsier (Tarsius syrichta), about five inches (13 cm) long, is one of the smallest primates.  (Roland Birkle)

apes (family Hominidae; the hominids) include the orangutans of Southeast Asia as well as the gorilla, chimpanzee, bonobo, and humans that originated in Africa. Because great apes do not have rump pads, they generally build nests in trees or on the ground for sleeping. With males weighing as much as 160 pounds (about 80 kg), the orangutans of Borneo and Sumatra are the largest arboreal primates. Orangutans are the least social of apes. They forage separately for fruit. Males and females interact only to mate, and the only social bond among orangutans is between mother and infants. With males weighing as much as 350 pounds (about 180 kg), the gorillas are the largest primates (see photograph on page 444). The three subspecies of gorillas (the mountain gorilla and the eastern and western lowland gorillas) live in the rain forests of central Africa in small groups that eat plant materials. In both orangutans and gorillas, males weigh about twice as much as females, which is characteristic of the harem. On at least two occasions, gorillas have been observed to use wooden tools. The apes commonly called chimpanzees consist of two species: the true chimpanzees (Pan troglodytes) and the pygmy chimpanzee or bonobo (Pan paniscus). True chimps range from dry woodlands to rain forests throughout central Africa; pygmy chimps live in a small area south of the Congo River. They eat a wide variety of foods, including leaves, fruits, seeds, insects, and occasionally red meat. They spend part of their time in trees and part on the ground (bonobos less than true chimps). Chimps exhibit behaviors that scientists once thought were found only in humans, such as the use of tools (although they do not fashion stones into tools) and warfare. Most of these

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behaviors were revealed only when researchers such as Jane Goodall spent long periods of time with chimp societies. True chimps are very aggressive, in contrast to bonobos, who live in small bands and engage in frequent, humanlike copulation. As primatologist Frans DeWaal says, “The chimpanzee resolves sexual issues with power; the bonobo resolves power issues with sex.” Humans share a common ancestor with chimps and bonobos that lived only about 5 million years ago. Primates similar to today’s prosimians evolved shortly after the Cretaceous extinction that wiped out the dinosaurs and other large reptiles. Some other highly specialized orders of mammals, such as bats and whales, also evolved in the Paleocene epoch of the Cenozoic period. When dinosaurs were no longer the dominant land animals, mammalian evolution exploded in diversity. One of the earliest primates, Purgatorius, may have evolved before the end of the Cretaceous. Purgatorius, and the plesiadapiform primates that evolved during the Paleocene, lived in Europe and North America (which were still connected at that time). They resembled shrews. During the ensuing Eocene epoch, adapid and onomyid primates evolved. It is unclear which of these groups may have been the ancestors of monkeys and apes. Both groups of Eocene primates had larger brains, shorter faces, and a better ability to grasp than Paleocene primates and relied on sight more than smell. The first true monkeys evolved during the ensuing Oligocene epoch in the Old World. Oligocene primates from what is now the Fayyum deposit in Egypt (such as Proconsul) may represent the first true apes. Sometime after 7 million years ago, perhaps associated with the spread of drier conditions across Africa, the human evolutionary lineage (now usually called the hominins) separated from the chimpanzee lineages. The earliest distinctive characteristic of the hominins was upright posture and walking on two legs, although numerous distinguishing features (such as very large brains, fashioning stones into tools, use of fire, use of language) arose later in the hominin line. The earliest known hominins were Orrorin and Sahelanthropus from west Africa and Australopithecus primarily from east Africa. Many australopithecines (and related hominins such as Kenyanthropus) are known from the period between 5 and 2 million years ago in east Africa. The plenitude of fossil information reveals a complex bush of hominin lineages, rather than a clear line of human ancestry. About the only thing regarding human ancestry of which anthropologists are certain is that the robust australopithecines (genus Paranthropus) did not lead to modern humans. From one of the gracile australopithecines,

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444 primates  444

first entry also endangered by predation by humans as “bushmeat” and for traditional medicine. Only a few hundred mountain gorillas survive, in the Virunga Mountains of east Africa. Because of their restricted habitats, they are vulnerable to natural disasters from which they could easily recover if they still had their original ranges. Drought and forest fires in 1997–98 resulted in the deaths of many orangutans (Pongo pygmaeus) in Borneo, either directly, or by reducing their habitat, or because villagers shot them as they fled from the fires. Their populations decreased from 23,000 before the fires to 15,400 after. There is good reason why saving primates is a high conservation priority. See also mammals. Further Reading

Like humans, gorillas are apes and provide extensive care to their offspring.  (NOAA/Department of Commerce)

either known or yet to be discovered, the genus Homo evolved about 2 million years ago in east Africa. Today, Homo sapiens is the only surviving species of hominin. The fact that humans are primates means that the physiology of the other primates most nearly resembles that of humans. It is for this reason that primates, especially monkeys and (even better) chimps, are favored for medical experimentation. For example, primates are the best subjects to use to study the transmission of viral diseases such as Ebola, which apparently emerged from primate populations, and to try out malaria vaccines. Some primates have simian immune deficiency viruses (SIV), similar to human immune deficiency viruses (HIV), and experimentation on monkeys and apes may allow researchers to find out how other primates prevent spread of the virus in their bodies. Primates can have or be induced to have human neurodegenerative diseases such as Parkinson’s and Alzheimer’s diseases. Because primate brains are the most similar to humans, the study of their brain functions may help medical researchers understand appetite, aggression, depression, and anxiety. Because monkeys and nonhuman apes have large brains and complex behavior, they may also experience such experimentation as cruelty, more so than other laboratory animals such as mice, rats, and dogs. For both reasons, medical experimentation upon primates has become particularly controversial. Most nonhuman primates survive in remote areas away from human contact, and a large proportion of them are endangered. Most primates are endangered from habitat destruction, but they are

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Beck, B., et al., eds. Great Apes and Humans: The Ethics of Coexistence. Washington, D.C.: Smithsonian Institute Press, 2001. Brashares, J. S., et al. “Bushmeat hunting, wildlife declines, and fish supply in West Africa.” Science 306 (2004): 1,180–1,183. Calvin, William H. A Brain for All Seasons: Human Evolution and Abrupt Climate Change. Chicago: University of Chicago Press, 2002. De Waal, Frans B. M. My Family Album: Thirty Years of Primate Photography. Berkeley: University of California, 2003. Hart, Donna L., and Robert W. Sussman. Man the Hunted: Primates, Predators, and Human Evolution. New York: Westview, 2005. Johanson, Donald, Lenora Johanson, and Blake Edgar. Ancestors: In Search of Human Origins. New York: Villard, 1994. Kalpers, J., et al. “Gorillas in the crossfire: Population dynamics of the Virunga mountain gorillas over the past three decades.” Oryx 37 (2003): 326–337. Keele, B. F., et al. “Chimpanzee reservoirs of pandemic and nonpandemic HIV-1. Science 313 (2006): 523–526. Leakey, Richard, and Roger Lewin. Origins Reconsidered: In Search of What Makes Us Human. New York: Doubleday, 1992. Pennisi, Elizabeth. “Genomicists tackle the primate tree.” Science 316 (2007): 218–221. Primate Photo Gallery. “Primate Photo Gallery: Chimpanzees, gorillas, orang-utans, monkeys, and apes.” Available online. URL: http://www.primates.com. Accessed August 3, 2010. Rowe, Noel. The Pictorial Guide to the Living Primates. East Hampton, N.Y.: Pogonias Press, 1996. ———. “Primate Conservation, Inc.” Available online. URL: http://www.primate.org. Accessed August 8, 2011. Rumbaugh, Duane M., and David A. Washburn. Intelligent Apes and Other Rational Beings. New Haven, Conn.: Yale University Press, 2003.

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protists  445 Sapolsky, Robert M. A Primate’s Memoir: A Neuroscientist’s Unconventional Life among the Baboons. New York: Simon and Schuster, 2001. Seiffert, Erik R. “Basal anthropoids from Egypt and the antiquity of Africa’s higher primate radiation.” Science 310 (2005): 300–304. Stewart, Caro-Beth, and Todd R. Disotell. “Primate evolution—in and out of Africa.” Current Biology 8 (1998): R582–R588. Stringer, Chris, and Peter Andrews. The Complete World of Human Evolution. London: Thames and Hudson, 2005. Tattersall, Ian, and Jeffrey Schwartz. Extinct Humans. New York: Westview, 2000. Templeton, Alan R. “Out of Africa again and again.” Nature 416 (2002): 45–51. van Schaik, C. P., et al. “Orangutan cultures and the evolution of material culture.” Science 299 (2003): 102–105. Walker, Alan, and Pat Shipman. The Ape in the Tree: An Intellectual and Natural History of Proconsul. Cambridge, Mass.: Harvard University Press, 2005. ———. The Wisdom of the Bones: In Search of Human Origins. New York: Knopf, 1996. Walsh, P. D., et al. “Catastrophic ape decline in western equatorial Africa.” Nature 422 (2003): 611–614. Winckler, Wendy, et al. “Comparison of fine-scale recombination rates in humans and chimpanzees.” Science 308 (2005): 107–111. Wood, Bernard, and M. Collard. “The human genus.” Science 284 (1999): 65–71.

protists  Protists are eukaryotic organisms that

do not produce complex tissues. Protists are generally considered to be simpler in structure than the “crown eukaryotes” (animals, plants, and fungi). Many protists are single-celled, though these single cells (such as Tetrahymena) can have very complex structures. If multicellular, they do not have highly organized tissues, although large seaweeds come pretty close to the complexity of plants, animals, and fungi. All eukaryotes appear to have evolved from a common ancestor that had a nucleus and mitochondria. According to the reconstruction used by evolutionary scientist Sandie Baldauf, eight major lineages of eukaryotes evolved. In one of the lineages, plants evolved; in another lineage, animals and fungi evolved. “Protists,” therefore, refers to all eukaryotes other than plants, animals, and fungi, making it a paraphyletic cladistic group. Kingdom Protista is therefore a conceptual category, not a distinct evolutionary group. Because they are not animals, and because seven of the eight lineages do not include animals, protists are no longer called protozoans (Greek for “original animals”).

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Major Lineages of Protists Lineage

Examples

Excavates and discicristates

Giardia, Euglena, acrasid slime molds

Heterokonts

Diatoms, brown algae, water molds

Alveolates

Ciliates, dinoflagellates, Plasmodium

Cercozoans

Foraminifers

Amoebozoans

Plasmodial slime molds

Green protists

Red algae, green algae (and plants)

Opisthokonts

Choanoflagellates (and fungi and animals)

Protists do not have adaptations for living on land, although many can survive desiccation. Protists are found in every moist region of the planet and fulfill nearly every ecological role. Some are decomposers; some are predators; some cause diseases; and some are photosynthetic. In all of these ways, they are important components of natural ecosystems. Protists are most reliably classified on the basis of DNA similarities. Such a classification results in evolutionary lineages that are difficult to define in terms of anatomy and life cycle. Perhaps the best way to understand the enormous diversity of protists is to survey the lineages (see table).

Excavate and Discicristate Protists Excavates are single-celled protists with flagella and an “excavated” feeding groove on one surface. Some excavates live in the intestines of insects. A few excavates are intestinal pathogens of animals, including humans, such as Giardia lamblia, which causes giardiasis. Giardia is one of the diplomonads, which appear to be two cells fused together: Giardia has two nuclei, each associated with four flagella, and duplicated organelles. Excavates lack mitochondria, but some of them have mitosomes and hydrogenosomes, which are vestigial remnants of mitochondria. Discicristates are also single-celled protists with flagella. Their name indicates that they have disc-shaped cristae (membranes) within their mitochondria. They often, like excavates, have a feeding groove. Examples include Euglena, which swims in water, guided by an eyespot that detects the direction of light. Euglena makes its food by photosynthesis with its large chloroplasts. The chloroplasts

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first entry

of plants and their ancestors (such as green algae) evolved from endosymbiotic cyanobacteria—that is, plant and green algae cells are “cells within cells.” In contrast, the chloroplasts of Euglena appear to have evolved from entire green algae cells, making the chloroplasts the evolutionary descendants of “cells within cells within cells,” an example of symbiogenesis. Euglena can also ingest food particles in the same manner as animal cells. Some discicristates are intestinal pathogens of animals, such as the Trypanosoma that cause sleeping sickness. The acrasid slime molds are in this lineage also. Acrasid cells are amoeba-like, which means that they flow across moist surfaces into extensions called pseudopods. They spend most of their time independently foraging for food, but under certain conditions some of them will release a hormone that causes the cells to gather together into a single amoeba-like organism that undergoes sexual reproduction and produces spores. The slime-mold life cycle has independently evolved in the amoebozoan lineage (see below). Some evolutionary scientists consider discicristates to be a lineage within the excavates.

Heterokont Protists Heterokonts (also called stramenopiles) are another major lineage of eukaryotes. Their name is Greek for “different flagella,” because their flagella have hollow, three-pointed hairs unlike the flagella of other eukaryotes. Most of them are photosynthetic “algae,” but not all algae are heterokonts—just the diatoms, golden algae, and brown algae. Their chloroplasts appear to be the evolutionary vestiges of single red algae cells (see below) that were incorporated by symbiogenesis (they are cells within cells within cells). Heterokont chloroplasts have chlorophyll a, just as do cyanobacteria and all other chloroplasts, and chlorophyll c, unique to this group. Also unique is the fucoxanthin that gives these algae their golden or brown color. Brown algae store food in the forms of laminarin, a carbohydrate, and mannitol, a kind of alcohol, rather than as starch, as do green plants. Diatoms store oil, which is lighter than water and keeps them afloat. Diatoms and golden algae are single-celled. Diatoms have shells made of silicate, the same mineral found in glass; some of these shells can be intricately sculpted. Besides being major components of the phytoplankton on which aquatic food webs depend, diatoms can accumulate at the bottoms of shallow seas. Millions of years of such accumulation, followed by compression, results in thick layers of diatomaceous Earth, an extremely light rock that can be mined as a filtration material. One such deposit is in the Purísima Hills near Lompoc, California.

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Brown algae (phaeophytes) are multicellular and mostly live in the oceans. They are the most famous big seaweeds. They can have complex structures that include: ●●

●●

●● ●● ●●

holdfasts, which look like roots but do not absorb and transport water; like the rhizoids of mosses, they anchor the organism to rocks stipes, which look like stems but do not transport water as do the true stems of plants; the tissues inside the stipes do, however, have a limited ability to transport food molecules from one part of the organism to another blades, which look like leaves pneumatocysts, which are balloonlike structures that provide buoyancy to the organism reproductive structures (see below)

Each part of the seaweed (except the holdfasts) is photosynthetic and largely on its own for nutrition. The heterokont lineage also includes the oomycetes, or “water molds.” As their name suggests, they superficially resemble fungi: They form a mycelium of strands and digest their way through organic food. They used to be classified as fungi, despite the major differences on the cellular level: Water molds have diploid nuclei, while fungi have haploid nuclei, in their mycelia; and water molds have cell walls made of cellulose, unlike the chitin cell walls of fungi. Water molds also produce flagellated spores, like other heterokonts. It eventually became clear that the oomycetes were heterokonts that had lost their chloroplasts and evolved into parasites. Water molds are one of the best examples of how appearances, without help from phylogenetic analysis, can be deceiving: They look and act like fungi but are more closely related to seaweeds. Some water molds have great economic and ecological importance, such as the following: ●●

●●

Phytophthora infestans is the “mold” that often kills whole fields of potatoes. It spread through European and American potato fields in the 19th century and in 1845 erupted in Ireland and destroyed nearly the entire crop. The Irish lived almost exclusively on potatoes, and the collapse of the potato crop resulted in the Potato Famine, in which a million Irish starved to death (despite the availability of food for those who could buy it) and another million emigrated. Phytophthora ramorum causes sudden oak death, which is killing thousands of oak trees in the Coast Ranges of California.

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protists  447 ●●

Pythium species kill seedlings of many kinds of plants, especially in greenhouses.

Some oomycetes (such as the two Phytophthora species above) are specialist parasites, while others such as Phytophthora megakarya and Pythium infect a range of hosts. P. megakarya is a parasite both of cocoa trees and of the trees in whose shade the cocoa bushes grow. Heterokonts have motile, flagellated cells at some point in their life cycle. In some species, these cells are sperm, which unite with eggs to produce zygotes, while in others they are zoospores, which grow into haploid structures. Single-celled heterokonts reproduce asexually most of the time, but occasionally they produce eggs or sperm, which unite to form a genetically different cell. Multicellular heterokonts (brown algae and oomycetes) produce antheridia (which produce sperm) and archegonia (which produce eggs). Most brown algae have a multicellular diploid phase (the sporophyte) that produces spores by meiosis. Each spore is capable of growing into a multicellular haploid phase (the gametophyte) that may be indistinguishable from the diploid phase. Male gametophytes release sperm, and female gametophytes produce eggs. Sporophytes of the genus Fucus directly produce eggs and sperm, dispensing with the gametophyte phase altogether. “Kelp forests,” such as the dense growth of Macrocystis off the coast of California, look like forests because the bulbs hold the stipes upright. The stipes can be more than 200 feet (up to 70 meters) in length. Like a forest, the kelp create a complex habitat in which many other species live. Like estuaries and seagrass beds, kelp forests are places where young fishes can grow before heading out into the ocean. Kelp forests are threatened by population explosions of sea urchins, which graze upon young kelp. Sea urchin populations are often large because human activities have reduced the numbers of predators (large fishes and sea otters) that normally consume them or their larvae. Kelp from these forests is commercially harvested by trawlers that cut off the tops of the organisms, which grow back. Alginates from kelp are used in products such as soap and ice cream. The Sargasso Sea, below the Gulf Stream in the Atlantic Ocean, is filled with brown algae of the genus Sargassum. Haptophytes are single-celled algae related to the heterokonts and produce calcium carbonate coccoliths. The white cliffs of Dover in England formed from the massive accumulation of coccoliths. Many evolutionary scientists classify the cryptomonads, which resemble single-celled brown algae, and the haptophytes into a larger group, the chromists.

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Alveolate Protists Alveolates have cavities (similar to the alveoli of lungs) underneath the membrane that can form a pellicle or form armored plates. The three major lineages of alveolates are the following: The ciliates have large numbers of cilia, which are like flagella, but shorter. They use cilia for movement, feeding, attachment, and sensation. They have two kinds of nuclei: micronuclei, which can replicate by means of accurate mitosis, and large macronuclei, composed of lots of copies of some of the genes. Macronuclei replicate less accurately and must be regenerated occasionally by micronuclei. Some ciliates, like Paramecium and Tetrahymena, are single complex cells that swim with their cilia. Others, like Stentor, attach themselves to a surface and grab food with their cilia. Large ciliates such as Didinium may ingest smaller ciliates such as Paramecium. The apicomplexans are protists that often have an apical complex, which is a degenerate complex chloroplast that no longer carries out photosynthesis. The apical complex produces enzymes that help parasitic apicomplexans to enter host cells. The most famous apicomplexans are the species of Plasmodium that cause malaria, one of the most widespread and devastating diseases in the world, by living inside of red blood cells. The dinoflagellates are covered with hard cellulose plates and have two flagella. They often have complex chloroplasts (cells within cells within cells), just as do heterokonts and the other alveolates. They swim in water and make food by photosynthesis. Some dinoflagellates do not have chloroplasts and live by consuming small food items. Dinoflagellate means “terrible flagellate,” in reference to the fact that they can be poisonous to vertebrates. Under certain conditions, such as warm weather and abundant nutrients, dinoflagellates have population explosions, forming “red tides.” Mollusks can consume large numbers of dinoflagellates without difficulty, but if vertebrates eat these mollusks, the toxins may cause nerve damage. This is why fishermen who gather shellfish traditionally avoid summer months (the months without the letter R in their name). Some blooms of neurotoxic algae are caused by diatoms, not dinoflagellates. Some dinoflagellates are the zooxanthellae that live as mutualists inside the skin of aquatic animals. These animals, which include corals, get most of their food from the zooxanthellae that live in them.

Cercozoan Protists Cercozoans are amoebae that produce long, filamentous pseudopods, with which they capture

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448 protists  448

first entry

food items, and often have hard outer shells. They include the foraminiferans and the radiolarians. “Forams” have calcium carbonate (limestone) shells that can be very complex and occasionally large—some have been reported to be almost 7 inches (19 cm) in diameter. Because of their abundance, they are major contributors to the buildup of lime sediments at the bottom of the ocean, and their shells have been abundant fossils for millions of years. The carbon isotope ratios of the limestone in fossil foram shells are one of the major sources of information about climate changes in the history of the Earth. Although they are not photosynthetic, they form mutualistic associations with photosynthetic protists such as green algae, red algae, golden algae, diatoms, and dinoflagellates. Some of them ingest algae but keep the chloroplasts alive in their tissues. Radiolarians are similar to foraminiferans, but their shells are usually composed of silicate rather than lime.

Green Protists The major lineages of green protists are the red algae and the green algae. They are the only photosynthetic eukaryotes to have simple chloroplasts— evolutionary descendants of cyanobacteria (cells within cells). The red algae (Rhodophyta) are marine seaweeds. Some of them have calcium carbonate reinforcements to their cell walls and contribute to the buildup of reefs. They have chlorophyll a and a unique chlorophyll d. Their red color comes from phycobilins. They live at greater depths in the oceans than other algae; their red color allows them to absorb blue light, which is the color that penetrates most deeply into the water. Most edible seaweeds (such as Japanese nori) are red algae. Despite their superficial resemblance to brown seaweeds, the red algae evolved separately from primordial eukaryotic ancestors and are closely related to green algae. The green algae (Chlorophyta) are considered to be the ancestors of all land plants, even though they are not the most complex algae. Many are unicellular; some of them form sheets; and others form more complex structures; but none of them rival the gigantic kelp in size or complexity. However, they have important similarities to land plants on the cellular level: ●●

Green algae include many freshwater species. Almost all brown and red algae, for example, are marine, as are many of the green algae. Land plants evolved from freshwater, not marine, ancestors.

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●●

The cells of green algae are chemically and structurally similar to those of land plants. They have the same kinds of chlorophyll, store the same kinds of carbohydrates, and have the same kinds of cell walls.

The green algal origin of land plants, long known from the fossil record, has been confirmed by DNA studies in which green algae of the family Charophyceae have been found to be more similar to land plants than are any other algae. The charophytes have some reproductive structures that are similar to the embryonic enclosures found in land plants. Land plants, therefore, are a lineage within the green algae. Freshwater algae often live in shallow water, and shallow water frequently dries up. Algae that had adaptations that allowed them to continue to function when water became mud would be favored by evolution. The first land plants, as seen in the fossil record, were small plants in wetlands, consistent with this explanation.

Amoebozoan Protists Most of the amoebalike protists are in the amebozoan lineage. Amoebalike cells move along surfaces when their cytoplasm flows into pseudopods. The pseudopods may also surround and engulf food items. Amoebalike cells have evolved independently in the discicristate and cercozoan lineages, although the amoebozoans have lobe-shaped pseudopods, as opposed to the filamentous ones in the cercozoans. Plasmodial slime molds are amoebozoans. Cells of Dictyostelium discoideum crawl in the soil and eat bacteria. When their food supply is scarce, they release cyclic AMP, which acts as a hormone that causes them to integrate into a multicellular sluglike creature that crawls along the surface of the ground. The head end of the slug attaches to the ground, and the rear end of the slug heaves up into the air (slowly) and lengthens into a stalk with a capsule on the end. The capsule produces sexual spores, which blow away to new locations. Although plasmodial slime molds superficially resemble cellular (discicristate) slime molds, they evolved this mode of living independently.

Opisthokont Protists Opisthokonts have flagellated cells with a single, basal flagellum. One of the opisthokont lineages is the fungi. Another lineage has produced flagellated protists called choanoflagellates, and the animals. The name choanoflagellate refers to the flagellum that emerges from a collarlike structure. The flagellum draws water into the collar, where small cellular protrusions capture bacteria and detritus. Choano-

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protostomes  449 flagellates can swim, but can also adhere to surfaces, sometimes forming small clusters or colonies. The structure of choanoflagellates closely resembles that of choanocytes, the cells that line the passageways of sponges. Choanocytes of sponges create water currents and capture food items. The close similarity of choanoflagellates and sponges was noticed, and choanoflagellates have been considered the closest single-celled relatives of animals since the 19th century. This relationship has been reinforced by DNA comparisons. Independently in most of these lineages, multicellularity has at least begun to evolve: Slime molds form temporary multicellular reproductive units in two of the lineages; heterokonts include the brown algae; the plant lineage includes red algae as well as green algae and land plants; and animals and fungi are opisthokonts that independently evolved multicellularity. There is no overarching law of progress toward complexity in evolution, but multicellularity allows adaptations that single cells cannot have and has been favored by natural selection over and over again. Even single-celled organisms (including bacteria) benefit from forming colonies with some division of labor among their components. See also cladistics; eukaryotes; symbiogenesis. Further Reading Byrnes, J., et al. “Predator diversity strengthens trophic cascades in kelp forests by modifying herbivore behavior.” Ecology Letters 9 (2006): 61–71. Dayton, P. K. “Ecology of kelp communities.” Annual Review of Ecology and Systematics 16 (1985): 215–245. Estes, James A., and D. O. Duggins. “Sea otters and kelp forests in Alaska: Generality and variation in a com-

xviii+598_Biodiversity_F.indd 449

munity ecological paradigm.” Ecological Monographs 65 (1995): 75–100. Foster, M. S., and D. R. Schiel. “The ecology of giant kelp forests in California: A community profile.” U.S. Fish and Wildlife Service Report 85 (1985): 1–152. Graham, M. H. “Effects of local deforestation on the diversity and structure of Southern California giant kelp forest food webs.” Ecosystems 7 (2004): 341– 357. ———, et al. “Deep-water kelp refugia as potential hotspots of tropical marine diversity and productivity.” Proceedings of the National Academy of Sciences USA 104 (2007): 16,576–16,580. Halpern, B. S., et al. “Strong top-down control in Southern California kelp forest ecosystems.” Science 312 (2006): 1,230–1,232. King, N., et al. “The genome of the choanoflagellate Monosiga brevicollis and the origin of metazoans.” Nature 451 (2008): 783–788. Opoku, I. Y., et al. “Shade trees are alternative hosts of the cocoa pathogen Phytophthora megakarya.” Crop Protection 21 (2002): 629–634. Patterson, D. J. “The diversity of eukaryotes.” American Naturalist 154 (1999, supplement): S96–S124. Pearse, J. S., and A. H. Hines. “Expansion of a central California kelp forest following the mass mortality of sea urchins.” Marine Biology 51 (1987): 83–91. Sala, E., et al. “Fishing, trophic cascades, and the structure of algal assemblages: Evaluation of an old but untested paradigm.” Oikos 82 (1998): 425–439. Steneck, Robert S., et al. “Kelp forest ecosystems: Biodiversity, stability, resilience, and future.” Environmental Conservation 29 (2002): 436–459.

protostomes  See animals.

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Q quaternary  period,  biodiversity  in  the

cal water to reach the arctic Ocean and prevent extensive ice formation. When the isthmus weakQuaternary period (starting 2.5 million years ago) ened ocean currents, huge ice sheets could build is the third period of the cenozoic era. it follow the up around the very cold arctic Ocean. Since the neogene period. the Quaternary period consists of beginning of the Quaternary, the arctic Ocean has the Pleistocene epoch, which ended about 12,000 been mostly covered with an ice cap. During periods years ago, and the current Holocene epoch. of glaciation, conditions in the tropical areas were Climate. the ice ages began in the Quaternary drier, largely because so much water was frozen in period. the motion of the earth relative to the Sun the ice caps. causes slight changes in sunlight intensity, which are Marine life. life in the Quaternary oceans magnified by the earth’s climatic systems. lower sunclosely resembled that of modern times: light intensity encourages the expansion of glaciers, while higher sunlight intensity encourages the glaciers ● Invertebrates. Ocean invertebrates were to melt. these Milankovic cycles have been going on very similar to those of today. for much of earth’s history, but until the Quaternary period they did not cause ice ages. During times of glacial expansion, atmospheric carbon dioxide was relatively scarce and sea levels were low; during times of glacial melt, atmospheric carbon levels increased and oceans rose (see table on pages 451 and 452). never before in earth’s history had there been such rapid shifts in global climate. However, the greenhouse effect is currently causing more rapid warming of the earth than occurred even at the end of the most recent glaciation. Continents. the continents assumed their modern arrangement in the Quaternary. especially important was the formation of the isthmus of Panama. Ocean currents had previously flowed between north and South Glyptodonts were large armadillos, now extinct, of the early Quaternary america, allowing warm tropi- period. 450

xviii+598_Biodiversity_F.indd 450

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Quaternary period, biodiversity in  451 Multicellular Biodiversity in the Quaternary Period Conditions Atmospheric oxygen

same as today

Atmospheric carbon dioxide

at pre-industrial levels (20% below modern level)

Global temperature

variable

Sea level

variable

Approximate number of families* Continental

1300

Marine

1100

Total

2400

Examples of marine animals Centrophorus squamosus

shark (extant)

Engraulis japonicus

anchovy (extant)

Eschrichtius robustus

gray whale (extant)

Homarus americanus

lobster (extant)

Oncorhynchus rastrosus

giant salmon (extinct)

Thunnus obesus

tuna (extant)

Examples of continental animals Arctodus simus

bear (extinct)

Bison antiquus

bison (extinct)

Branta canadensis

Canada goose (extant)

Canis dirus

dire wolf (extinct)

Canis latrans

coyote (extant)

Castoroides ohioensis

giant beaver (extinct)

Clemmys marmorata

turtle (extant)

Discus macclintocki

freshwater snail (extant)

Equus occidentalis

horse (extinct)

Haliacetus leucophalus

bald eagle (extant)

Hemiauchenia macrophela

llama (extinct)

Homo habilis

human (extinct)

Homo neanderthalensis

human (extinct)

Homo sapiens

human (extant)

Larus oregonus

gull (extinct)

Mammut americanum

mastodon (extinct)

Megalonyx jeffersonii

large ground sloth (extinct)

Ovis canadensis

bighorn sheep (extant)

Panthera atrox

lion (extinct)

Phalacrocorax macropus

cormorant (extinct)

Smilodon fatalis

saber-toothed cat (extinct)

Vorticifex effusa

freshwater snail (extant)

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452 Quaternary period, biodiversity in  452

first entry

Examples of land plants Acer pleistocenicum

maple (extinct)

Agropyron cristatum

grass (extant)

Alnus glutinosa

alder (extant)

Asimina triloba

pawpaw (extant)

Dacrycarpus carpenterii

podocarp conifer (extinct)

Deschampsia cespitosa

grass (extant)

Fraxinus quadrangulata

ash (extant)

Ginkgo biloba

ginkgo (extant)

Picea abies

spruce (extant)

Picea critchfieldi

spruce (extinct)

Pinus monophylla

piñon pine (extant)

Quercus palmeri

oak (extant)

Yucca brevifolia

Joshua tree (extant)

*Based on Benton.

●●

Vertebrates. Bony fishes and sharks continued to diversify in the oceans, as did the toothed whales, baleen whales, porpoises, and dolphins.

Continental life. With each ice age cycle, plants and animals in the Northern Hemisphere migrated south when glaciers advanced and north when glaciers retreated. The ice ages resulted in some extinctions, but speciation also occurred as populations were alternately separated and rejoined. ●●

●●

●●

Plant life. Nearly all modern genera of plants were in existence, and probably most species. Grassland, boreal, and desert plants spread during glacial advances, while tropical and deciduous forests spread during interglacial periods. Invertebrates. All major groups of terrestrial invertebrates had evolved before the Quaternary period. Vertebrates. Most modern genera of freshwater fishes, amphibians, and reptiles were in existence. Many large mammals did not survive the Pleistocene extinction (see figure on page 450). Modern horses of the genus Equus (which includes donkeys and zebras) became common during the Quaternary. Human ancestors evolved, first in dry forests then in the savannas of Africa toward the end of the Neogene period, and modern humans evolved during the Quaternary.

xviii+598_Biodiversity_F.indd 452

Extinction. The Pleistocene epoch ended with the Pleistocene extinction. It was not one of the mass extinctions in the history of life, but it is famous because many species of large terrestrial vertebrates became extinct at that time. The fact that this extinction event had an impact mostly on large land animals is the reason that it was not a mass extinction: Large land animals have always represented a minority of species on Earth. The Pleistocene extinction is the only extinction that selectively struck a certain group of organisms, which is one of several reasons that many scientists conclude that it was caused by human overhunting. See also greenhouse effect; ice ages; Pleistocene extinction. Further Reading Barnosky, Anthony D. “Assessing the causes of late Pleistocene extinctions on the continents.” Science 306 (2004): 70–75. Benton, Michael J. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Elias, Scott A. “Fossil insect evidence for late Pleistocene paleoenvironments of the Lamb Spring site, Colorado.” Geoarcheology 1 (2007): 381–387. Harris, John M. “Bones from the tar pits.” Natural History, June 2007, 18–22. Kenchington, Ellen L., et al. “Pleistocene glaciation events shape genetic structure across the range of the American lobster, Homarus americanus.” Molecular Ecology 18 (2009): 1,654–1,667. Kürschner, Wolfram M., et al. “Oak leaves as biosensors of late Neogene and early Pleistocene paleoatmospheric

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Quaternary period, biodiversity in  453 CO2 concentrations. Marine Micropaleontology 27 (1996): 299–312. Liu, Jin-Xian, et al. “Late Pleistocene divergence and subsequent population expansion of two closely related fish species, Japanese anchovy (Engraulis japonicus) and

xviii+598_Biodiversity_F.indd 453

Australian anchovy (Engraulis australis).” Molecular Phylogenetics and Evolution 40 (2006): 712–723. Miller, Gifford H., et al. “Ecosystem collapse in Pleistocene Australia and a human role in megafaunal extinction.” Science 309 (2005): 287–290.

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R reptiles  Reptiles are primarily terrestrial vertebrates, with amniotic eggs but without feathers or hair. an amniotic egg has a shell and a series of fluid-fi lled membranes that feed and protect the developing embryo. largely because of the amniotic egg, most reptiles are very well adapted to life on dry land. there are about 8,000 species of reptiles (see table). the category reptiles includes some but not all of the lineages that diverged from a common ancestor. as bird and mammal lineages evolved from reptile lineages, they would also be considered members of the reptile group. Many evolutionary biologists now distinguish between the synapsids and the reptiles. the synapsid group is today represented only by mammals, while the reptile group is represented by birds and those animals commonly called reptiles. the reptiles, mammals, and birds (amniotes) represent a lineage within the tetrapods or four-legged vertebrates. all other tetrapods, are referred to as amphibians. Of the major lineages of reptiles:







By the Mesozoic era, the diapsids had diverged into the archosaurs and the lepidosaurs.

estimated number of  reptile speCies Group



Number of Species

Turtles

325

Crocodilians

22

Squamates



Lizards

4,000

Snakes

3,000

the anapsids are turtles, first known from the Jurassic period. “anapsid” refers to the lack of any openings in the dermal bone on the sides of the skull; the skulls have openings only for eyes and nostrils. turtles are either the sole survivors of the primitive anapsid form, or else they evolved from diapsids when the skull openings fused shut. the synapsids included pelycosaurs, such as Dimetrodon of the Permian period and the therapsids of the triassic and Jurassic periods. the mammals, fi rst known from the Jurassic period, evolved within this lineage. the name refers to the single opening of the dermal bones of their skulls. Mammals are the only surviving synapsids. the diapsids include all other reptiles. the birds evolved from within this lineage. the name refers to the two openings of the dermal bones of their skulls.

the archosaurs diverged into the crocodiles and their relatives, fi rst known from the Jurassic period; the pterosaurs, flying reptiles of the Jurassic period and cretaceous period; and the dinosaurs. the only surviving archosaurs are the crocodile lineage and birds, which are the surviving lineage of dinosaurs. the lepidosaurs diverged into the tuataras, of which only one lineage survives on islands off of new Zealand, and the squamates (lizards and snakes), fi rst known from the Jurassic period.

454

xviii+598_Biodiversity_F.indd 454

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reptiles  455

Physiological Adaptations of Reptiles Reptiles neither generate very much body heat nor regulate their body temperature. Therefore they are both ectothermic and heterothermic. Many researchers believe dinosaurs were endothermic. Most reptiles have three-chambered hearts. The two atria of the reptile heart allow a partial separation of blood that circulates to the lungs and back (pulmonary circulation) from the blood that circulates through the rest of the body (systemic circulation). As a result, oxygenation of the blood is less efficient in most reptiles than it is in birds and mammals, which have four-chambered hearts. Crocodilians have four-chambered hearts, but the structure of the heart still allows blood to cross between systemic and pulmonary circulation; their hearts evolved four chambers independently of those in birds and in mammals. Some lizards and snakes have heart muscles that can contract in such a way as to create the same blood circulation pattern that is found in mammals and birds, even though their hearts have only three chambers. Reptiles have numerous features that allow complete adaptation to terrestrial life. Their scaly skins resist water loss. Both juvenile and adult reptiles breathe by means of lungs. Most reptiles excrete most of their nitrogenous wastes in the form of uric acid, which is less toxic than ammonia (which amphibians excrete) and requires little water to eliminate. Turtles, which live in water, excrete urea, just as mammals do. These wastes, together with intestinal wastes and gametes, exit the body through a single opening, the cloaca. Reptiles have teeth that are all more or less alike. Many reptiles replace their teeth throughout their lives. Crocodilian teeth are hollow, with new teeth developing inside of old ones; as a result, when they lose a tooth (they can lose 3,000 in a lifetime), a new one is already in place. Only in the synapsid lineage did teeth differentiate into the mammalian pattern of incisors, canines, and grinding teeth. Therefore reptiles do not chew their food very well before swallowing it. Crocodilians swallow stones (stomach stones or gastroliths), which help to grind the food in their muscular gizzard (the first chamber of the stomach). The reproductive life cycle of reptiles also allows complete adaptation to terrestrial life. Most reptiles lay eggs on land. Even marine turtles return to land to lay their eggs. In some snakes, the eggs hatch inside the mother’s body, allowing the live birth of young. Reptiles have internal fertilization. Males and females press their cloacae together, allowing the male’s sperm to travel to the female’s reproductive tract without being exposed to dry air. In many reptiles such as turtles and crocodilians, the gender

xviii+598_Biodiversity_F.indd 455

of the offspring is determined by the temperature at which the eggs are incubated.

Turtles and Tortoises The turtles and tortoises (see figure) are classified as chelonians or testudines. The common names have no clear definition: In many cases, these animals are called turtles if they live in water and tortoises if they live on dry land. “Terrapin” often refers to Malaclemys terrapin, which lives in brackish water; the name comes from a Native American word. The largest turtle is the leatherback sea turtle (Dermochelys coriacea), which can reach six and a half feet (2 m) in length and weigh a ton (900 kg). Sea turtles, particularly this species, have been the focus of worldwide conservation efforts not only because of their ecological importance in marine food webs, but also because of their dramatic egglaying and hatching events on numerous beaches around the world. Giant tortoises were widespread on land until the arrival of modern humans, who presumably hunted them to extinction. This was nearly the fate of the giant tortoises of the Seychelles and Galápagos Islands. Turtles have shells (upper carapace and lower plastron) in which ribs are fused with dermal tissue. Most turtles have hard, thick shells, but members of the family Trionychidae are the “soft-shell turtles” that defend themselves mostly by camouflage. Turtle jaws, without teeth, have beaks that (in species such as the snapping turtle) can serve as fierce weapons. Many turtles and tortoises are predators, although Galápagos tortoises eat vegetation (see photograph on page 456). Ancestral turtles could not withdraw their heads inside of their shells. Modern turtles can withdraw their heads in two different ways: The cryptodires (most turtles) pull their heads straight in, ­underneath

Painted turtles (Chrysemys picta) are cold blooded but warm up by lying in the sun.  (Mary Moore Ferracci)

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456 reptiles  456

first entry

Lizards and Snakes (Squamates)

Giant tortoises live on the Galápagos Islands off the coast of Ecuador. Most of them now live in protected areas.  (Stanley A. Rice)

the spine, while the pleurodires (the side-neck turtles) bend their necks sideways.

Crocodiles and Their Relatives “Crocodilians” include alligators, crocodiles, caimans, and gharials. The largest crocodilian (and the largest reptile) is the saltwater crocodile (Crocodylus porosus), which can reach 3,300 pounds (1,500 kg) in weight and 17 feet (5 m) in length. Prehistoric crocodiles were often much larger. Though their sprawling gait suggests that of primitive amphibians, crocodiles can walk with their legs erect underneath their bodies, as some prehistoric crocodiles did. Crocodiles and their relatives have webbed feet and a vertically flattened tail that aids them in swimming through their aquatic habitats. The secondary palate that isolates the breathing passages from the mouth allows them to immerse in water except for eyes and nostrils as they wait for their prey. Alligators and caimans have wider and shorter heads, with a snout that is more U-shaped than V-shaped, as in crocodiles. Crocodiles are most easily recognizable because the fourth tooth of the lower jaw is visible outside of the mouth when the jaw is closed. Crocodiles are usually lighter in color and more aggressive than alligators. There are only two species of alligators: one in the southeastern United States (Alligator mississippiensis) and one in the Yangtze River of China. There are only two species of gharials, with elongated snouts, native to India and Malaysia. Because of their role as top predators in many freshwater habitats, protection of crocodilians has been a focus of many conservationists. Researchers were surprised to discover that crocodilian blood has strong antiviral properties. This is just one more example of the unexpected human benefits that may result from the preservation of biodiversity.

xviii+598_Biodiversity_F.indd 456

Snakes are legless reptiles that lack eyelids and external ears, and have broad plates on the ventral (lower) surface of the body, the movement of which propels them forward. Snakes have no necks, very long bodies with 200 to 400 vertebrae, and very short tails. Snakes have adaptations that allow their bodies to be as narrow as possible while still having a lot of muscle. For example, many snakes have only a right lung. Some snakes have primitive properties: Pythons and boas have rudimentary hip bones, indicating that their ancestors had legs, and their left lungs are almost as large as their right lungs. Many snakes are venomous. Venom is modified saliva, delivered by fangs that can be grooved or hollow. More than 700 species of snakes are venomous, 250 of which can kill a human with a single bite. Some snakes squeeze and suffocate (but do not crush) their victims. Snakes smell with their tongues, which, being forked, can distinguish the direction from which a particular scent comes. Because they lack external ears, snakes cannot hear very well, but they are very sensitive to vibrations. Because they cannot manipulate large food items, snakes must swallow their prey whole. Their very flexible jaws allow them to eat animals larger than themselves (see figure). The lack of legs allows snakes to move through narrow crevices that few other animals could penetrate. Examples of snakes include: ●● ●●

Boas (family Boidae) and pythons (family Pythonidae) asphyxiate their victims. Elapids (family Elapidae) include many of the most venomous snakes. Naja naja, the

Snakes can eat very large prey: This Afghan snake is eating a lizard that is almost as large as itself.  (Wikimedia)

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reptiles  457

●●

●●

Indian cobra, raises itself from the ground and spreads out its upper body in a threat display. Dendroaspis polylepis, the black mamba of Africa, has venom that shuts down both nerve and heart activity in its victims. The spitting cobra (Hemachatus haemachatus) can spit venom over 6 feet (2 m) into the eyes of prey or attackers. North American coral snakes are poisonous, though not aggressive. Nonpoisonous king snakes have red, black, and yellow bands, apparently in mimicry of coral snakes. They can be distinguished by the red and yellow bands adjoining one another in coral snakes (“Red and yellow, kill a fellow”). Vipers (family Viperidae), with their distinctive triangular heads, can inject venom through hollow, retractable fangs. They can open their mouths nearly 180° when biting. One group of vipers, the pit vipers, has infrared-sensitive pits behind their eyes that allow them to sense the presence of a warmblooded victim in the dark. Vipers in the United States include the copperhead Agkistrodon contortrix, the cottonmouth Agkistrodon piscivorus, and rattlesnakes such as the sidewinder Crotalus cerastes. Shed scales remain attached to the tail, which rattlesnakes vibrate to produce a warning rattle. Scolecophid snakes are small snakes that burrow in the ground. One of them, Leptotyphlops carlae from Barbados, is only 4 inches (10 cm) long. Other squamates include the following:

●●

Chameleons (family Chameleonidae) have several unique features. Their eyes can move independently of one another, allowing a range of vision unmatched in most animals. In Madagascar, where chameleons are diverse and numerous, the native Malagasy people say that chameleons keep one eye on the past and one on the future. They also have very long tongues, which may be as long as the body. The tongue has a bone that moves the tongue quickly and a suction cup that grabs the prey (in 30-thousandths of a second). Chameleons are perhaps most famous for being able to change the color of their skin to camouflage them against their backgrounds and, perhaps more importantly, as a social signal. One layer of skin contains cells with yellow or red pigment granules; if the granules are concentrated in the center of a cell, it is nearly transparent,

xviii+598_Biodiversity_F.indd 457

●●

●●

●●

●●

but if the granules are spread throughout the cell, it has intense color. Another layer of skin reflects blue light. Green skin results from blue light reflected back through cells with dispersed yellow pigment granules. Komodo dragons (Varanus komodoensis), up to 10 feet (3 m) long and weighing 150 pounds (70 kg), are the largest lizards in the world. They live on a few Indonesian islands. There are no large native mammals on the islands they inhabit, and as a result they have evolved to a large size. They are poisonous but are too slow to frequently hunt; they mostly eat carrion. Gila monsters (Heloderma suspectum) are the only venomous lizards in the United States. They are very sluggish and produce little venom. They use the venom mostly for defense and must chew in order to get the venom into the victim’s tissues. Geckos are numerous species of small, often brightly colored lizards that are unique in being able to make sounds and in their ability to walk on vertical surfaces. Their foot pads have numerous tiny hairlike structures that adhere to surfaces not with chemicals but by displacing electrons on their surfaces, creating an electrical attraction. Technologists are studying gecko feet to produce nonchemical adhesive structures, making geckos one of the best examples of biomimicry. Skinks are small lizards with long tails, short necks, and short legs.

Snakes are not as distinct from lizards as might first appear. Some lizards lack movable eyelids. Perhaps most importantly, many separate lineages of lizards are fully or partly legless (a major example of evolutionary convergence), as in the following examples: ●●

●●

●●

Glass snakes (genus Ophisaurus, Greek for “snake-lizard”) are legless lizards that, unlike snakes, have movable eyelids, external ear openings, and the ability to drop parts of their tails (like broken glass) to distract predators. The dropped portion of the tail continues to move as a decoy to the predator, while the glass snakes make their bodies immobile. Grass lizards (genus Chamaesaura) have rudimentary hind limbs and no forelimbs. They “swim” through the grass with snakelike movements. Fogs (family Pygopodidae) have rudimentary hind limbs and no forelimbs, and are

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458 reptiles  458

●● ●● ●●

●● ●●

●●

first entry

very elongated in shape, like snakes. They are close relatives of geckos. Dibamid lizards are not only legless but, living in burrows, are nearly blind. Genus Anniella contains two species of American legless lizards. Several species of spectacled lizards (family Gymnophthalmidae) have reduced or absent hind limbs; they pull themselves forward with their forelimbs. Genus Typhlosaurus is a skink without legs; other genera of skinks have reduced legs. Some species of plated lizards (family Gerrhosauridae) have only rudimentary hind limbs. Amphisbaeneans are another lineage of legless lizards. They are sometimes considered to be a lineage distinct from the lizards and snakes.

Tuataras The two species of tuataras (genus Sphenodon) look like lizards, but they are the only surviving members of a separate lineage that may closely resemble primitive diapsids. Tuataras were more common and diverse than lizards 200 million years ago. Today they live only in New Zealand. For example, the vertebrae are hourglass-shaped, as in fishes and a few amphibians, and tuataras are the only amniotes to have this type of vertebrae. Their abdominal ribs also have a primitive structure that is unique among amniotes. Tuataras also have a third eye on the top of the head: The parietal eye has its own lens, cornea, and retina. Its optic nerve connections have degenerated, and it is more closely associated with the pineal gland, which regulates the biological clocks of vertebrates. The third eye is visible only in newly hatched tuataras, and is soon covered by skin and scales. See also biodiversity, resources for medicine; biomimicry; convergence; dinosaurs; Galápagos Islands. Further Reading Adams, Clark E., and John K. Thomas. Texas Rattlesnake Roundups. College Station, Tex.: Texas A and M Press, 2008. Apesteguía, Sebastián, and Hussam Zaher. “A Cretaceous terrestrial snake with robust hindlimbs and a sacrum.” Nature 440 (2006): 1,037–1,040. Barrow, Mark. “Dragons in distress: Naturalists as bioactivists in the campaign to save the American alligator.” Journal of the History of Biology 42 (2009): 267–288. Browne, Constance L., and Stephen J. Hecnar. “Species loss and shifting population structure of freshwater turtles despite habitat protection.” Biological Conservation 138 (2007): 421–429.

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Cree, A., et al. “Reproduction of a rare New Zealand reptile, the tuatara Sphenodon punctatus, on rat-free and rat-inhabited islands.” Conservation Biology 9 (1995): 373–383. Dubois, Y., et al. “Thermoregulation and habitat selection in wood turtles Glyptemys insculpta: Chasing the sun slowly.” Journal of Animal Ecology 78 (2009): 1,023–1,032. Ernst, C. H., and R. W. Barbour. Turtles of the World. Washington, D.C.: Smithsonian Institution Press, 1989. Fry, Brian, et al. “Early evolution of the venom system in lizards and snakes.” Nature 439 (2006): 584–588. Girard, Charlotte, et al. “Post-nesting migrations of loggerhead sea turtles in the Gulf of Mexico: Dispersal in highly dynamic conditions.” Marine Biology 156 (2009): 1,827–1,839. Glaucas, X., et al. “Timing and reproduction of a cold desert viperid snake from North America, the Great Basin rattlesnake (Crotalus lutosus).” Journal of Arid Environments 73 (2009): 719–725. Greene, Harry W. Snakes: The Evolution of Mystery in Nature. Berkeley: University of California Press, 1997. Henderson, Donald M. “Effects of stomach stones on the buoyancy and equilibrium of a floating crocodilian: A computational analysis.” Canadian Journal of Zoology 81 (2003): 1,346–1,357. Kelly, Shannon M., et al. “Accumulation and maternal transfer of polychlorinated biphenyls in snapping turtles of the upper Hudson River, New York, U.S.A.” Environmental Toxicology and Chemistry 27 (2008): 2,565–2,574. Kenow, Kevin P., et al. “Predation of radio-marked mallard (Anas platyrhynchos) ducklings by eastern snapping turtles (Chelydra serpentina serpentina) and western fox snakes (Pantherophis vulpinus) on the upper Mississippi River.” Journal of Herpetology 43 (2009): 154–158. Maladen, Ryan D., et al. “Undulatory swimming in sand: Subsurface locomotion of the sandfish lizard.” Science 325 (2009): 314–318. Mazzotti, Frank J., et al. “Alligators and crocodiles as indicators for restoration of Everglades ecosystems.” Ecological Indicators 9 (2009, supplement): S137–S149. Merchant, Mark E., et al. “Antiviral activity of serum from the American alligator (Alligator mississippiensis).” Antiviral Research 66 (2005): 35–38. Motani, Ryosuke. “The evolution of marine reptiles.” Evolution Education and Outreach 2 (2009): 224–235. Mullin, Stephen J., and Richard A. Seigel. Snakes: Ecology and Conservation. Ithaca, N.Y.: Cornell University Press, 2009. Navas, Carlos A., et al. “Morphological and physiological specialization for digging in amphisbaenians, an ancient lineage of fossorial vertebrates.” Journal of Experimental Biology 207 (2004): 2,433–2,441.

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resistance, evolution of  459 Pianka, Eric R., and L. J. Vitt. Lizards: Windows to the Evolution of Diversity. Berkeley: University of California Press, 2003. Pyron, R. Alexander, and Frank T. Burbrink. “Lineage diversification in a widespread species: Roles for niche divergence and conservatism in the common kingsnake, Lampropeltis getula.” Molecular Ecology 18 (2009): 3,443–3,457. Ramstad, Kristina M., et al. “Species and cultural conservation in New Zealand: Maori traditional ecological knowledge of tuatara.” Conservation Biology 21 (2007): 455–464. Santidrián Tomillo, Pilar, et al. “Influence of emergence success on the annual reproductive output of leatherback turtles.” Marine Biology 156 (2009): 2,021–2,031. Shine, Richard. “Life history evolution in reptiles.” Annual Review of Ecology, Evolution, and Systematics 36 (2005): 23–46. ———, et al. “Windows of embryonic sexual lability in two lizard species with environmental sex determination.” Ecology 88 (2007): 1,781–1,788. Stuart-Fox, D., and A. Moussalli. “Selection for social signaling drives the evolution of chameleon color change.” Public Library of Science Biology 6 (2008): e25. Vincent, S. E., et al. “Convergence in trophic morphology and feeding performance among piscivorous natricine snakes.” Journal of Evolutionary Biology 22 (2009): 1,203–1,211. Walker, DeEtte, and John C. Avise. “Principles of phylogeography as illustrated by freshwater and terrestrial turtles in the southeastern United States.” Annual Review of Ecology and Systematics 29 (1998): 23–58. Wang, Xianyan, et al. “Response specificity to advertisement vocalization in the Chinese alligator (Alligator sinensis). Ethology 115 (2009): 832–839. Warner, Daniel A., and Richard Shine. “The adaptive significance of temperature-dependent sex determination in a reptile.” Nature 451 (2008): 566–568. White, Mel. “When crocs ruled.” National Geographic, November 2009, 128–139.

being weeded out. Now, in many areas and among many species only the strong and fit remain to defy our efforts to control them.” This entry will focus on the evolution of resistance to herbicides in populations of weeds and of resistance to pesticides in populations of animal pests. Within populations of pest animals and weeds, some individual organisms may be resistant to the chemicals that kill most of the other organisms. Examples include the following: ●●

●●

Under normal conditions (in the absence of pesticides and herbicides), the mutant (resistant) individuals have inferior reproduction: ●●

●●

resistance, evolution of  Microbes, insects, and weeds have evolved resistance to the chemical methods used to control them. The most important modern example of natural selection—both in terms of the clear and easily studied process, and of importance to human health and the economy—is the evolution of antimicrobial, pesticide, and herbicide resistance. As biologist Rachel Carson wrote in 1962, “If Darwin were alive today the insect world would delight and astound him with its impressive verification of his theories of the survival of the fittest. Under the stress of intensive chemical spraying the weaker members of the insect populations are

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Within a population of insects, certain individuals may have a genetically based ability to resist pesticides that will kill most members of their species. This resistance may result from an increased production of defensive enzymes, the production of an improved defensive enzyme, or a behavioral tendency to detect and avoid the pesticide. For example, some cockroach populations have evolved an aversion to sugar—not a good thing for them, under normal conditions, but it does cause them to avoid sugarbaited pesticide traps. Within a population of weeds, certain individuals may have a genetically based ability to resist herbicides that would kill most members of their species. This resistance may result from a mutation that alters the membranes of the chloroplast, the structure within plant cells that carries out photosynthetic food production.

●●

Insects that expend much of their metabolic reserves producing resistance enzymes have less energy left over for reproduction than normal insects. Rats that are resistant to the rat poison warfarin suffer a high incidence of bleeding and require higher levels of vitamin K in their diets; therefore, under normal conditions, they bleed to death and die of vitamin deficiency more frequently than normal rats. Weeds with mutated chloroplasts have inferior photosynthetic food production compared to normal weeds.

Under these conditions, natural selection operates against the resistant individuals. But when pesticides or herbicides are common and persistent in the environment of the populations, natural selection operates in favor of these very same resistant

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460 restoration ecology  460 individuals. The heavy and persistent use of chemicals, therefore, creates the perfect environment for the evolution of animals and weeds that resist the very chemicals that humans use to control their populations. Individual animals and weeds generally cannot change their resistance. They either are resistant or are not. The individuals survive and reproduce or they do not survive; therefore only the populations and species can evolve resistance. The extensive and heavy use of pesticides has selected pesticide-resistant insects and rats; the extensive and heavy use of herbicides has selected herbicide-resistant weeds. The first DDT-resistant mosquitoes in Pakistan were detected in 1965, just five years after DDT use began in the region. The swift evolution of resistance occurs with each new pesticide. In the last decade, more than 520 species of insects and mites, 273 weed species, 150 plant diseases, and 10 rodent species have developed genetic resistance to at least one pesticide or herbicide. Many species are now becoming resistant to all major classes of insecticides. An insect that is resistant to one pesticide is often resistant to other related, chemically similar pesticides. In addition to promoting the evolution of resistant strains of animals and weeds, the overuse of chemicals in insect control and agriculture has resulted in the buildup of toxicity in the environment and in the food chain. The evolution of pesticide resistance in insects and rat populations has implications both for public health and for agriculture. Pesticide sprays are heavily used to control many species of insects, such as the mosquitoes that spread diseases like malaria and yellow fever. Insect pests (such as weevils and caterpillars) cause millions of dollars of agricultural yield loss. When the sprays become less effective (because many, though not all, of the insect populations evolve resistance), public health officials may respond by increasing the application of sprays, which has two effects: greater environmental contamination and an even greater evolution of resistance. The evolution of herbicide resistance in weeds also portends greater agricultural yield loss (due to competition between weeds and crops) and greater environmental contamination from stepped-up herbicide applications. In recent years, crops (such as maize, soybeans, and potatoes) that have been genetically engineered to resist herbicides have come on the market, and large acreages are now devoted to them. Farmers can now spray massive amounts of herbicides on their fields, to kill the weeds, without fear of killing the crops. This encourages the heavy use of herbicides—which is precisely what the companies that sell the seeds of these crops want, since the herbicides are manufactured by the same compa-

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first entry nies that sell the seeds. Unfortunately, this will result in even greater environmental contamination. There is some concern that the genetic basis of herbicide resistance, which has been put into crops by genetic engineering, could spread to wild weed species by crossbreeding. While this has not happened extensively, it has occurred: Resistance to the herbicide glyphosate has been transferred from crops to weeds within the crucifer (mustard) family by cross-pollination. Once the resistance genes are in the wild weed populations, natural selection will favor their spread whenever herbicides are used. To minimize this process, researchers have also bred crops that resist the herbicide Dicamba. Because the mechanism of resistance occurs in the chloroplasts, and pollen contains no chloroplasts, it is unlikely that this form of herbicide resistance will spread through cross-pollination. An evolutionary understanding of public health and agriculture demands that pesticides and herbicides be used sparingly to minimize environmental contamination and to prevent the evolution of resistance in the very species of organisms that humans are trying to control. If the use of chemical control agents is restrained, they will remain effective when they are really needed in an emergency. The overuse of chemical control agents is a direct result of overlooking the laws of ecology and evolution. See also natural selection. Further Reading Behrens, Mark R., et al. “Dicamba resistance: Enlarging and preserving biotechnology-based weed management strategies.” Science 316 (2007): 1,185–1,188. Summarized by Service, Robert F. “A growing threat down on the farm.” Science 316 (2007): 1,114–1,117. Carson, Rachel. Silent Spring. New York: Houghton Mifflin, 1962. Smith, P., et al. “A new aspect of warfarin resistance in wild rats: Benefits in the absence of poison.” Functional Ecology 7 (1993): 190–194. Tardif, F. J., et al. “A mutation in the herbicide target site acetohydroxyacid synthase produces morphological and structural alterations and reduces fitness in Amaranthus powellii.” New Phytologist 169 (2006): 251–264. WeedScience.org. “International Survey of Herbicide Resistant Weeds.” Available online. URL: http://www.weed science.org/in.asp. Accessed August 8, 2011.

restoration ecology  Restoration ecology is the application of ecological principles to restore a damaged ecosystem to something close to its original integrity. Scientific principles of ecology allow current problems to be identified and allow

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restoration ecology  461 researchers to determine what the goal should be—the characteristics that the restored ecosystem should have. One major problem in restoration ecology is that it is often impossible to determine what the characteristics of the “original” ecosystem were. Throughout most of the world, prehistoric peoples have in fact altered natural ecosystems on large and small scales. The most noticeable large-scale alteration has been the maintenance of grasslands. Native Americans started fires that burned large areas of central North America, encouraging the spread of grasslands (and the game animals that lived in them) at the expense of forests. Although the tallgrass prairie was not an artificial ecosystem, its geographic extent was artificially enhanced. On a smaller scale, Native Americans built up artificial embankments of rich soil on which they raised crops and lived. The soils of the Amazon Basin are (except along rivers and near the volcanic Andes) notoriously poor in nutrients and will not hold nutrients for very long after fertilizer (such as the ashes of a burned forest) is applied. Amazonian tribes built compost piles that included pottery shards, which persist today as pockets of rich soil known as terra preta de Indio. The Mississippian culture covered much of eastern North America about 700 years ago, and the tribes (united by extensive trade networks) built artificial mounds not only for their buildings (thus earning the name Mound Builders), but also for agriculture. When botanist William Bartram traveled through Florida and what is now Mississippi and Alabama in the late 18th century, he saw many of these mounds, regarding which the Natives that he met knew nothing. There is evidence that Australian aborigines used fire to transform the arid regions of that continent into grassland. Few if any restoration ecologists would claim that ecosystems should be restored to the conditions that existed prior to the fire regimes and other transformations of the original inhabitants. The standard map of potential natural vegetation in the coterminous United States, drawn up by A. W. Küchler in 1964, depicts plant communities prior to European, not Native, habitation. In some cases, aboriginal inhabitants promoted extensive ecological degradation. Outstanding examples are Pleistocene and recent extinctions and land degradation. There is evidence that the Hohokam culture of the American southwest, the Mississippian culture of eastern North America, and the Mayan culture of Central America caused deforestation and soil erosion extensive enough to contribute to their own collapse, although the immediate precipitating events were droughts several centuries ago. In semiarid regions, such as the

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American Southwest, ecological degradation caused by aboriginal inhabitants may have contributed to a nearly permanent change in vegetation. The land around Chaco Canyon, New Mexico, is now desert, but when it was inhabited by people who lived in large apartment complexes (see photograph), piñon pine forest was extensive, and there was enough water to raise corn for hundreds of people. It is possible that soil degradation, caused by those inhabitants, contributed to the failure of the pine forest to regenerate. Restoration ecologists, therefore, would aim to restore ecosystems to the condition in which Native peoples originally lived before they caused ecological degradation. Some situations that observers of nature have assumed to be “natural” may have been the product of indirect human alteration of habitats. Perhaps the best example of this is the huge populations of bison (Bison bison) and passenger pigeons (Ectopistes migratorius) just prior to European and American conquest of North America. Every child is taught that prairies covered with millions of bison and the air blackened with millions of passenger pigeons that would break limbs from trees in which they roosted, was “natural” and brought to an end by deliberate overhunting. The second half of this statement is undeniably true. But how natural were the huge populations? Scholars have suggested that large populations of Native Americans kept both bison and pigeon populations under control by hunting. Then European diseases such as smallpox, introduced (in most cases) accidentally, reduced Native American populations by up to 90 percent. In some cases, entire agriculture-based civilizations (such as those of southeastern North America) were destroyed and replaced by scattered villages. With only 10

There was a large city in Chaco Canyon of New Mexico about 1000 c.e. This civilization collapsed during a prolonged drought that was made worse by deforestation.  (Stanley A. Rice)

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­ ercent as many hunters as before, game populations p exploded. This may also be the reason that William Bartram saw hundreds of alligators in nearly every pool and stretch of river that he explored in the late 18th century. Most of the Native fishermen had died; fish populations exploded and so did the populations of alligators that ate them. It would therefore be unrealistic for a restoration ecologist to attempt to bring back huge populations of bison, pigeons, or alligators. An even more important problem is that it may be impossible to restore the “original” ecosystem characteristics even if they were known. Reasons include the following: ●●

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Some of the original species have become extinct. This would apply not only to all of the species lost in the Pleistocene extinction, but those driven to extinction by hunting much more recently, such as the elephant birds (family Aepyornithidae) extirpated by the original inhabitants of Madagascar, the moas (bird family Dinornithidae) by the Maori of New Zealand, and the dodos (Raphus cucullatus) killed by Europeans on the island of Mauritius. Extinctions of some species can cause a cascade of other extinctions, although this has not been documented to occur. It appears that dodos were important dispersers of the seeds of the tambalacoque tree (Sideroxylon grandiflorum), and that the extinction of the dodos has reduced the reproduction of this tree. In most cases, however, other species move into the role vacated by the extinct species and at least partly compensate for the disappearance. Dodos were not the only dispersers of tambalacoque seeds (although most of the other animals that ate the seeds are also extinct). When a fungal disease killed almost all adult American chestnut trees in the eastern deciduous forest of North America, various species of oaks primarily took their place. Invasive species have been introduced. It is nearly impossible to eradicate invasive species. Restoration ecologists have considered themselves successful when they have reduced invasive species populations to the extent that they do not significantly depress the populations of the native species. Climatic conditions have changed and will continue to change. Ecological degradation is not the only reason that piñon forests will not grow in Chaco Canyon today; a drier climate also contributes. As the greenhouse

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effect intensifies, it may be impossible to restore vegetation cover that depends on the climatic conditions that prevailed even a few decades ago. If global warming continues at its current rate, sugar maples will grow only in Canada. A certain amount of global warming is inevitable. Therefore, some of the southern part of the sugar maple’s range will inevitably be lost. Tundra conditions may not exist, and tundra restoration may be impossible, in the next century. Sometimes these factors interact with one another. Introduced tree species such as eucalyptus often use a lot of water from underground sources and cause the water table to drop, thus creating an effectively drier climate. Agriculture covers a large area of the Earth. Almost a third of the Earth’s dry land surface has been transformed into farmland or managed pasture. Intensification of agricultural practices has barely kept pace with increases in human population. It is nearly inconceivable that the area of land now used for agriculture will ever be reduced or that those areas will be restored to the condition they were in prior to modern agriculture. Human habitation has created a demand for fire suppression. Fires are an essential component of nearly every natural ecosystem, even though they may play a minor role in those with high rainfall. Fire suppression has allowed ponderosa pine to spread into land formerly occupied by shortgrass prairie in the Black Hills of South Dakota. Trees that live in wetter conditions, such as shumard oaks (Quercus shumardi), grow underneath and replace post oaks (Quercus stellata) in the Cross Timbers forest that have not been burned, and these trees have actually created wetter conditions, a process known as mesophication. Largescale fires for habitat restoration would be vigorously opposed by local residents in all of these places. The scale of restoration is simply too large. The aquatic habitats of Chesapeake Bay have been severely damaged by human activities, including the nutrients and sediments in the watershed runoff. The previously abundant oysters find it difficult to regenerate as sediment builds up. Fertilizer in the runoff from cities and farms has caused eutrophication. The result has been large “dead zones” of anoxic water at the bottom of the bay. There have been some recent successes at ecologi-

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restoration ecology  463

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cal restoration in Chesapeake Bay. Ecologist David Schulte led a project to create artificial reefs on one of the tributaries to the bay. Within five years, this project had allowed the regeneration of 185 million native oysters (Crassostrea virginica). But saving the entire bay may prove impossible. Although Chesapeake Bay is very large, it is dwarfed by the size of the heavily populated watershed around it. The causes of environmental degradation are ongoing. Perhaps the best example of this problem is coral bleaching. Some bleached coral reefs have been restored by creating new surfaces upon which larval corals can settle or by simply having local divers break off pieces of healthy coral in one location and wedge them into bleached coral reefs, where they act as sources of regeneration. The sometimes spectacular (though spatially limited) regrowth of coral on reefs will be nullified by the same conditions that produced bleaching in the first place, which have been intensified by global warming.

One example of a natural habitat that has been changed beyond the possibility of restoration (on any timescale meaningful to modern civilization) is the San Joaquin Valley of California. Much of this valley used to be covered by a large shallow lake, Tulare Lake, because snowmelt from the Sierra Nevada came down the Kern, Tule, and Kaweah Rivers and was blocked by the Coast Ranges. During the 1930s, a large system of irrigation canals was built by the federal Bureau of Reclamation to use the snowmelt for irrigation. The San Joaquin Valley is now almost entirely agricultural. The climate is much less humid, and the valley is saturated with pesticides. Nearly every plant species in the valley is introduced, either by agriculture (e.g., citrus and olive orchards) or as weeds, except some of the spring wildflowers. The dominant grasses are annuals introduced from Europe and Asia (such as Avena and Bromus); the native perennial grasses are rare. Eucalyptus trees, introduced from Australia, can tolerate the dry conditions, and when they establish a forest, their toxic leaves inhibit the growth of other plants. There has been remarkably little extinction, though many animal species persist only in nearby foothills. Restoration ecologists generally focus on restoring ecosystem function rather than returning ecosystems to a pristine, precivilized condition. Indicators of damaged ecosystems are conditions such as excessive runoff of water, soil, and nutri-

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ents or the proliferation of pests and introduced species. A “managed ecosystem,” which functions as agricultural land or as a source of wood, will have more, but perhaps not much more, runoff than a natural ecosystem. In many places, such as China, intact forests are cut down and replaced by tree plantations of single species, such as eucalyptus (the low-quality wood of which is used for paper production), rubber, or oil palm. The profit, much of which goes to poor local people, is nearly irresistible. But research has shown that a mixture of native tree species can yield almost as much profit and have much less soil erosion and runoff. In a mixture of tree species, the faster-growing trees can be selectively harvested, leaving behind the slower-growing trees for later harvest; the trees left behind hold down the soil. A mixed-tree plantation produces better humus and water retention than a single-species plantation. A rubber plantation in Southeast Asia has three times as much runoff and 45 times as much soil erosion as an intact forest. A managed forest can easily have less runoff and erosion than a rubber plantation. A replanted forest of large native trees, with a shade crop of tea underneath them, is not a natural ecosystem but functions like one and can be profitable to local people. In a few cases, habitat restoration is as easy as discontinuing the disturbance that damaged it in the first place. Many species return on their own without needing to be seeded or stocked. Sometimes they can do so with a little technological help. Coral reef regeneration is enhanced by exposing the damaged reef to a chemical that induces coral larvae to settle on the exposed surfaces. Usually, however, substantial work is needed to create conditions for the success of the returning species. Deforested land is often too hot and dry for native trees to grow back. Shrubs may need to be planted as “nurse plants” under whose shade the native trees can establish themselves. Sometimes these nurse plants are the invasive species themselves, which do not need to be planted, and many of which will die in the shade of the replanted trees once they have grown. Frequently, invasive plants must be laboriously and repeatedly removed, at least until the restored species become established. In addition, it is necessary to ensure that the populations involved in habitat recovery have sufficient genetic variation. Care must be taken to ensure that pollinators and other mutualists return to the restored ecosystem. One of the most ambitious restoration projects is taking place in the Aral Sea in the former Soviet Union. The Aral Sea was once the fourth largest inland body of water. Under Soviet control, the water

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464 restoration ecology  464

first entry See also extinction; grasslands and savannas; invasive species; marshes and swamps; Pleistocene extinction; temperate deciduous forests. Further Reading

This fishing vessel is stranded on dry land that used to be under the surface of the Aral Sea in western Asia.  (Lukasz Kruk)

from rivers that kept the Aral Sea full was diverted to irrigate cotton. One result was that large areas of the Aral Sea dried up, destroying the fishing industry that it had once supported. The sight of large fishing vessels sitting stranded on vast dry plains became an international icon of environmental degradation (see figure). Another effect was from the irrigation itself. Salt buildup (salinization) degraded the fertility of the agricultural soil, and salt in the dust contributed to respiratory problems of the local residents. The northern section of the Aral Sea had shrunk by 75 percent by the time a joint project of the World Bank and the government of Kazakhstan built the Kok-Aral Dam between the northern and southern sections of the Aral Sea. Between 2003 and 2008, the northern part of the sea grew 30 percent larger and 40 percent deeper. The next phase of reclamation will remediate salty soils into sustainable pasturelands. Perhaps the biggest threat to the success of restoration ecology is that the causes of the original problem are ongoing. Global warming will continue to promote coral bleaching and the decline of forests. Poor people will continue to devastate natural habitats in their pursuit of mere survival. They need an alternative to practices that are destructive to natural ecosystems, such as deforestation for farming and the blast fishing that has destroyed many coral reefs. Meanwhile, the new techniques that are being developed by restoration ecologists will allow habitat managers to quickly take advantage of any improvements in the current situation that may come along. There remains a lot of room for improvement. A recent study that combined the results of 89 restoration assessments showed that the restored ecosystems had only 44 percent as much biodiversity, and provided only 25 percent as many ecosystem services, as intact ecosystems.

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Bartram, William. Travels through North and South Carolina, Georgia, East and West Florida, the Cherokee Country, the Extensive Territories of the Muscogulges or Creek Confederacy, and the Country of the Chactaws. Philadelphia: James and Johnson, 1791; reprinted Savannah, Ga.: Beehive Press, 1973. Behre, Karl-Ernst. “The role of man in European vegetation history.” In Vegetation History, edited by B. Huntley and T. Webb III, 633–672. Dordecht, Netherlands: Kluwer Scientific Publications, 1988. Benayas, José M. Rey, et al. “Enhancement of biodiversity and ecosystem services by ecological restoration: A meta-analysis.” Science 325 (2009): 1,121–1,124. Chazdon, Robin L. “Beyond deforestation: Restoring forests and ecosystem services on degraded lands.” Science 320 (2008): 1,458–1,460. Comin, Francisco A., ed. Ecological Restoration: A Global Challenge. New York: Oxford University Press, 2010. Dean, Jeffry S. “Anthropogenic environmental change in the Southwest as viewed from the Colorado Plateau.” Chap. 10 in The Archaeology of Global Change: The Impact of Humans on Their Environment, edited by Charles L. Redman et al. Washington, D.C.: Smithsonian Institution Press, 2004. Dixon, Kingsley W. “Pollination and restoration.” Science 325 (2009): 571–573. Environmental News Service. “The Kazakh Miracle: Recovery of the North Aral Sea.” August 1, 2008. Available online. URL: http://www.ens-newswire.com/ens/ aug2008/2008-08-01-01.asp. Accessed August 4, 2010. Harris, Jim. “Soil microbial communities and restoration ecology: Facilitators or followers?” Science 325 (2009): 573–574. Henson, Kate S. E., et al. “The restoration of parasites, parasitoids, and pathogens to heathland communities.” Ecology 90 (2009): 1,840–1,851. Jackson, Stephen T., and Richard J. Hobbs. “Ecological restoration in the light of ecological history.” Science 325 (2009): 567–569. Koenig, Robert. “Unleashing an army to repair alien-ravaged ecosystems.” Science 325 (2009): 562–563. Mann, Charles C. 1491: New Revelations of the Americas before Columbus. New York: Knopf, 2005. ———. “Addicted to rubber.” Science 325 (2009): 564–566. Manning, Adrian D., and David Lindenmayer. “Paddock trees, parrots, and agricultural production: An urgent need for large-scale, long-term restoration in southeastern Australia.” Ecological Management and Restoration 10 (2009): 126–135.

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rivers, streams, ponds, and lakes  465 Maran, Tiit, et al. “The survival of captive-born animals in restoration programmes: Case study of the endangered European mink, Mustela lutreola.” Biological Conservation 142 (2009): 1,685–1,692. Martin, Katherine L., and Katherine L. Kirkman. “Management of ecological thresholds to re-establish disturbance-maintained herbaceous wetlands of the south-eastern USA.” Journal of Applied Ecology 46 (2009): 906–914. Nishihiro, Jun, et al. “Toward the restoration of a sustainable population of a threatened aquatic plant, Nymphoides peltata: Integrated genetic/demographic studies and practices.” Biological Conservation 142 (2009): 1,906–1,912. Normile, Dennis. “Bringing coral reefs back from the living dead.” Science 325 (2009): 559–561. Norton, David A. “Species invasions and the limits to restoration: Learning from the New Zealand experience.” Science 325 (2009): 569–571. Nowacki, Gregory J., and Marc D. Abrams. “The demise of fire and the ‘mesophication’ of forests in the eastern United States.” BioScience 58 (2008): 123–138. Palmer, Margaret A., and Solange Filoso. “Restoration of ecosystem services for environmental markets.” Science 325 (2009): 575–576. Redman, Charles L. “Environmental degradation and early Mesopotamian civilization.” Chap. 8 in The Archaeology of Global Change: The Impact of Humans on Their Environment, edited by Charles L. Redman et al. Washington, D.C.: Smithsonian Institution Press, 2004. Rey, Pedro J., et al. “Community-level restoration profiles in Mediterranean vegetation: Nurse-based vs. traditional reforestation.” Journal of Applied Ecology 46 (2009): 937–945. Schou, Majbritt Overgård, et al. “Restoring lakes by using artificial plant beds: Habitat selection of zooplankton in a clear and a turbid shallow lake.” Freshwater Biology 54 (2009): 1,520–1,531. Schulte, David M., et al. “Unprecedented restoration of a native oyster metapopulation.” Science 325 (2009): 1,124–1,128. Stokstad, Erik. “Oysters booming on new reefs, but can they survive disease?” Science 325 (2009): 525. Stone, Richard. “Nursing China’s ailing forests back to health.” Science 325 (2009): 556–558. Tennesen, Michael. “Black gold of the Amazon.” Discover, April 2007, 46–52. Vieira, Daniel M., et al. “Agro-successional restoration as a strategy to facilitate tropical forest recovery.” Restoration Ecology 17 (2009): 451–459. Willis, K. J., et al. “How ‘virgin’ is virgin rain forest?” Science 304 (2004): 402–403. Witmer, M. C., and A. S. Cheke. “The dodo and the tambalacoque tree: An obligate mutualism reconsidered.” Oikos 61 (1991): 133–137.

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rivers, streams, ponds, and lakes  Most of the water in the smallest creeks comes from underground aquifers, often from springs. Rainfall contributes to creeks only briefly after heavy rain events. When two of the smallest (first-order) creeks converge, they form a second-order creek. Of the 3.2 million miles (5.2 million km) of streams and rivers in the United States, half consist of first-order streams and 85 percent are first- to third-order. The Columbia River is a ninth-order river, and the Mississippi is a tenth-order river. The major drainage basins in the United States are the following: ●●

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Atlantic and Gulf Coastal system, in which the major rivers drain into the Atlantic Ocean and the Gulf of Mexico Great Lakes system, which drains into the Atlantic Ocean through the St. Lawrence River Rio Grande system, in which major rivers (the longest of which is the Rio Grande) drain into the Gulf of Mexico Mississippi River basin, in which the rivers of most of the central United States join to form the Mississippi River, which drains into the Gulf of Mexico Red River basin, in which water from Minnesota and the Dakotas enters a river that ultimately drains into Hudson Bay Colorado River basin, in which several rivers of the American West join to form the Colorado River, which drains into the Gulf of California Great Basin system, most of whose rivers do not reach the ocean Columbia River basin, in which several rivers on the landward side of the Cascades join to form the Columbia River, which drains into the Pacific Ocean Pacific Coast system, in which the rivers drain into the Pacific Ocean, many of them through San Francisco Bay

With each increase in order, the creek or river undergoes changes such as the following: ●●

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The average velocity of the water increases. The most rapid water is in the middle of the creek or river, because the drag imposed by rocks, soil, and vegetation slows down the water near the banks. The water may become cooler, because the average depth of the water increases. The oxygen content of the water may increase, if bubbles of air enter the water through the action of waterfalls or rapids.

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466 rivers, streams, ponds, and lakes  466 In a large river, especially if it is broad and shallow, the temperature may have risen and oxygen content decreased, due to the accumulation of eroded soil and the microbial life that comes along with it. Creeks may form ponds, and rivers may form lakes, on their way to (usually) the ocean. Therefore, rivers, streams, ponds, and lakes offer a great diversity of microhabitats in which different aquatic species of plants and animals live. Creeks experience frequent floods, which temporarily disturb the ecological communities. In contrast, lakes may experience very stable conditions for long periods. One of the major differences between different freshwater habitats is the nutrient content of the water. Oligotrophic water has clear water because it contains very few dissolved nutrients and therefore has few suspended single-celled organisms. Most of the nutrients are within the cells of organisms. The low level of nutrients is associated with the lack of suspended silt and clay. Eutrophic water, in contrast, has turbid water because abundant nutrients promote the growth of single-celled organisms, and the water may also contain silt and clay. Despite the abundance of nutrients, eutrophic habitats may have lower biodiversity because a few species of algae and other protists may dominate the food web. The abundance of single-celled organisms uses up much of the dissolved oxygen. Eutrophic habitats often have slower and warmer water, which holds less oxygen than cool water. In many cases, freshwater habitats may be eutrophic because of human influences. Wastewater, even when treated, may contain abundant nutrients. Sources of these nutrients include: ●●

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Nonpoint sources. Soil and organic material from all along the riverbanks, which often have farms and ranches, may promote eutrophic conditions. Farms frequently have fertilizer runoff, especially when chemical fertilizers are heavily used. Ranches and concentrated animal feeding operations (CAFOs) may produce an immense amount of animal waste, which is rich in nutrients. Point sources. Municipalities send storm water and sewage to defined locations on riverbanks. In nearly every American municipality, the sewage is treated; the solid material (sludge) ferments before being disposed of, and bacteria break down organic molecules in the dissolved material (effluent), which is also exposed to oxygen by various mechanical means. The purpose of sewage treatment is to eliminate potentially dangerous bacteria. Older municipali-

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first entry ties have combined water sources in which the storm water and treated effluent come together. Newer municipalities may have the storm water, which does not need treatment, separate from the effluent. The advantage of the newer system is that floodwater generally cannot overwhelm the sewage treatment system. Nutrients from human activity often cause eutrophication, which is the artificial production of eutrophic conditions. Eutrophication causes freshwater habitats to be very green, the surface layers filled primarily with cyanobacteria. These photosynthetic bacteria can fix their own nitrogen compounds from atmospheric nitrogen gas, and the nitrogen content of the water is not a limiting resource to their growth. It is primarily phosphorus (from soaps and detergents, as well as from human wastes) that causes eutrophication. Eutrophication results in freshwater habitats that are typically far more eutrophic than any conditions found in the wild. While cyanobacteria predominate in conditions of eutrophication, most unaltered freshwaters have food webs based on eukaryotic photosynthetic protists such as desmids and diatoms. Single-celled animal-like protists and small floating animals such as rotifers eat the algae. Small invertebrates, such as copepod crustaceans, eat the smallest animals. Larger invertebrates and small fishes eat them. The top predator may be large fishes, such as sturgeons or paddlefishes, or a fish-eating mammal such as the otter. There are many examples of insects that have aquatic larvae and terrestrial or aerial adults. These include stoneflies; caddisflies, whose larvae construct protective cases from sand and organic litter; dobsonflies, whose larvae are called hellgrammites; mosquitoes; dragonflies and damselflies; and some beetles, whose larvae are called water pennies. Dragonfly nymphs are large enough that they eat small fishes. The insects may spend several years in a larval stage and emerge in adult form for a relatively brief mating period, which in the case of mayflies is only a single day. While the larvae are important prey (and are often predators themselves) in the water, the adults are important prey items for terrestrial animals such as birds. In this way, the streams and rivers help to support the food web of the surrounding land. Mammals such as otters, and birds such as kingfishers, bald eagles (Haliaeetus leucocephalus), and ospreys (Pandion haliaetus) hunt in the water by diving. The dipper or water ouzel (Cinclus mexicanus) may walk right into the water. Some

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rivers, streams, ponds, and lakes  467 animals, such as crayfish, live both underwater and in tunnels in wet soil on the margins of creeks and ponds. Beavers are important keystone species because they often build dams that transform creeks into ponds. They use their front teeth as chisels to chop down trees, often ones like cottonwood or alder that have soft wood, and they construct dams by interweaving the trunks or branches. They live in beaver lodges that are above the water level but have an underwater entrance. Plants and animals that live underwater have adaptations allowing them to obtain carbon dioxide and oxygen, respectively. ●●

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Underwater plants often have very finely dissected leaves, such as those of the parrot feather (Miriophyllum aquaticum), or very thin leaves, such as those of the Elodea canadensis. Emergent plants, including some buttercups, may produce thin or dissected leaves underwater but larger, thicker leaves on their stems above water. The very high ratio of surface area to leaf volume allows rapid absorption of bicarbonate ions and dissolved carbon dioxide, without any risk of excessive water loss as would occur with such leaves in the air. Other emergent plants, such as Nelumbo lutea water lilies, Typha angustifolia cattails, and Pontederia cordata pickerelweeds, have underwater stems that spread along the bottom of the pond and from which leaves and flowering stems emerge. These plants may have tissues that conduct air down into the submerged stems and roots. Animals have adaptations that allow their blood to absorb oxygen from the water. Gills of underwater animals such as fishes bring their blood in close contact with the oxygen dissolved in the water. Segmented Tubifex tubifex worms embed themselves in sediments and wave their tails in the water. The abundant hemoglobin in the tails, and the close contact with water that results from their movement, helps to absorb oxygen from water that may contain little of it. Turbellarian flatworms, which eat detritus and smaller animals and protists on the bottom of creeks and ponds, are small and flat, allowing the whole body to absorb scarce oxygen from the water.

Some plants and aquatic insects have adaptations that are unique to the air-water interface. Duckweeds (family Lemnaceae) are monocot flower-

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ing plants, each of which consists almost entirely of a tiny floating green plate. Wolffia duckweeds are the smallest seed plants. Some larger aquatic plants, such as water hyacinth (Eichhornia crassipes) and water lettuce (Salvinia molesta), float on the water. Water striders (bugs of the family Gerridae) are light enough that they can actually walk on the surface of the water without breaking the surface tension. Others, such as whirligig beetles (family Gyrinidae), are buoyant and float as they swim half in and half out of the water. The top half of the body is waterrepellent, and the top half of each eye is suited for aerial vision, while the bottom half is suited for underwater vision. Backswimmers (bugs of the family Notonectidae) swim upside down in the surface layer of water. Some air-breathing adult insects take air with them as they dive: Water boatmen (bugs of the family Corixidae) take a bubble of air with them on the underside of the body, while diving beetles (family Dytiscidae) hold air underneath their hard wing covers. Water scorpions (which are actually bugs, Nepa cinerea) and rat-tailed maggots (the larvae of the hoverfly, Eristalis tenax) have a hollow tube protruding from their abdomens that siphons air from above the surface while they feed underwater. Fishing spiders (genus Dolomedes) usually walk on the water’s surface in search of prey (which includes small fishes), but when they dive their bodies are surrounded by bubbles of air that allow them to breathe. Animals of streams and rivers have adaptations that allow them to move with or against the current. Many fishes are strong swimmers. Sculpins (fishes of several different families) brace themselves against the current by embedding their strong fins in the bottom of the creek. Freshwater mussels have larvae that are not strong enough to swim upstream. What is it that keeps the last freshwater mussels from washing out to sea? Freshwater female bivalves of the species Lampsilis perovalis produce floating clumps of larvae that look like small fishes. The clump remains attached to the mother by a thin line, causing the clump to move like a fish in the currents. When a predatory fish tries to eat the larvae, they hitch a ride on the fish and may thereby disperse upstream. Several other kinds of mollusks have a similar strategy. Several species of fishes are anadromous, that is, they hatch in streams, travel downriver to live in the oceans, then swim back upstream (often to the same stream in which they hatched) to fertilize or lay eggs. Most famous are the Chinook, coho, chum, and pink salmon of the Pacific Northwest (Oncorhynchus tshawytscha, O. kisutsh, O. keta, and O. gorbuscha). Chinook and sockeye salmon return to central Idaho, over 900 miles (1,400 km)

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468 rivers, streams, ponds, and lakes  468

first entry

Pond Plant and Mammal Species Scientific Name

Common Name

North America

Europe

Asia

Africa

Plants Cyperus papyrus

Paper sedge

Cyperus rotundus

Purple nut-sedge

Juncus effusus

Common rush

Juncus tenuis

x x

x

x

x

x

x

x

Narrow rush

x

x

Nelumbo lutea

American lotus

x

Nelumbo nucifera

Lotus

Nymphaea caerulea

Egyptian water lily

Phalaris arundinacea

Reed canary grass

x

Pontederia cordata

Pickerelweed

x

Sagittaria cuneata

Arumleaf arrowhead

x

Sagittaria sagittifolia

Arrowhead

Schoenoplectus acutus

Tule

x

Scirpus fluvatilis

River bulrush

x

Sparganium americanum

American bur-reed

x

Typha angustifolia

Narrow-leaved cattail

x

x

x

Typha latifolia

Broad-leaved cattail

x

x

x

Typha minima

Lesser cattail

Zizania aquatica

Wild rice

Zizania latifolia

Manchurian wild rice

x x x

x

x

x

x

x

x x x

Mammals Aonyx capensis

African clawless otter

Castor canadensis

American beaver

Castor fiber

European beaver

Lontra canadensis

American river otter

Lutra lutra

European otter

Ondatra zibethicus

Muskrat

from the ocean, climbing nearly 7,000 feet (2,100 m) from the Pacific Ocean in the process. Streams that widen and in which the water flows slowly are ponds (see table above). In these ponds, emergent plants around the edges create a littoral zone. Water that is too deep for emergent plants, in the middle of the pond, forms the limnetic zone. Because the water moves more slowly than in a stream, partially decomposed organic matter and

xviii+598_Biodiversity_F.indd 468

x x x

x

x

x

x

x

sediments accumulate in the littoral zone. Over time, during the process of stream succession, the littoral zone moves out toward the middle of the pond, and the limnetic zone may eventually be filled in. Such a pond then becomes a marsh or, if trees grow in it, a swamp. After the most recent ice age, chunks of ice were left behind the retreating glaciers and formed ponds in heavy clay soil. These ponds, also called prairie

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rivers, streams, ponds, and lakes  469 potholes, frequently had no creeks flowing into or out of them and received limited water from underground and from rain. Because the water contained few nutrients and because tundra species (including sphagnum moss) colonized them, most of these ponds developed into bogs, which may be very different from regular ponds. If a lake is large enough, the water may become stratified, with warm oxygenated water at the top and cool, less-oxygenated water at the bottom. Nutrients tend to accumulate in the bottom layer as well. The layers are frequently mixed, whether by wind or by the flow of river water into and out of the lake. In addition, in lakes in the temperate climatic zone, there may be an annual overturn of water. This occurs because water is most dense at about 40°F (4°C). As ice melts in the spring, the water becomes denser, and when it exceeds 40°F it sinks toward the bottom of the lake, forcing the bottom water up. The world’s oldest and deepest lake is Lake Baikal in Siberia, with an average depth of 2,440 feet (744 m); the greatest depth is 5,380 feet (1,642 m). More than 80 percent of the 1,550 species and varieties of animals in the lake live nowhere else. The dominant species of zooplankton is a species found nowhere else. Lake Baikal is the home of the Baikal seal or nerpa (Phoca sibirica), one of only three freshwater seal species. Most large lakes persist for a long time, because sediments do not build up very much within them. The inflow and outflow of river water keeps them cleaned out. Large reservoirs, created by large dams, accumulate sediment, since the outflow of water is either through tunnels with turbines or over the spillway. There are more than 36,000 dams in the world

xviii+598_Biodiversity_F.indd 469

that are greater than about 50 feet (15 m) in height, and they collectively impound 2,050 cubic miles (8,400 cubic km) of water. This is seven times the volume of all the rivers in the world. Artificial reservoirs are therefore collectively important enough to affect the hydrological cycle of the entire planet. See also bogs, life in; hydrological cycle; insects; keystone species. Further Reading Allan, J. David. “Landscapes and riverscapes: The influence of land use on stream ecosystems.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 257–284. Boulton, Andrew J., et al. “The functional significance of the hyporheic zone in streams and rivers.” Annual Review of Ecology and Systematics 29 (1998): 59–81. Carpenter, Stephen R., et al. “Cascading trophic interactions and lake productivity.” BioScience 35 (1985): 634–639. Dudgeon, D., et al. “Freshwater biodiversity: Importance, threats, status, and conservation challenges.” Biological Reviews 81 (2006): 163–182. Haag, Wendell R., et al. “An extraordinary reproductive strategy in freshwater bivalves: Prey mimicry to facilitate larval dispersal.” Freshwater Biology 34 (2006): 471–476. Paul, Michael J., and Judy L. Meyer. “Streams in the urban landscape.” Annual Review of Ecology and Systematics 32 (2001): 333–365. Persson, Lennart, et al. “Density dependent interactions in lake ecosystems: Whole lake perturbation experiments.” Oikos 66 (1993): 193–208. Keddy, Paul. Wetland Ecology, 2nd ed. New York: Oxford University Press, 2010.

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S seed  dispersal  Dispersal usually refers to the

a few species of plants have ballistic seed dispersal, that is, the fruits explode when touched by an animal or jostled by the wind. Jewel weeds (genus Impatiens) has spring-loaded tissue inside of its fruits, while squirting cucumbers (Ecballium elaterium) have fruits that hold in water pressure. Some seeds and fruits float in the water. Because water always flows downhill, any upland plant species that relied solely upon water dispersal would eventually fi nd all of its seeds out in the ocean. But many of these species rely on wind as well as water. Other water-dispersed seeds are transported back uphill during occasional storms. coconuts already live by the seashore. their seeds can float thousands of miles on ocean currents. these seeds often land on sandy shores that have poor soil. coconut seeds have a large and rich supply of food available to the tiny embryonic seedling inside. Some plants produce dry fruits that have prickles or barbs, which attach to mammal fur. cockleburs are a well-known example. in some cases, as with the puncture-vine, the fruit has sharp spikes that imbed in the soft feet of mammals or flightless birds. the unicorn plant, despite its name, has dry fruits with two long horns, which clasp onto the legs of animals or flightless birds. the seeds eventually fall out of the dry fruits in a new location. in all of these cases, the animal either attempts to scratch away the fruits or the fruits fall off of the animal. Puncture-vine seeds can even be transported by car tires. these adaptations are not often considered examples of coevolution, since few if any animals have evolved special adaptations to either facilitate the dispersal of these fruits or prevent them from attaching. Many fruits are highly attractive to animals because of their bright color, sugar content, and

transport of seeds from the parent plant to a new location. it can also refer to the transport of spores. transport of pollen from one plant to another is called pollination. it is important for seeds to disperse to new locations for at least two reasons: ●



if seeds did not disperse, they would grow into dense populations near the parent plant. Plants in these dense clumps would compete with one another for resources, such as light, water, and nutrients. Pests and diseases would also spread rapidly through such dense plant populations, particularly in the tropics, where pest and disease populations are not reduced each year by winter conditions. if plants remained in localized clumps, the entire clump might be destroyed by an ecological disturbance, such as a fi re or a flood. natural selection favors plants that disperse their seeds, not only because the genetic lineage will have a greater chance of survival by traveling to new locations, but such plants will also be able to spread quickly into newly disturbed areas.

Many plants rely on the wind to transport their seeds. the seeds themselves may have flat surfaces, such as the seeds of catalpa trees, or the seeds may be surrounded by a fruit that provides a thin, flat surface, as in the seeds of maple trees, whose surfaces function as glider wings. Dandelion seeds have a thin fruit covering that forms a delicate parachute. these adaptations would not be considered examples of coevolution, since the wind, not other organisms, have selected them. 470

xviii+598_Biodiversity_F.indd 470

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seed dispersal  471 ­ avors. The animals (particularly birds and mamfl mals) eat the fruits, but the seeds, which have hard seed coats, survive the passage through the intestines. The seeds emerge from the animal, having been transported to a new location and receiving a patch of fertilizer in which to begin growing. In many of these species, such as the wild persimmon, passage of the seed through an animal’s digestive tract may be necessary to soften the seed coat enough to allow germination to occur. In many plant species, it is the seed rather than the fruit that is soft and nourishing to animals. Many seeds have eliasomes, which are fat-producing structures on the seed coat. Ants carry the seeds from the ground, where they might otherwise be eaten by mammals or birds, and bury them in the nest, where they can eat the eliasome at their leisure. Once the ants have eaten the eliasome, the seed germinates in good soil, which has been aerated and fertilized by ants. These plants, in effect, pay the animals for the work of dispersing the seeds by providing them with food. However, they expend only as much as is necessary. Most wild fruits have much less pulp, relative to the seeds, than do domesticated fruits, which humans have bred to produce excessive amounts of pulp. Furthermore, the pulp of wild fruits attaches tightly to the seed. Therefore, it is much easier for the animal to just swallow the seeds than to spit them out. Domesticated fruits, in contrast, have seeds that are easily avoided by humans. Plants that produce soft fruits discourage animals from consuming fruits in which the seeds are not ready to germinate. This is the reason that unripe fruits are green, hard, starchy, and distasteful. Only after the seeds are mature will the fruit also mature, becoming colorful, soft, sugary, and fragrant. There is, however, competition among animals to eat the fruits as early as possible, that is, earlier than other animals. Animals may, therefore, eat fruits that are not quite ripe. The fruits, at this stage, contain astringent digestion inhibitors, which the animals counteract by ingesting clay. Some parrots consume unripe fruits and then congregate at exposed banks of earth to consume the avian version of kaopectate. (Kaopectate is the brand name of an antidiarrheal medication that was originally made from kaolin clay.) If the animal chews up the seeds along with the fruit pulp, the seeds are killed and dispersal fails. This is why animals that pick seeds out of a fruit and eat them—such as when squirrels eat bois d’arc seeds—are considered seed predators, not dispersers. In many cases, the seeds inside of soft fruits are poisonous. Seeds of several fruits in the rose family, for example, contain cyanide. This adaptation tips the balance of natural selection away from animals

xviii+598_Biodiversity_F.indd 471

that chew up the seeds and toward the animals that simply swallow them. In some plant species, the seed predator also functions in seed dispersal. Squirrels hoard caches of acorns for the winter, placing the hoards in different locations so that they do not lose an entire supply of food. This activity is therefore known as scatterhoarding. The squirrels eat many of the nuts but fail to locate all of them. These acorns germinate, having been dispersed to a new location by the squirrel. Some birds disperse the seeds of pines in this fashion. Cones of subalpine pines remain tightly closed and are sticky with resin; plundering squirrels cannot open them to get the seeds. Jays, however, can pry open the cones and take the seeds. The jays hide the seeds in rock crevices, often in locations at some distance from the parent tree. Some of these seeds germinate into new pine trees. Most of the plant species that live on oceanic islands are the descendants of plants whose seeds can disperse long distances. Once the plants are on the island, however, natural selection may favor the loss of dispersal ability, because the plants reproduce more successfully by remaining on the island than by launching out once again over the seas. The dispersal of soft fruits and scatterhoarding are examples of coevolution, in which each partner provides resources to the other partner, even while investing primarily in its own reproductive success. See also coevolution; pollination. Further Reading Andresen, E., and D. J. Levey. “Effects of dung and seed size on secondary dispersal, seed predation, and seedling establishment of rain forest trees. Oecologia 139 (2004): 45–54. Cody, Martin L., and J. M. Overton. “Short-term evolution of reduced dispersal in island plant populations.” Journal of Ecology 84 (1996): 53–61. Corlett, R. T. “Frugivory and seed dispersal by vertebrates in the Oriental (Indomalayan) Region.” Biological Reviews 73 (1998): 413–448. Garrison, W. J., et al. “Ballistic seed projection in two herbaceous species.” American Journal of Botany 87 (2000): 1,257–1,264. Lengyel, S., et al. “Ants sow the seeds of global diversification in flowering plants.” Public Library of Science ONE 4 (2009): e5480. Levin, Simon A., et al. “The ecology and evolution of seed dispersal: A theoretical perspective.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 575–604. Levine, Jonathan M., and David J. Murrell. “The community-level consequences of seed dispersal patterns.” Annual Review of Ecology, Evolution, and Systematics 34 (2003): 549–574.

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472 seedless plants  472 Manzano, Pablo, and Juan E. Malo. “Extreme long-distance seed dispersal via sheep.” Frontiers in Ecology and the Environment 4 (2006): 244–248. Narbona, E., et al. “Explosive seed dispersal in two perennial Mediterranean Euphorbia species (Euphorbiaceae).” American Journal of Botany 92 (2005): 510–516. Sorenson, A. E. “Seed dispersal by adhesion.” Annual Review of Ecology and Systematics 17 (1986): 443–463. Tiffney, Bruce H. “Vertebrate dispersal of seed plants through time.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 1–30. Wenny, D. G., and D. J. Levey. “Directed seed dispersal by bellbirds in a tropical forest.” Proceedings of the National Academy of Sciences USA 95 (1997): 6,204–6,207.

seedless plants  Seedless plants are bryophytes (mosses and their relatives) and pteridophytes (ferns, horsetails, and club mosses, and their relatives). (Algae are sometimes considered to be seedless plants, but they are actually photosynthetic protists.) Seedless plants must live in moist environments on land, for one or both of these two reasons: ●●

●●

Vascular tissue is the plumbing system of higher plants. Vascular tissue consists of xylem, which brings water up from the soil to the leaves, and phloem, which carries nutrients (dissolved in water) throughout the plant. Bryophytes do not have vascular tissue; because they must soak up water rather than transporting it in vascular tissue, they must live in moist environments. Pteridophytes have vascular tissue. Both bryophytes and pteridophytes reproduce sexually by releasing sperm or similar cells that swim or are carried to eggs. This form of sexual reproduction can only occur in a wet environment, and this is why pteridophytes also must live in moist environments. When seed plants evolved, sexual reproduction could be carried out in the absence of a wet environment.

Because life began in water, the earliest plants were aquatic. The first plants that lived on land were seedless plants similar to those that are in moist terrestrial environments today. An analogous situation occurred with animals, in which the earliest animals on the Earth were aquatic, and the first animals that lived on land were restricted to moist environments. As with plants, this was due both to a reduced ability to survive dry conditions and to the inability to sexually reproduce in dry conditions. In both plants

xviii+598_Biodiversity_F.indd 472

first entry and animals, evolution has produced progressively more species that live in dry environments. Freshwater green algae, the ancestors of land plants, often live in shallow water, and shallow water frequently dries up. Algae that had adaptations that allowed them to continue to function when water became mud would be favored by evolution. The first land plants, as seen in the fossil record, were small plants in wetlands, consistent with this explanation. Nearly all organisms have a sexual life cycle in which a haploid phase alternates with a diploid phase. Cells with unpaired chromosomes are haploid; cells with paired chromosomes are diploid. A type of cell division known as meiosis separates chromosome pairs and produces haploid cells; in turn, some haploid cells come back together, in a process called fertilization, to restore the original diploid number. In animals, the haploid phase consists only of eggs and sperm. But in plants, the haploid (gametophyte) phase is multicellular. As green algae evolved into land plants, they diverged: ●●

●●

Some of them evolved into bryophytes, in which the gametophyte phase is relatively large and independent, while the diploid multicellular phase (the sporophyte) is relatively small and depends on the haploid cells to supply its needs. They reproduce when sperm swim through a film of water to eggs. None of these plants grows taller than a few centimeters. These plants were already established on the Earth by at least 350 million years ago. Some of them evolved into plants in which the sporophyte phase was relatively large and independent, while the gametophyte phase was relatively small and sometimes dependent on the diploid cells to supply its needs. These plants were the earliest known land plants. They lived in marshlike habitats during the Silurian period 435 million years ago, although a few fossil spores have been found from the previous Ordovician period. Some of their fossils have been so well preserved that the vascular pipes can actually be seen in rock cross sections. They were the ancestors of pteridophytes and seed plants.

The earliest land plants, in the swamps of the Silurian period, were only about a meter tall or less and were hardly more than branching stems with reproductive structures at the tips. They had no roots or leaves. They included: ●●

rhyniophytes, such as Cooksonia. They consisted mostly of branching stems that produced sporangia. Vascular tissue can be

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seedless plants  473

●● ●●

recognized in the fossil remains. The rhyniophytes apparently became extinct without descendants. zosterophylls. Some zosterophylls evolved into the ancestors of the club mosses. trimerophytes. Some trimerophytes evolved into the ancestors of horsetails, whisk ferns, and true ferns. These plants were common during the Silurian and Devonian periods. Their evolutionary descendants included large forest trees of the Carboniferous period (see below) as well as smaller plants, which are today’s ferns and fernlike plants.

By the Carboniferous period, many of these plants had grown very tall. Some of them, such as Lepidodendron, were relatives of modern club mosses, while others such as Calamitales were relatives of modern horsetails. Then as now, some ferns reached the size of small trees. Their leaves were long, narrow, and very simple. Their water pipes allowed them to grow tall, but their upward growth was limited by their inability to continue producing new wood. They dominated the Carboniferous swamps. They could only live in moist environments, such as swamps, because their sexual reproduction required sperm to swim through water, just as seedless plants do today. Therefore, the forests of the Carboniferous period were found only in swamps; the hillsides and dry plains were probably barren. Fortunately for these plants, swamp conditions were extremely widespread on Earth during the Carboniferous period. When the plants died, they did not completely decompose. The piles of organic matter that they produced constitute today’s coal deposits. Although coal itself contains no fossils, mineral inclusions (coal balls) often do. These coal balls provide most of the information that scientists have about these plants. Beginning in the Carboniferous period, seed plants started their evolutionary diversification and eventually dominated most of the Earth. In very

Approximate Number of   Species in Selected Groups   of Seedless Plants Group Mosses

Number of Species 12,000

Liverworts

8,000

Club mosses

1,200

Horsetails Ferns

xviii+598_Biodiversity_F.indd 473

30 20,000

few places on land do the seedless plants dominate (though the ocean is still the realm of seaweeds, including forests of giant kelp). Seedless plants, however, still have a fair measure of species diversity (see table). Though they primarily hide in the shade of the seed plants, they are still important to the biodiversity of the living world.

Diversity of Bryophytes Liverworts (division Marchantiophyta) are one of the bryophyte lineages. They are a separate lineage from all other plants. Their name refers to the flat, roundish, liver-shaped lobes of the gametophytes of some common species that grow on the surfaces of moist soil. Most liverwort species, however, have gametophytes with leaflike and stemlike structures. Because liverworts have no vascular tissue, their flat photosynthetic structures are not really leaves, and the stalks that support these structures are not really stems, although they may look like them. Liverworts can be distinguished from mosses (see below) because their leaflike structures are often lobed and have hairlike projections. They have rhizoids that look like tiny roots, but their function is to hold the plant in place rather than to absorb water, since they, also, have no xylem. Liverworts often live in wet areas and on rock surfaces, to which the rhizoids anchor them. It is the gametophyte phase that has the leaflike, stemlike, and rhizoid structures. Male gametophytes of liverworts produce sacs called antheridia underneath the caps of umbrellalike stalks. Each antheridium produces many sperm cells. Female gametophytes produce sacs called archegonia under the caps of their stalks. Each archegonium typically produces one large egg cell. Sperm (which have two flagella) emerge from the antheridia, swim down the male stalk, over the ground, and up the female stalk to an archegonium, through a layer of water from spring rains or snowmelt. The sperm cells enter the archegonium through an opening, and one of them fertilizes the egg cell. (In some liverworts, antheridia and archegonia are on the same gametophyte.) The egg cell, now a zygote (fertilized egg cell), develops into a sporophyte that contains a capsule (often football-shaped), which produces haploid spores and releases them into the wind. The spores, if they land on a suitable moist surface, grow into new gametophytes. Mosses (division Bryophyta) are another lineage of bryophytes. Like many liverworts, mosses can generally be recognized by the presence of leaflike and stemlike structures and rhizoids. Moss rhizoids, unlike those of liverworts, are multicellular. The rhizoids look like tiny roots, but their function is to hold the moss plant in place rather than to absorb

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474 seedless plants  474 water, since they have no xylem. Mosses often live in wet areas and on rock surfaces, to which the rhizoids anchor them. It is the gametophyte phase that has the leaflike, stemlike, and rhizoid structures. Many mosses have hydroid cells that are similar to xylem and can conduct water from the base to the tip of a gametophyte, though not as well as the xylem cells of vascular plants. Although they can metabolize and grow only under wet conditions, most mosses have the ability to tolerate complete and prolonged desiccation. The gametophytes usually grow together in clumps. Most mosses grow in shaded, moist conditions in forests and along waterways. Peatmoss (genus Sphagnum) forms thick mats on tops of bogs. Bog water is acidic and poor in nutrients. The mats keep the bog water cool, largely isolate it from oxygen, and contribute to its acidity. The few vascular plants that can tolerate these conditions grow with their roots in the mat of moss. Sphagnum bogs are widespread in the boreal forests. Male moss gametophytes produce antheridia at their tips. Each antheridium produces many sperm cells. Female gametophytes produce archegonia at their tips. Each archegonium typically produces one large egg cell. Sperm emerge from the antheridia, swim down the male stalk, over the ground, and up the female stalk to an archegonium, through a layer of water from spring rains or snowmelt. The sperm cells enter the archegonium through an opening, and one of them fertilizes the egg cell. (In some mosses, antheridia and archegonia are on the same gametophyte.) The egg cell, now a zygote (fertilized egg cell) develops into a long stalk, the sporophyte (see photograph). (The liverwort sporophyte, in contrast,

Mosses, which do not have roots or water-conducting tubes, grow low to the ground, where they absorb water. They release their reproductive spores into the wind from capsules at the end of stalks.  (Stanley A. Rice)

xviii+598_Biodiversity_F.indd 474

first entry does not do this.) The sporophyte stalk grows from, and is fed by, the female gametophyte. The stalk may extend several inches into the air. A capsule at the end of the stalk produces spores and releases them into the wind. The spores, if they land on a suitable moist surface, grow into new gametophytes. Hornworts are similar to mosses and liverworts, being distinguished by such features as the structure of their spores. They are the evolutionary lineage from which the vascular plants evolved.

Diversity of Pteridophytes Pteridophytes often superficially resemble bryophytes (as club mosses resemble mosses) but have important differences, such as the following: ●●

●●

The most visible phase of the life cycle is the sporophyte phase. The gametophytes are very small, living on or in the soil. The sporophytes have vascular tissue, which allows them to grow taller than any bryophytes.

Club mosses and quillworts (division Lycopodiophyta) are small plants that grow mainly in shaded, moist conditions (club mosses) or at the edges of lakes and ponds (quillworts). Club moss sporophytes are often branched and covered with small leaves (see photograph on page 475). Some Selaginella club mosses have an iridescent layer of cells that make their leaves appear deep blue, an adaptation that apparently helps them to absorb red light. Sporangia (often superficially resembling cones) grow at the tips of many of the branches and release numerous tiny spores into the air. If the spores land on a moist surface, they may germinate and grow into very small (but not microscopic) gametophytes. Gametophytes of some lycopods are photosynthetic and grow on the surface of the soil, while others grow underground and depend upon a symbiotic association with fungi to provide food. The male gametophytes release sperm, each with two flagella, which swim to a female gametophyte, where they enter the archegonia and fertilize the eggs. The resulting sporophyte grows from and quickly obliterates the female gametophyte. Quillwort sporophytes have long, narrow leaves that grow from an underground corm and among which the sporangia grow. Though modern club mosses are small plants, some of them were trees up to 100 feet (30 m) in height, such as the Lepidodendron of the Paleozoic era—the largest plants of the early Paleozoic forests. Horsetail (division Equisetophyta) sporophytes spread by underground rhizomes in wet areas. Single stems grow up out of the rhizomes, which branch out and absorb water and nutrients; they do

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seedless plants  475 row, suggesting the appearance of human hair. The fronds emerge from underground rhizomes and unfurl, resulting in the appearance of a “fiddlehead.” Staghorn ferns produce two kinds of fronds: flat basal fronds and large fronds that remind people of antlers. The rhizomes produce fibrous underground roots. Tree ferns produce trunks, but the trunks do not grow by producing new wood, as do the trees of seed plants. Instead, the trunks are reinforced by the growth of aboveground mats of roots. Because of this weak structure, most tree ferns do not grow more than about 20 feet (6 m) tall, though some grow up to 65 feet (20 m) in height. In some fern species, sporangia develop on the undersides of the fronds in regular patterns along the veins or the edges of the blades. In other fern species, sterile fronds are green and photosynthetic, while fertile fronds are covered with sporangia and do not produce blades (see figure). If a spore lands on a suitable surface, it germinates into a gametophyte, which is aboveground and green, though very inconspicuous. The male gametophytes release sperm, each with two flagella, which swim to a

Club mosses, such as this Selaginella plana, resemble mosses, but they have roots and water-conducting tubes.  (Forest and Kim Starr)

not produce an extensive root system. The hollow stems have segments that fit inside one another, not unlike drinking straws. Unlike seed plants, in which stems grow at the tips, horsetail stems can grow as each segment becomes longer. Whorls of needlelike leaves emerge from each segment, giving the whole stem the appearance of a bottle brush or the tail of a horse. Sporangia (often superficially resembling cones) grow at the tips of the branches and release numerous tiny spores into the air. If the spores land on a moist surface, they may germinate and grow into very small (but not microscopic) underground gametophytes. The male gametophytes release sperm, which swim to a female gametophyte, where they enter the archegonia and fertilize the eggs. The resulting sporophyte grows from and quickly obliterates the female gametophyte. Modern horsetails are relatively small (though some can reach almost 10 feet [3 m] in height), but during the Paleozoic era some horsetails such as Calamites grew much taller. True fern (division Pteridophyta) sporophytes produce leaves (fronds) that are often large and divided into many smaller surfaces connected by stalks that contain the vascular tissues. In Adiantum maidenhair ferns, the stalks are dark and nar-

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Many ferns produce spores on the undersides of their photosynthetic leaves. This fern, however, produces spores in reddish structures on fronds that are separate from the photosynthetic leaves.  (Stanley A. Rice)

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476 seedless plants  476

The fern Asplenium septentrionale grows over a wide area of North America and Europe, living in crevices on boulders, but is very rare in each location. In the Black Hills of South Dakota, there are only a few individuals, all of them on granite boulders near the base of Mount Rushmore.  (Stanley A. Rice)

female gametophyte, where they enter the archegonia and fertilize the eggs. The resulting sporophyte grows from and quickly obliterates the female gametophyte. Ferns are usually found in moist, shaded areas, although they can also grow in the cracks of rocks (see figure). Filmy ferns (family Hymenophyllaceae) have very thin leaves and grow where they are continually moistened by mist from waterfalls. But, as with other pteridophytes, many ferns are restricted to moist areas mainly by the gametophyte stage. The sporophytes can be quite resistant to dry conditions. Bracken fern (Pteridium aquilinum) has spread extensively in acidic soils around the world and fills whole fields (where gametophytes could not survive) just by the growth of its rhizomes. Fronds of Pleopeltis polypodioides, the resurrection fern that grows on tree branches in the southeastern United States, can expand and become green upon exposure to water after shriveling in dry conditions. The staghorn fern Platycerium veitchii, which also lives on

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first entry tree branches, even has the same kind of photosynthesis that is found in succulents. Some ferns, such as the climbing fern Lygodium, spread when the tip of a frond touches the ground and grows into a new plant. Ferns of the genus Salvinia and Azolla float on the surface of water; some of them have become invasive species, covering the surfaces of rivers. Azolla ferns have symbiotic cyanobacteria that fix nitrogen into fertilizer; Azolla ferns growing in plots of aquatic crops such as taro act as a natural fertilizer. Whiskferns (division Psilophyta) and the adder’s-tongue ferns (Ophioglossophyta) are lineages of pteridophytes that were once classified with the true ferns. Like horsetails, they are relatively small plants that grow from underground rhizomes; in whiskferns, these rhizomes serve in place of roots. The aboveground stems branch and produce sporangia, which release numerous tiny spores into the air. If the spores land on a moist surface, they may germinate and grow into very small (but not microscopic) gametophytes. Unlike fern gametophytes, they grow underground and depend upon a symbiotic association with fungi to provide food. The male gametophytes release sperm, each with several flagella, which swim to a female gametophyte, where they enter the archegonia and fertilize the eggs. The resulting sporophyte grows from and quickly obliterates the female gametophyte. Genus Psilotum does not produce leaf blades, and the others produce just one leaf at a time. Despite its superficial resemblance to some of the earliest land plants (such as Rhynia), Psilotum evolved from the fern lineage. See also seed plants. Further Reading Conard, Henry S., and Paul L. Redfearn, Jr. How to Know the Mosses and Liverworts. Dubuque, Iowa: William C. Brown, 1979. Hebant, C., and David W. Lee. “Ultrastructural basis and developmental control of blue iridescence in Selaginella leaves.” American Journal of Botany 71 (1984): 216–219. Holtum, J. A. M., and K. Winter. “Degrees of crassulacean acid metabolism in tropical epiphytic and lithophytic ferns.” Australian Journal of Plant Physiology 26 (1999): 749–757. Gensel, Patricia G. “The earliest land plants.” Annual Reviews of Ecology, Evolution, and Systematics 39 (2008): 459–477. Graham, Linda E., Martha E. Cook, and J. S. Busse. “The origin of plants: Body plan changes contributing to a major evolutionary radiation.” Proceedings of the National Academy of Sciences USA 97 (2000): 4,535–4,540.

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seed plants  477 Kenrick, Paul, and Peter Crane. “The origin and early evolution of plants on land.” Nature 389 (1997): 33–39. Moran, Robbin C. A Natural History of Ferns. Portland, Ore.: Timber Press, 2004. Niklas, Karl J. The Evolutionary Biology of Plants. Chicago: University of Chicago Press, 1997. Qiu, Y. L., et al. “The deepest divergences in land plants inferred from phylogenomic evidence.” Proceedings of the National Academy of Sciences USA 103 (2006): 15,511–15,516. Shear, William A. “The early development of terrestrial ecosystems.” Nature 351 (1993): 283–289.

seed plants  Seed plants are plants that have vascular tissue and produce pollen and seeds, as explained below: ●●

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Vascular tissue. Vascular tissue consists of xylem and phloem. Xylem tissue conducts water up from roots into stems and leaves. Phloem tissue conducts water with sugar and other organic molecules, usually down from the leaves where the sugar is made to the roots. Some such as ferns also have vascular tissue. Roots, stems, and leaves are defined partly by the presence of vascular tissue. Mosses and their relatives do not have vascular tissues and do not have true roots, stems, or leaves. Because of vascular tissue, seed plants are well adapted to life on dry land. Pollen. Pollen grains contain one or more sperm nuclei inside a hard protein coat that protects the sperm and other male cells while they are transported through the air by the wind or by pollinators. In seedless plants, sperm must swim through layers of water from one plant to another. Because pollen carries sperm through the air, seed plants are well adapted to life on dry land. Seeds. Seeds contain an embryonic plant and a food supply, surrounded by a protective coat. Because the embryo is already partly grown and has a food supply, a plant can germinate from a seed and grow quickly, whereas seedless plants must begin their growth from single spores.

Most species of eukaryotes have life cycles in which meiosis alternates with fertilization. Meiosis eventually produces haploid eggs and sperm that fuse together during fertilization. Plant life cycles differ from those of protists, animals, and fungi by having a multicellular haploid phase called the gametophyte stage. The gametophytes produce eggs

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and/or sperm. The haploid structures of the simplest land plants, which evolved earliest, live in water or moist soil. In seed plants, however, the male gametophytes are pollen grains, which contain sperm and travel through the air from one plant to another; the female gametophytes remain within the immature seed. Pollen grains land on female tissue and germinate, producing pollen tubes that grow toward the female gametophytes. Sperm nuclei, instead of swimming through a layer of water in moist soil, travel through pollen tubes. The fertilization of egg and sperm nuclei produce a zygote, which is the beginning of the diploid, or sporophyte, phase of the plant life cycle. Seeds contain, feed, and protect embryonic sporophytes. The two major groups of seed plants are the gymnosperms and the angiosperms.

Gymnosperms Gymnosperms constitute a broad category that includes all extant seed plants that are not flowering plants, as well as many extinct forms. It is, therefore, not a monophyletic category. In gymnosperms, pollen grains usually develop inside of small male cones, and seeds often develop inside of larger female cones. Seeds of gymnosperms (Greek for “naked seed”) develop without being surrounded by parental tissue. The first gymnosperms evolved during the Paleozoic era. The earliest gymnosperms were Elkinsia and Archaeosperma, which appeared late in the Devonian period. Gymnosperms remained a relatively minor component of the forest vegetation during the Carboniferous period, when seedless plants grew to a very large size, such as tree-sized club mosses. During the Permian period, as cooler and drier conditions spread, the large seedless trees declined in abundance, and gymnosperms dominated the forests. Among these gymnosperms were the trees known as Cordaites. Two modern groups of gymnosperms, the conifers and the cycads, evolved during the Permian period. Also common in the late Mesozoic era were seed ferns (pteridosperms), which were not ferns and were probably not related to modern gymnosperms. In the cooler, drier conditions of the Mesozoic era, gymnosperms (especially conifers and cycads) dominated the forests of the Triassic and Jurassic periods. Many of the conifers resembled the modern Norfolk Island pine, which is not really a pine. The Wollemi pine, which is also not really a pine, was thought to be extinct until it was discovered in Australia in 1994. True pines and their relatives also evolved during the Mesozoic. Another group of Mesozoic gymnosperms was the bennettitalean plants. The details of their leaf

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and wood anatomy, as well as of their reproductive structures, suggest that they may have been the ancestors of the flowering plants. Some bennettitalean plants had female conelike structures surrounded by male reproductive structures inside of bracts, which is very similar to the structure of a flower. When the flowering plants evolved at or before the beginning of the Cretaceous period, they displaced the gymnosperms from the tropical areas. Modern gymnosperms spread during the Cenozoic era to their present habitats. Modern gymnosperms include these groups: ●●

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Conifers. Most conifers have stiff needlelike or scalelike evergreen leaves. Some primitive conifers, such as the podocarps of New Zealand and South America, and the auracarians of Chile, are found in the Southern Hemisphere. Most modern conifers are junipers, cypresses, pines, spruces, firs, hemlocks, and larches. Pines evolved during the Mesozoic era but have spread extensively since, especially in cool regions with poor soils. Cycads. Cycads look like small palm trees. They produce seeds on specialized leaves rather than in cones. Ginkgoes. There is only one modern species of ginkgo (the maidenhair tree, Ginkgo biloba) that closely resembles ginkgoes that lived millions of years ago. This species may have been saved from extinction by Chinese monks who grew them in monasteries. Ginkgoes have leaves with veins that diverge rather than branching out. They produce seeds singly on stalks rather than inside of cones. Gnetales. This is a loosely defined group of plants with gymnosperm reproductive structures, some of which have thin, flat leaves that resemble those of flowering plants. One member of this group is the desert ephedra bush.

Angiosperms Angiosperms (the flowering plants) are one of the largest groups of plants, with at least 260,000 living species in 453 families. Angiosperms live in nearly every habitat except the deep oceans. They range in size from large trees to tiny floating duckweeds. Despite their tremendous diversity, angiosperms are a monophyletic group, which means that they all evolved from a common ancestral species. The major lineages of the angiosperms are as follows: ●●

basal angiosperms, which include plants such as magnolias, water lilies, and butter-

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●● ●●

cups, whose flowers often have many separate parts monocots, such as grasses and lilies eudicots, which include most of the other angiosperms, such as roses, sunflowers, and oak trees

Angiosperms have flowers, which facilitate the transport of pollen to the immature seeds and fruits, which facilitate the dispersal of seeds to new locations. Extensive coevolution between flowering plants and animals (such as pollinating insects and mammals that disperse fruits) has contributed to the explosive speciation of flowering plants and animals that has occurred since the beginning of the Cretaceous period. See also cladistics; coevolution; conifers; flowering plants (angiosperms); seedless plants. Further Reading Baskin, Carol C., and Jerry M. Baskin. Seeds: Ecology, Biogeography, and Evolution of Dormancy and Germination. San Diego: Academic Press, 2001. Bewley, J. D., M. Black, and P. Halmer, eds. The Encyclopedia of Seeds: Science, Technology, and Uses. Oxford, U.K.: Oxford University Press, 2006. Henry, Robert J. Plant Diversity and Evolution: Genotypic and Phenotypic Variation in Higher Plants. Oxford, U.K.: Oxford University Press, 2005. Kesseler, Rob, and Wolfgang Stuppy. Seeds: Time Capsules of Life. Richmand Hill, Ont.: Firefly Books, 2006. Leubner, Gerhard. “The seed biology place.” Available online. URL: http://www.seedbiology.de. Accessed May 16, 2011. Museum of Paleontology, University of California, Berkeley. “Introduction to the Bennettitales.” Available online. URL: http://www.ucmp.berkeley.edu/seed plants/bennettitales.html. Accessed May 16, 2011. Richardson, Sarah. “Seeds: How flowering plants beat out the competition on ancient Earth.” Discover, October 2006, 36–41. Wollemi Pine International. “The Wollemi Pine.” Available online. URL: http://www.wollemipine.com. Accessed May 16, 2011.

sexual selection  Sexual selection is the evolu-

tionary selection of characters that enhance reproductive success rather than (even at the expense of) survival. The individuals in which the characteristic is well developed will reproduce more often and leave more offspring than individuals in which the characteristic is absent or less well developed. Sexual selection is similar to natural selection, in that a characteristic evolves because it causes the

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sexual selection  479 individuals that possess the trait to leave more offspring than individuals that do not possess it. The difference is that sexual selection favors characteristics that directly enhance reproductive success rather than characteristics that enhance it indirectly through survival or obtaining resources. Charles Darwin proposed natural selection as the major mechanism of evolution in his world-changing 1859 book On the Origin of Species by Means of Natural Selection. He also proposed sexual selection in his 1871 book The Descent of Man and Selection in Relation to Sex. Sexual selection may be responsible for even more of the biodiversity in the world than is natural selection. This is because in natural selection, certain adaptations work and others do not, whereas in sexual selection, almost anything can happen.

Sexual Selection in Animals In most animal species, males can produce more offspring than can females. This is partly because sperm cells are small and cheap, while egg cells are large and expensive. In animals with external fertilization, such as most fishes, this may be almost the entire difference in reproductive cost between males and females. In species with internal fertilization (such as most terrestrial vertebrates), at least part of the embryonic development occurs within the body of the female. Bird and reptile eggs are relatively large by the time the female lays them. In species with live birth (vivipary), it is the female in which embryonic development occurs. In most animal species in which newborns receive parental care, it is the female that provides a disproportionately large amount of that care. Sexual selection can operate at the level of the reproductive cell or of the reproductive individual, as in these examples: Sexual selection upon sperm. In many animal species, males produce millions of sperm, while females produce far fewer eggs. This can lead to an intense selection process occurring upon the sperm themselves. In humans, very few of the many millions of sperm reach the egg. This is why a sperm count of 50 million, although that sounds like a large number, may indicate infertility.

metabolic genes that promote sperm success also promote the vigor of the offspring. Sexual selection has not only favored the production of strong sperm but also the production of chemicals in the semen that partially suppress the woman’s immune response. Selection for successful sperm is a very important part of reproductive success. Each sperm is the product of a long series of cell divisions, each one an opportunity for mutations. There are therefore many mutant sperm that need to be “weeded out.” This explanation seems inadequate to explain all of the characteristics of sperm cells in all animal species. No convincing explanation has yet been offered for why the sperm of Drosophila bifurca, a species of fruit fly that is about one-20th of an inch (1 mm) long, can have tails almost two inches (6 cm) long, as described by evolutionary biologists Adam Bjork and Scott Pitnick. Sexual selection at the individual level. Because one male can produce so many sperm, and since in many animal species the act of mating is the male’s only contribution to the success of the offspring, a female animal cannot typically increase her reproductive success by mating more often. Therefore, it is usually males that compete with other males for access to females; it is females that choose which males they allow to fertilize their eggs. Females may choose among males on the basis of genetically based characteristics that have no connection with the quality of the male. According to the “sexy sons” hypothesis, females in a species may choose a male with any characteristic, perhaps an outlandish color pattern. The sons of these females will also have this characteristic, which will enhance their chances of being chosen by females in the next generation. Evolutionary theorist R. A. Fisher first pointed out that this could result in a positive feedback loop of runaway sexual selection. Females may also choose among males on the basis of genetically based characteristics that indicate the quality of the male: ●● ●●

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The acidic environment of the vagina kills many sperm. The sperm must also be strong swimmers to climb up through the cervix into the uterus. Because the sperm are genetically different from the cells of the woman’s body, the woman’s immune system begins to launch an attack on the sperm.

Selection of strong sperm may also result in the selection of strong offspring, because many of the

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The best genes may be those that allow males to obtain resources most effectively. The best genes may be those that allow resistance to parasites and diseases. Because parasites can evolve so much more rapidly than their hosts, most animal species are in a continual race to keep ahead of their parasites.

There are many fitness indicators that females can use to choose the best males. A fitness indicator is any trait that reliably displays the strength of the state of health of the male. A healthy male is likely to be superior in resource acquisition and

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480 sexual selection  480 in resistance to parasites, therefore likely to have higher potential fitness. A fitness indicator must, therefore, be expensive—and the more expensive it is, the better a fitness indicator it is. This is the “handicap principle” proposed by evolutionary biologist Amotz Zahavi. Evolutionary biologists William Hamilton and Marlene Zuk proposed that the most valuable fitness indicators are those that show the male to be free from parasites. Fitness indicators include: ●●

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A male that defends a large territory in prime quality habitat not only has more resources to offer to the female but is probably healthier and therefore able to drive away other males. It is not only expensive for the male to obtain and defend the territory, but to advertise it to females. A male mockingbird may sing all day for several weeks, which uses a lot of energy and makes him noticeable to predators. Bodily ornamentation is another fitness indicator. Consider a bird species that uses colored feathers as fitness indicators. Any male, even an inferior one, can (potentially) produce a few small colored feathers, but only a healthy one, free of parasites, is likely to produce many long colorful feathers. High testosterone levels, which enhance aggression in birds and mammals, also decrease the function of the immune system. The males that manage to have both the longest, most colorful feathers as well as the most aggressive territorial defense may be able to leave the most offspring. Feathers will continue to evolve to be longer and more colorful until the feathers become too expensive or burdensome. In many bird species, male ornamentation consists of only a few feathers or a crest, but in some, such as peacocks and birds of paradise, the ornamentation is so excessive that it constitutes a significant drain of resources and puts the male in greatly enhanced danger of attack by predators. Researchers such as evolutionary biologist Malte Andersson have experimentally augmented the feathers of some males and found that the males with artificially long feathers have more offspring. In many bird species, males congregate in leks to display their plumage and their mating dances, and females stroll around and choose from among them. Symmetry is a fitness indicator in many species, including humans, who show a preference for faces and bodies that are sym-

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first entry metrical. Poor health often results in asymmetry between the right and left sides of a vertebrate. Expensive fitness indicators among mammals include antlers (which in the now-extinct Irish elk could reach more than six feet [2 m] in expanse). Natural selection can put a stop to sexual selection, but not before excesses of ornamentation, some of them bacchanalian, are produced. The more expensive the better, up to a point, because if the ornamentation were cheap, less healthy males could cheat by producing an ornament that merely made them look healthy. Aside from being expensive, and being truthful representations of health, fitness indicators may be arbitrary, as reflected in the tremendous diversity of feather ornamentation and courtship dances among the more than 10,000 bird species. Once fitness indicators come into existence, as a result of sexual selection, they can serve as reproductive isolating mechanisms that help to separate one population into two. This can lead to speciation, when males with novel traits are chosen by females with a preference for those same novel traits. In many animal species, sexual selection has produced particularly marked characteristics that facilitate competition between males: ●●

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Size dimorphism. In many animal species, the male is larger than the female even though it is the females, not the males, that have most of the costs of reproduction. Large size gives males a competitive advantage in fighting with one another. Weapons. The same antlers that serve as fitness indicators for female choice also serve as weapons for fighting other males. Impulsiveness. In most species, it is the males that are more impulsive, and sometimes more violent. This is why, as Darwin noted in 1871, it is usually males (even among the invertebrate animals) that are, as he said in his inimitable Victorian prose, more “pugnacious” than females. In their hurry to mate, males can sometimes be absurdly undiscriminating: Male turkeys, for example, will attempt to mate with a replica of a female turkey head. Interference with the reproduction of other males. There are numerous instances in which males interfere with the opportunity for other males to inseminate females. In some stick insects such as Necroscia sparaxes, the male will copulate with the female for weeks at a time, thus keeping rival males away. Whether in flies or in

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sexual selection  481

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­ rimates, males may have very large reprop ductive organs that deliver a large amount of sperm. This helps to outcompete the sperm that a previous male may have left. Male voles produce more sperm if there are other males in the vicinity than they do if they are alone. The males of some species have penises with bristles, which are believed to scrub away sperm left by other males. In other cases, males produce secretions that plug up the female’s reproductive tract after he has mated with her, thus preventing the sperm of other males from entering. However, the males have also evolved the ability to remove the plugs inserted by other males. Evolutionary biologist Rebecca Dean and colleagues explain that when young or old males copulate, they may not be successful at producing offspring but may succeed in keeping other males from copulating. Stealth. In many cases, males have evolved to be stealthy in their approach to females. In some salamanders, such as Plethodon jordani, the female follows the male until the male drops a spermatophore, a structure that contains sperm; the female then sits on the spermatophore and receives the sperm. Sometimes a third male will intrude between the couple, waddle along as if he is a female, and then when the first male drops his spermatophore, the second runs off with the female. In some fishes, some males imitate females, infiltrate themselves into the harems controlled by dominant males, and mate with some of the females. Perhaps the ultimate example is when certain male bats (Myotis lucifugus) creep around amidst hibernating females and inseminate them. Chemical components of semen. Some male houseflies even produce semen that contains proteins that reduce the female’s interest in copulation—after he has finished with her, of course. This reduces the chance that she will accept the advances of another male. In some cases, the compounds in the semen are even slightly poisonous. In one experiment, in which male flies were allowed to evolve in competition but female flies were not, the semen from the male flies actually killed the females.

Male-male competition may in some cases have promoted speciation. In dragonflies and damselflies, males clasp females behind their heads to mate with them, thus keeping other males away. Their penises scrub out the sperm of previous males. This pro-

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cess can be so violent that the females get severely injured. But the post-reproductive survival of the female does not matter to the male. According to evolutionary biologist Ola Fincke, the female evolutionary response to this conflict of interest may have been new shapes and colors, which make it more difficult for the males to recognize the females. For animals with either monogamous or harem mating systems, in which the male can be reasonably confident of his exclusive access to the female, males have small reproductive organs. Gorilla males, for example, have penises even smaller than those of some ducks. In these instances, the male reproductive investment may be completed upon successful copulation, and thus the male may be expendable. In the cases of many spiders and praying mantises (Mantis religiosa), females often eat the males—in the case of the mantis, even while copulation is occurring. There are cases in which the males have the larger reproductive investment, and females choose among them. Females may provide eggs to males, who take care of them; often, males receive eggs from more than one female: ●●

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In the rhea (Rhea Americana), a South American bird similar to the ostrich, the male incubates the eggs and takes care of the hatchlings. In some wading birds, such as the rednecked phalarope (Phalaropus lobatus), it is the males that raise the young. The rednecked phalarope is also one of the few bird species in which the females are more brightly colored than the males. In some stickleback fishes such as Gasterosteus aculeatus, females prefer to provide eggs to males who already have eggs in the nests they have built. This has led to the evolution of stealing behavior, in which males will steal eggs from the nests built by other males. Males of the fish species Cyrtocara eucinostomus, though only 0.4 inches (10 cm) in length, build enormous sand castles a meter wide at the base, one mouthful of sand at a time. The female chooses the male that constructs the best castle. In some frogs and fishes (such as the seahorse), the female lays the eggs, and then the male scoops them up into his mouth to protect them while they hatch, a process called mouth-brooding. This activity benefits the male in that he can be certain the offspring are his. However, during this prolonged period of time, the male cannot fertilize any other eggs. This is a considerable

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482 sexual selection  482 expense for the male. Because it typically takes more than one male to mouth-brood the eggs produced by one female, it is the females that compete with one another for access to mouth-brooding males. Therefore, while sperm are individually cheap, male reproductive expenditure can be expensive. In some instances, the females may be so widely dispersed that a male is lucky to ever find one, and a female is unlikely to be found by more than one male. In these cases, there is no advantage for a male to be large. In some species of invertebrates (such as some barnacles) as well as some fishes (such as deep sea angler fishes), the males are small, and even merge into the flesh of the females so that they resemble an organ or a lump on the female. Sexual selection has operated strongly during human evolution. Men have evolved numerous fitness indicators to influence female choice. Some of these fitness indicators are visible characteristics such as muscularity; as a result, sexual selection may have caused men to become more muscular than they need to be. Most male fitness indicators have less to do with appearance than with function. The human penis is larger than that of some other primates. There may be two reasons for this. One reason is, as noted above, a large penis is associated with promiscuous mating systems, as in chimpanzees, while a small penis is associated with harem mating systems, as in gorillas; humans are intermediate. Another reason is that large penis size may have been selected because of the tactile pleasure that it provides to the females, who would then choose to keep company with the man who could provide this pleasure. This explanation would make no sense if pregnancy often occurred after a single copulation (as in cats), because by the time the female determined that a certain male gave less pleasure than others it would be too late to reject him. However, because numerous copulations are typically necessary for pregnancy to occur in humans, pleasure is a useful piece of information on which a woman could partly base her decision. Therefore female choice that maintains a relationship, as well as the choice that initiates it, has been important in human evolution. As noted above, males sometimes select among competing females. This is especially the case in animal species that have expensive offspring, such as humans. Human reproduction is so expensive that there is a definite survival benefit to the offspring if both parents help to raise them. The genetic fitness of the men, as well as the women, would be enhanced if the man stays with the woman and helps with the provision and protection of the offspring.

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first entry If the woman has fitness indicators that will attract the man and entice him to stay, her reproductive success may be enhanced, as well as his. The man, in turn, may want his genes to be carried by a woman who is most likely to raise the children to adulthood. Women have, therefore, also evolved fitness indicators that show that they are healthy and well nourished. A primary indicator of health is the face. A face that is symmetrical and unblemished is an indicator of past and current health. Another indicator is fat accumulation. Fat accumulation serves not only as a fitness indicator, but as a direct contributor to the ability to raise children—through nursing and later the ability to survive food shortages during which feeding the child or children receives top priority. Fat accumulation throughout the body would be less obvious than fat accumulation in visible places such as breasts and buttocks. To be effective, a fitness indicator must be expensive and show variation among individuals. Faces, breasts, and buttocks not only indicate health and nutrition but also age. If skin did not wrinkle and if breasts did not sag with advancing age, they would not have served as reliable indicators of female fitness. Evolutionary scientists have been slow to catch on to Darwin’s insight that sexual selection has been paramount in human evolution. They have instead focused on the more practical survival aspects of life as paramount in human evolution, for example: language as a means of communicating the locations of resources or sorting out social hierarchies; tools as means of obtaining resources or as weapons against competing tribes; and the relative hairlessness of the human body as an adaptation that allows warmblooded mammals to cool off in the hot African savannas. In general, all of the many adaptations that are collectively called intelligence have been attributed to natural selection for the serious businesses of resource acquisition and war. In many cases, these explanations were and are believable. Tools certainly have enhanced the ability of humans to exploit natural resources, and complex social interactions would be impossible without language (even though chimpanzee societies are quite complex despite the lack of true language). But even the believable explanations seem insufficient. Consider, for example, language, which some scientists consider the major adaptation that distinguishes human from animal intelligence. Theories proposed early in the 20th century attempted to explain the origin of language in terms of practical natural selection. What should have been obvious even at that time is that languages are far more complex than they need to be for such simple practical requirements. Just how complex does language have to be in order to say “Lion!” or “Time for lunch!”?

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sexual selection  483 Perhaps the best explanation for the origin of language is that it was an indicator of the quality of intelligence and of the brain. People who could not just talk but speak with complex grammar and poetical allusions obviously had good brains. Many other characteristics of human intelligence, such as the production of art and music, serve as clear indicators of the quality of the brain and could therefore function as sexual fitness indicators. Evolutionary biologist Geoffrey Miller explains that the human brain itself is a fitness indicator, since it is such an expensive organ (consuming tremendous amounts of energy and oxygen) and at least half of the genes are involved in brain development. Therefore, practically anything that the brain does can be a fitness indicator. As such, it can be the subject of sexual selection. By choosing intelligent mates, both men and women could be reasonably certain that their mate had good genes. Another example of a characteristic often considered to have evolved for its practical benefits is hunting. The practical explanation of hunting is that men bring home the meat while women gather nuts, berries, and grains. While plant materials may provide most of the calories, the meat brought home by the men provides essential nutrients that would be missing from a vegetarian diet. Even if it is true that a purely vegetarian diet would be inadequate, this does not explain why men hunt big game in nearly every tribe that has been studied and continue to do so today in civilized nations. Men could provide adequate meat by hunting small game. In fact, they could provide more meat in this manner and with considerably less danger to themselves. Simply put, hunting big game is not a practical way for a man to provide for his family. It appears that hunting, in all societies, has been and is a sport. Its purpose is to be a fitness indicator: Only very strong males with good brains can show off their qualities by undergoing the physical exertion and having the intelligence to track down, or trick, dangerous game animals and then kill them. By choosing good hunters, the women could be reasonably sure that their mates were strong and intelligent. Many human characteristics, not the least of which is the large human brain, are part of a pattern called neoteny, in which juvenile characteristics are retained into adulthood. This explains many unique human features as part of a suite of neotenous traits but does not explain why neoteny occurred in the first place. What, if anything, caused neoteny to operate during human evolution? It is possible that the retention of juvenile characteristics was selected because they made older people look younger, thus deceptively enhancing fitness indicators of youth in both sexes.

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Some scientists question the pervasiveness of sexual selection in the animal kingdom. Evolutionary biologist Joan Roughgarden points out that if sexual selection were the most important explanation of sexual reproductive behavior among animals, then such behavior would be mostly heterosexual. Other forms of sexual behavior are too common to be dismissed as mere exceptions to the rule. Sexual behavior plays other roles, such as dominance or the enhancement of cooperation. Other scientists point out that, while this is true, it was sexual selection that produced the reproductive systems in the first place, and they were then available for other functions, such as dominance and cooperation.

Sexual Selection in Plants Mate choice, resulting in sexual selection, can occur in organisms other than animals. Evolutionary biologists Mary Willson and Nancy Burley pointed out not only that male plants, or the male function of bisexual plants, compete with one another in terms of sperm or pollen production (as explained previously) but also that female plants, or the female function of bisexual plants, may be able to discriminate among sperm or pollen. Male competition in plants occurs for the same reason that it does in animals: A plant can produce more sperm, or more pollen, than a female plant can produce eggs, or ovules, and the female plant, or female function within the plant, not only produces eggs or ovules, but also nourishes the resulting embryo, often within a seed, and provides for its dispersal, often within a fruit. Instances of sexual selection in plants may include the following: ●●

●●

Male competition can cause plants to undergo male reproduction earlier than female reproduction, since the first plant to produce sperm or pollen can fertilize numerous female plants. Botanist Stanley Rice and his students have shown that in cottonwoods (Populus deltoides), which have separate male and female trees, the male trees open their flower buds earlier, on the average, than female trees—although, of course, their flowering times must overlap or else pollination would fail. Male trees that open earlier may pollinate many female flowers before other male trees get a chance to do so. This could be interpreted as sexual selection among male trees. Plants do not copulate. Pollen must be carried from the male parts of one plant to the female parts of another. Plants rely on the wind, or on many species of pollinators, to accomplish this. The plants that more

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484 sexual selection  484

●●

●●

●●

effectively attract pollinators are more effective at sexual reproduction. All of the characteristics of plants related to pollination can therefore be considered the products of sexual selection. In animal-pollinated dioecious plant species, in which some plants are male and others are female, male flowers are usually larger and more colorful than female flowers. This can be interpreted as male-male competition for sperm delivery, and therefore sexual selection. Once a flower has been pollinated, the pollen must grow a tube down into the flower, making contact with an ovule, which may be a great distance away. In maize, for example, the tube from a pollen grain must grow up to eight inches (20 cm), a thousand times the length of the pollen grain, to reach the ovule. The sperm nucleus then descends through this tube to complete the act of fertilization. The structure through which the pollen tube must grow, the style, can be said to exist for the sole purpose of “weeding out” inferior pollen grains. Botanist Allison Snow has found that in the bush Hibiscus moscheutos, pollen grains from some plants grow tubes faster than pollen grains from other plants. Because flowers often receive more pollen than they need, there is often a race between the different pollen tubes to be the first ones to arrive at the immature seeds—which may constitute sexual selection among the pollen tubes. In terms of differences among pollen grains in the rate of growth, the style functions just as the food source through which the tube grows. But the pistil is more than just a food source for the pollen tube. The pistil itself may chemically encourage the growth of some pollen tubes and discourage others. This is difficult to demonstrate. It has been shown that there is greater variation in pollen tube growth rate in the pistils of healthy plants than of plants that are experiencing stresses such as drought. This implies but does not prove that a healthy plant chemically distinguishes among pollen tubes. The haploid cells surrounding the egg cell, in the immature seed, have genes that control the release of sperm from the pollen tubes. This implies the possibility of sexual selection in which the female cells are in control of which sperm are allowed to fertilize the immature seeds. Botanist Diane Marshall found that radish plants may provide more food to those

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developing fruits that contain seeds that are more genetically variable (the result of a greater diversity of pollen donors) than to fruits that contain genetically more uniform seeds. Botanists K. Searcy and M. McNair found that monkeyflower plants (Mimulus guttatus) that grow in soil that contains mildly toxic levels of copper selectively abort seeds that had been fertilized by pollen from donors that were not resistant to copper. These may be examples of sexual selection in which the maternal plant selects among pollen sources. The endosperm is the food supply for the embryo inside the seed. It is triploid, having formed from two sets of chromosomes from the plant that produces it but only one set from the pollen. Several researchers, such as botanist Mark Westoby, have interpreted this as sexual selection in which the maternal plant gains more control than the paternal plant in controlling the growth of the embryo.

Therefore, while natural selection explains the diversity of adaptations that allow organisms to survive and reproduce in different environments, and in response to other species, it is sexual selection that primarily explains much of the seemingly arbitrary characteristics of animals and perhaps many characteristics of plants as well. Natural selection has made the world of organisms efficient; sexual selection has made it wildly beautiful and extremely diverse. See also coevolution; life history, diversity of; natural selection. Further Reading Albert, Arianne Y. K., and Sarah P. Otto. “Sexual selection can resolve sex-linked sexual antagonism.” Science 310 (2005): 119–121. Alcock, John. An Enthusiasm for Orchids: Sex and Deception in Plant Evolution. New York: Oxford University Press, 2005. Andersson, Malte. “Evolution of classical polyandry: Three steps to female emancipation.” Ethology 111 (2005): 1–23. ———, and Leigh W. Simmons. “Sexual selection and mate choice.” Trends in Ecology and Evolution 21 (2006): 296–302. Bernasconi, G., et al. “Evolutionary ecology of the prezygotic stage.” Science 303 (2004): 971–974. Bjork, Adam, and Scott Pitnick. “Intensity of sexual selection along the anisogamy-isogamy continuum.” Nature 441 (2006): 742–745. Chaine, Alexis S., and Bruce E. Lyon. “Adaptive plasticity in female mate choice dampens sexual selection

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sexual selection  485 on male ornaments in the lark bunting.” Science 318 (2008): 459–462. Crump, Marty. Headless Males Make Great Lovers: And Other Unusual Natural Histories. Chicago: University of Chicago Press, 2007. Cuervo, J. J., and R. M. De Ayala. “Experimental tail shortening in barn swallows (Hirundo rustica) affects haematocrit.” Functional Ecology 19 (2005): 828–835. Darwin, Charles. The Descent of Man, and Selection in Relation to Sex. London: John Murray, 1871. Reprint, with introduction by James Moore and Adrian Desmond, New York: Penguin Classics, 2004. Dean, Rebecca, Michael B. Bonsall, and Tommaso Pizzari. “Aging and sexual conflict.” Science 316 (2007): 383–384. DelBarco-Trillo, Javier, and Michael H. Ferkin. “Male mammals respond to a risk of sperm competition conveyed by odours of conspecific males.” Nature 431 (2004): 446–449. Diamond, Jared. Why Is Sex Fun? New York: Basic Books, 1997. Gomendio, Montserrat, et al. “Male fertility and sex ratio of birth in red deer.” Science 314 (2006): 1,445–1,447. Haig, David, and Mark Westoby. “Parent-specific gene expression and the triploid endosperm.” American Naturalist 134 (1989): 147–155. ———. “Seed size, pollination costs and angiosperm success.” Evolutionary Ecology 5 (1991): 231–247. Hamilton, William D., and Marlene Zuk. “Heritable true fitness and bright birds: A role for parasites?” Science 218 (1982): 384–387. Heinsohn, Robert, Sarah Legge, and John A. Endler. “Extreme reversed sexual dichromatism in a bird without sex role reversal.” Science 309 (2005): 617–619. Holland, Jennifer S. “Feathers of seduction.” National Geographic, July 2007, 82–101. Judson, Olivia. Dr. Tatiana’s Sex Advice to All Creation. New York: Henry Holt, 2002. Kappeler, Peter M., and Carel P. van Schaik. Sexual Selection in Primates: New and Comparative Perspectives. Cambridge, U.K.: Cambridge University Press, 2004. Lehrer, Jonah. “The gay animal kingdom: The effeminate sheep and other problems with Darwinian sexual selection.” Available online. URL: http://seedmagazine. com/news/2006/06/the_gay_animal_kingdom.php. Accessed August 3, 2010. Marshall, Diane L., and M. W. Folsom. “Mate choice in plants: An anatomical to population perspective.” Annual Review of Ecology and Systematics 22 (1991): 37–63. ———, and Pamela K. Diggle. “Mechanisms of differential pollen donor performance in the wild radish,

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Raphanus sativus (Brassicaceae).” American Journal of Botany 88 (2001): 242–257. Miller, Geoffrey. The Mating Mind: How Sexual Choice Shaped the Evolution of Human Nature. New York: Doubleday, 2000. Miller, Paige M., et al. “Sexual conflict via maternal-effect genes in ZW species.” Science 312 (2006): 73. Nielsen, M. G., and W. B. Watt. “Interference competition and sexual selection promote polymorphism in Colias (Lepidoptera, Pieridae).” Functional Ecology 14 (2000): 718–730. Pomiankowski, A., and Y. Iwasa. “Runaway ornament diversity caused by Fisherian sexual selection.” Proceedings of the National Academy of Sciences USA 95 (1998): 5,106–5,111. Reed, Wendy. “Physiological effects on demography: A long-term experimental study of testosterone’s effects on fitness.” American Naturalist 167 (2006): 667–683. Roughgarden, Joan. Evolution’s Rainbow: Diversity, Gender, and Sexuality in Nature and People. Berkeley: University of California Press, 2004. Searcy, K. B., and M. R. McNair. “Developmental selection in response to environmental conditions of the maternal parent in Mimulus guttatus.” Evolution 47 (1993): 13–24. Snow, Allison A. “Postpollination selection and male fitness in plants.” American Naturalist 144 (1994): 569–583. ———, and Timothy Spira. “Pollen-tube competition and male fitness in Hibiscus moscheutos.” Evolution 60 (1996): 1,866–1,870. Trivers, Robert. “Parental investment and sexual selection.” In Sexual Selection and the Descent of Man, edited by B. Campbell, 136–179. Chicago: Aldine, 1972. Van Oort, H., and R. D. Dawson. “Carotenoid ornamentation of adult male common redpolls predicts probability of dying in a salmonellosis outbreak.” Functional Ecology 19 (2005): 822–827. West, Peyton M. “The lion’s mane.” American Scientist 93 (2005): 226–235. Williamson, K. A., et al. “Yolk antioxidants and mate attractiveness in the zebra finch.” Functional Ecology 20 (2006): 354–359. Willson, Mary F., and Nancy Burley. Mate Choice in Plants: Tactics, Mechanisms, and Consequences. Princeton, N.J.: Princeton University Press, 1983. Zahavi, Amotz. The Handicap Principle: A Missing Piece of Darwin’s Puzzle. New York: Oxford University Press, 1997. Zimmer, Carl. “In ducks, war of the sexes plays out in evolution of genitalia.” New York Times (May 1, 2007). Available online. URL: http://www.nytimes. com/2007/04/30/science/01duck.html?pagewanted=all. Accessed May 16, 2011.

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486 shrublands  486

shrublands  The shrubland ecological community consists of dense shrubs from about a foot to about nine feet (about one-half meter to 3 m) in height and the other species living in association with them. Shrubs, rather than trees or grasses, dominate these communities, usually for the following reasons: ●●

●●

●●

Low rainfall. Shrublands typically receive little rainfall (and only very rarely snow), and most of this occurs in the winter. Dominant shrubs have adaptations such as small, thick leaves that allow them to survive the long, dry summers. One of the reasons that most of the shrubs are evergreen is that most of the rain falls during mild winters. Poor soil. Shrubland soils are typically very poor and often very rocky. In some shrublands, the soil is acidic. Another reason that most of the shrubs are evergreen is that the soil is poor, and the shrubs retain their leaves because of the nutrients in them. Fire. Fires occur in shrublands every few decades because the shrubs grow densely and because of summer drought. The accumulation of dry dead leaves promotes the chances of fire, especially during windy conditions. Many shrub and wildflower species cannot persist in the shrublands unless a fire has burned away the shrub cover, at which time many seeds germinate and some of the shrubs resprout. Fires also convert plant material into ash, which fertilizes the poor soil.

Some shrublands have ecological conditions different from these. For example, the moorlands of England are wet and may even have layers of peat moss. Artificial shrublands are found in many areas scattered around the world. Humans cleared forests thousands of years ago and have kept the forest trees out by fire and by continued clearing in these areas. Chaparral and related shrublands. The chaparral community dominates some areas with a Mediterranean climate of mild, wet winters and hot, dry summers. This kind of climate occurs in California, where most of the chaparral is located; in the Mediterranean Basin, where the shrublands are called maquia or garrigue; in central Chile and Central Mexico, where they are called matorral; in southwestern Australia, where they are called mallee; and in the Cape region of South Africa, where they are called fynbos. The shrubs, often about six feet (2 m) tall, are very dense and all but

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first entry Some Important Dominant Species   in Shrublands Chaparral (California) Bush monkeyflower

Mimulus aurantiacus

Chamise

Adenostoma fasciculatum

Holly-leaf cherry

Prunus ilicifolia

Large-fruited ceanothus

Ceanothus megacarpus

Laurel sumac

Malosma (Rhus) laurina

Pointleaf manzanita

Arctostaphylos pungens

Scrub oak

Quercus dumosa

Toyon

Heteromeles arbutifolia

Maquia and Garrigue (Mediterranean) Holm oak

Quercus ilex

Kermes oak

Quercus coccifera

Myrtle

Myrtus communis

Strawberry tree

Arbutus unedo

Tree heath

Erica arborea

Matorral (Mexico) Desert ceanothus

Ceanothus greggii

Pointleaf manzanita

Arctostaphylos pungens

Scrub oak

Quercus sebifera

Texas madrone

Arbutus xalapensis

Matorral (Chile) Coastal daisy

Bahia ambrosioides

Colliguay

Colliguaya odorifera

Soapbark tree

Quillaja saponaria

Litre

Lithraea caustica

Fynbos (South Africa) Cape Flats erica

Erica verticillata

Broad-leaved sugarbush

Protea eximia

Laurel protea

Protea laurifolia

Renosterbos

Elytropappus rhinocerotis

Sunshine conebush

Leucadendron saligna

Mallee (Southwestern Australia) Firewood Banksia

Banksia menziesii

Golden Dryandra

Banksia nobilis

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shrublands  487 Prickly toothbrush

Grevillea armigera

Quandong

Santalum acuminatum

Sage Scrub (California) Black sage

Salvia mellifera

California buckwheat

Eriogonum fasciculatum

California sagebrush

Artemisia californica

White sage

Salvia leucophylla

Sage Scrub (Mediterranean) Common sage

Salvia officinalis

Lavender

Lavandula spica

Rosemary

Rosmarinus officinalis

Thyme

Thymus vulgaris

Heather (Britain) Bell heather

Erica cinerea

Ling heather

Calluna vulgaris

i­ mpenetrable to humans and large animals. Chaparral and similar ecological communities usually have many dominant shrub species, which contribute to the hot spot diversity in their geographical areas. Due to massive buildup of combustible leaf litter and dead branches, fires become nearly inevitable in the chaparral after a few decades. Without fire, the chaparral would probably become temperate evergreen forest, for example, of evergreen oaks in California or the Mediterranean or of eucalypts in Australia. (Oaks and eucalypts also resprout or germinate after fires.) With excessive fire, the chaparral would probably become grassland. Because the thick branches create a very hot fire, because the fires spread rapidly, and because they are inevitable, people who build homes in chaparral regions need to be aware of the risk they are taking—more of a fire risk than in perhaps any other natural habitat on Earth. Some wildflower species are rare except immediately after a chaparral fire. Examples from California include the giant-flowered phacelia (Phacelia grandiflora) and the fire poppy (Papaver californicum). Other wildflowers, such as the ground pink (Linanthus dianthiflorus) and the California poppy (Eschscholzia californica), grow in disturbed areas and, for this reason, are abundant after chaparral burns.

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The Northern Hemisphere shrub communities share some genera of dominant plants, most notably scrub oaks (Quercus). Both California and Mexico share the manzanitas (Arctostaphylos) and Ceanothus bushes. A completely different set of plants dominates the Southern Hemisphere shrublands (see table). Mediterranean sage scrub. Short bushes dominate sage scrublands. In California and in the Mediterranean Basin, many of these shrubs are in the mint family (Lamiaceae) and have strongly scented leaves. One role that the volatile chemicals from these leaves may play is allelopathy, that is, the chemicals inhibit the growth of other species of plants. Heather. The heather of England and Scotland are dominated by a relatively small number of shrub species in the genus Erica and Calluna. Thin acidic soil covers chalk (basic) soil in these areas, where shallow-rooted species tolerate acid, deeper rooted ones do not, and some species tolerate both acidic and basic conditions. It is likely that the heather is an artificial shrubland that resulted from the prehistoric clearing of forests. See also competition, ecological; disturbances, ecological. Further Reading Armstrong, Wayne P. “Ashes to Wildflowers: A Promise of Renewal Springs from Destruction.” Available online. URL: http://waynesword.palomar.edu/ww0604.htm. Accessed July 8, 2010. Arroyo, J., and T. Marañón. “Community ecology and distributional spectra of Mediterranean shrublands and heathlands in southern Spain.” Journal of Biogeography 17 (1990): 163–176. California Chaparral Institute. “California Chaparral Institute.” Available online. URL: http://www.california chaparral.org. Accessed July 8, 2010. Christensen, Norman L., and Cornelius H. Muller. “Effects of fire on factors controlling plant growth in Adenostoma chaparral.” Ecological Monographs 45 (1975): 29–55. Holmgren, Milena, et al. “Why have European herbs so successfully invaded the Chilean matorral? Effects of herbivory, soil nutrients, and fire.” Journal of Arid Environments 44 (2000): 197–211. Jaksi´c, F. M., and E. R. Fuentes. “Why are native herbs in the Chilean matorral more abundant beneath bushes: Microclimate or grazing?” Journal of Ecology 68 (1980): 665–669. Jiménez, Héctor E., and Juan J. Armesto. “Importance of the soil seed bank of disturbed sites in Chilean matorral in early secondary succession.” Journal of Vegetation Science 3 (1992): 579–586.

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488 Silurian period, biodiversity in  488 Keeley, Jon E., et al. “Role of allelopathy, heat, and charred wood in the germination of chaparral herbs and suffrutescents.” Journal of Ecology 73 (1985): 445–458. ———, et al. “Reexamining fire suppression impacts on brushland fire regimes.” Science 284 (1999): 1,829–1,832. ———, et al. “Fire suppression impacts on postfire recovery of Sierra Nevada chaparral shrublands.” International Journal of Wildland Fire 14 (2005): 255–265. Lavorel, Sandra. “Ecological diversity and resilience of Mediterranean vegetation to disturbance.” Diversity and Distributions 5 (1999): 3–13. Minnich, R. A. “Fire mosaics in southern California and northern Baja California.” Science 219 (1983): 1,287–1,294. Moritz, M. A., et al. “Testing a basic assumption of shrubland fire management: How important is fuel age?” Frontiers in Ecology and the Environment 2 (2004): 67–72. Muller, Cornelius H., Walter Muller, and Bruce Haines. “Volatile growth inhibitors produced by aromatic shrubs.” Science 143 (1966): 471–473. Valiente-Banuet, Alfonso, et al. “The chaparral vegetation in Mexico under non-Mediterranean climate: The convergence and Madrean-Tethyan hypotheses reconsidered.” American Journal of Botany 85 (1998): 1,398–1,408.

Silurian period, biodiversity in  The Silurian period (440 to 410 million years ago) was the third period of the Paleozoic era. It followed the Ordovician period and preceded the Devonian period. An average of about 450 families of marine organisms and 50 families of continental organisms existed during the Ordovician, compared to 2,200 total families today. Climate. The climate of the continents was generally warm and moist, except the landmasses directly over the South Pole, during the Silurian period. Some southern glaciers from the Ordovician period melted and raised the sea level. Atmospheric oxygen levels were much lower, and carbon dioxide levels much higher, than today. Global temperatures were also higher than today (see table on page 489). Continents. As in the preceding and following periods, most of the landmass was near the South Pole (Gondwana). Other landmasses that today constitute Eurasia, Siberia, and China were near the equator. Sea level was much higher than today—just under 600 feet (about 180 m) higher than modern oceans. Marine life. During the Silurian period, aquatic animals continued expanding from shallow marine waters into deeper waters and into freshwater. ●●

Invertebrates. The trilobites continued to evolve new forms as they declined in diver-

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first entry

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sity. Among the earliest crustaceans from this period was Ceratiocaris. Mollusks continued to be abundant and diverse in shallow seas, including bivalves. However, brachiopods (which superficially resemble bivalves) were much more common than bivalves. Among the echinoderms were the stalked crinoids such as Ampheristocystus. Vertebrates. The only vertebrates were fishes, jawless descendants of the early fishes of the Ordovician period. Armored jawless fishes were common. The first jawed fishes evolved at the end of the period but were rare.

Life on land. The earliest complete specimens of continental organisms date from the Silurian period. ●●

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Plants. The first complete specimens of land plants were small vascular plants, such as Cooksonia, that resembled modern club mosses. They grew only in freshwater wetlands, extending a few inches into the air rather than being completely underwater. But they had the plumbing cells (xylem) that would later allow plants to live on dry land. The most enigmatic fossil of the Silurian period is Prototaxites. It was originally considered to be a vascular plant that towered over 25 feet (8 m), high above the other plants. Then it was suggested, based on a chemical analysis of the fossils, that Prototaxites was actually a giant fungus. Most recently, botanist Linda Graham and associates have questioned whether it was an organism that stood upright at all. They claim that these fossils may be rolled-up mats of liverworts! Invertebrates. The first terrestrial animals were relatives of modern millipedes, scorpions, and insectlike collembolans. These arthropods fed mostly on one another or on detritus. The plants contained lignins and toxins; it is likely that the animals could not digest the plant material until it had been softened and detoxified by fungi. While today the food chain is based largely upon the consumption of fresh green plant tissue, the Silurian continental food chain may have depended only indirectly on plants. Vertebrates. The first bony fishes evolved during the Silurian period. Little is known about Silurian bony fishes. The earliest bony fishes may have evolved in freshwater. Bones may have served primarily to store calcium, of which freshwater can be deficient.

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speciation  489 Multicellular Biodiversity   in the Silurian Period Conditions Atmospheric oxygen

70% of modern level

Atmospheric carbon dioxide

12.9 times modern level

Global temperature

3°F (2°C) higher than today

Sea level

580 feet (180 m) higher than today

Approximate number of families* Continental

50

Marine

450

Total

500

Examples of marine animals Amperistocystus sp.

crinoid echinoderm

Ceratiocaris sp.

crustacean

Coelocaulus sp.

gastropod mollusk

Dalmanites limuliroides

trilobite arthropod

Doryapsis nathorsti

armored jawless fish

Eurypteris sp.

sea scorpion

Gavosites gothlandicus

coral

Pentameroides subrectus

brachiopod

Phragmoceras exaggeratus

cephalopod mollusk

Examples of continental animals Andreolepis hedei

bony fish

Pneumodesmus newmani millipede Proscorpius sp.

scorpion

Rhyniognatha hirsti

insect relative

Example of land plant and fungus Cooksonia pertoni

club moss relative

Prototaxites loganii

fungus**

*Based on Benton. **Identity as fungus now disputed.

Further Reading Benton, Michael. “Diversification and extinction in the history of life.” Science 268 (1995): 52–58. Botella, Hector, et al. “Jaws and teeth of the earliest bony fishes.” Nature 448 (2007): 583–586. Ericksson, Mats E., et al. “Vertebrate extinctions and reorganizations during the Late Silurian Lau Event.” Geology 37 (2009): 739–742. Graham, Linda E., et al. “Structural, physiological, and stable carbon isotopic evidence that the enigmatic Paleozoic fossil Prototaxites formed from rolled liverwort mats.” American Journal of Botany 97 (2010): 268–275. Jeram, Andrew J., et al. “Land animals in the Silurian: Arachnids and myriapods from Shropshire, England.” Science 250 (1990): 658–661.

speciation  Speciation occurs when two or more

species diverge from a single ancestral population. This process has produced all of the species-level biodiversity in the world. Natural selection and sexual selection can produce evolutionary change within lineages of organisms over time. However, as many writers have pointed out, Charles Darwin’s book Origin of Species did not actually explain how two or more species could evolve from one species but only how one species could change into another. Something more is needed, besides natural and sexual selection, to explain speciation. A certain amount of reproductive isolation is necessary. If one population of organisms is separated into two populations, the two groups cannot interbreed. This could result from geographical isolation, in which the two populations are isolated from one another by impassible barriers such as deserts or oceans. Or it could result from characteristics of the organisms themselves: Isolating mechanisms are negative processes that prevent interbreeding between groups, and specific mate recognition systems are positive processes that encourage breeding within groups. Once even partial reproductive isolation occurs, the genes of the two populations no longer mix completely together. The two populations may eventually become two species because new genetic combinations, and new mutations, that occur in one population will be different from those in the other, and the two populations could then diverge along different evolutionary lines. Divergence may then occur: ●●

Extinctions. The Silurian period began after the Ordovician extinction, which was one of the five mass extinctions in the history of the Earth. See also Devonian period, biodiversity in; Ordovician period, biodiversity in.

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Natural selection may favor different characteristics in each group strongly enough to compensate for interchange of genes (gene flow) between the populations. After the populations have begun to diverge, natural selection may favor isolating mechanisms

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first entry

and specific mate recognition systems that complete the process of speciation. Different and random genetic changes may occur in each group. Even if natural selection favors the same characteristics in both populations, they will probably diverge because they will not have the same genes upon which natural selection can act.

Evolutionary biologists distinguish species on the basis of either a biological or a phylogenetic species concept. The biological species concept recognizes the potential to interbreed under natural conditions as the definition of species membership. Even though this concept has some difficulties (hybridization between recognized species occurs frequently, and investigators cannot know the interbreeding potential of geographically isolated populations or fossil species), it is the concept that most closely reflects the evolutionary process itself. The phylogenetic species concept recognizes that species are different if they have evolved along distinct evolutionary lines. Natural or sexual selection may occur rapidly after reproductive isolation, as the incipient species adjusts by directional selection to the new environmental conditions or the new set of species with which it is in contact. This may be followed by a long period of stabilizing selection. This has occurred frequently enough, according to many paleontologists, to produce a pattern of punctuated equilibria in the fossil record, in which long periods of equilibrium are punctuated by brief spurts of speciation.

Given long enough time, the geographic separation of populations almost inevitably produces new species through allopatric speciation. Peripatric speciation. Peripatric speciation is similar to allopatric speciation but involves the geographical isolation of small populations from the main population. Small populations can be important in speciation, since the genetic makeup of small populations can change more rapidly than that of large populations. A classic experimental demonstration of rapid evolution in small populations is the study by Theodosius Dobzhansky of evolutionary change in fruit flies over the course of a year and a half. Dobzhansky established 20 large and 20 small populations of fruit flies, each with a certain chromosome at 50 percent frequency. In most populations, this chromosome became less frequent. In all of the large populations, the chromosome became less frequent to about the same extent; they all evolved similarly. In the small populations, some hardly evolved at all, and some evolved a great deal; the small populations had a much greater range of evolutionary outcomes than the large populations. Parapatric speciation. A large population may evolve into two or more species by specialization on different habitats within the geographical range of the ancestral species. Sympatric speciation. Reproductive isolation can also occur between two populations that live in the same location. Examples include: ●●

Patterns of Speciation Speciation can occur in different patterns, as described in the following sections. Allopatric speciation. Allopatric speciation occurs when populations are geographically or ecologically isolated. This has occurred frequently on islands, where dispersal of plants and animals from the mainland is rarely successful, and once it occurs, the island population is unlikely to disperse back to the mainland. This is the process that has produced the vast number of unique endemic species found only on certain islands. The presence of many endemic species on islands—most notably the Galápagos Islands—was one of Darwin’s chief evidences that evolution has, in fact, occurred. Most species of nettles are small, stinging herbs, but in Hawaii, a stingless nettle bush has evolved, in isolation from mainland nettles. Hawaii has or had many species of birds, snails, insects, plants, and many other species found nowhere else in the world. Not surprisingly, Hawaii has the longest list of threatened and endangered species of any state in the United States.

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If two species of plants open their flowers in different seasons (for example, the autumnflowering v. the spring-flowering species of alder trees of the genus Alnus), they cannot interbreed, even if they live in the same habitat. If two species of plants depend upon different pollinators (such as the hummingbird-pollinated v. the bumblebee-pollinated monkeyflowers of the genus Mimulus), they will not interbreed, even if they are right next to one another (see below). Genera of plants with bilaterally symmetrical flowers tend to have more species than genera that are otherwise similar but have radially symmetrical flowers, perhaps because bilaterally symmetrical flowers often have more specialized relationships with pollinators. If two species of animals specialize on different food plants (especially if they live on and mate on these food plants as well), they will not interbreed very often, even if their respective food plants are right next to one another. It has been reported that some European corn borer larvae now consume

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speciation  491

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hops. This has resulted in adult insects that emit different mating pheromones. Adult borers whose larvae ate hops preferentially mate with other such adults, rather than adults whose larvae ate corn. If two species of animals have different mating calls or rituals, they will not interbreed very often, even if they are in contact. This has been observed with Darwin’s finches on the Galápagos Islands (see below). Indigobirds are nest parasites, which means that they lay their eggs in the nests of other bird species. Cladistic analysis indicates that indigobirds evolved into several species more recently than did the host species. This apparently happened because the young indigobirds learned songs and habits from their hosts, and when they grew up, they tended to mate with other indigobirds that had similar songs and habits and to parasitize the nests of the same species of birds as their parents. If two species of plants can cross-pollinate, but the pollen grains do not successfully fertilize the egg nuclei—or if two animal species can mate with one another but the sperm from one population has inferior performance in the female reproductive tracts of the other—then the proximity of the two populations does not matter. In some cases, symbiogenesis may cause reproductive isolation if one population that consists of individuals in which a mutualistic microbe is living cannot crossbreed with a population whose individuals lack the microbe.

Isolating mechanisms (see below) can separate two populations and allow them to evolve into two species. The two populations might as well be separated by an ocean. Given long enough time, the reproductive separation of populations almost inevitably produces new species through sympatric speciation. Speciation by hybridization. Hybrids between species may result in offspring with incompatible chromosomes. If the chromosomes within the cells of the offspring are unable to match up with one another during meiosis, the offspring are sterile. Among animals, hybrids are generally the end of the evolutionary line. A strong mule, for example, cannot produce offspring. Many species of animals hybridize, but the hybrid offspring are often inferior in survival and reproduction. Nevertheless, an occasional hybridization can be an important source of new genes for a species. The gene for organophos-

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phate insecticide resistance originated in the mosquito species Culex pipiens, but it spread worldwide, even across mosquito species boundaries, probably because of rare but important hybridizations. However, among plants, sterile individuals produced by hybridization may have options that are not available to animals. Many plants reproduce without sex, a process called apomixis. The embryo produced inside the seed is an exact genetic copy of the parent, and the plant that grows from it is a clone of the parent. An example is the wildflower Oxalis pes-caprae in the shamrock family. Many individuals in this species have chromosomes in groups of five rather than in groups of two; they produce beautiful flowers, but because meiosis cannot handle unpaired chromosomes, the flowers cannot produce either pollen or egg nuclei. They reproduce only by making underground bulbs, by which they survive the dry season. Each lineage of these plants is reproductively isolated from all the rest. Mutations may occur, and if the mutations are passed on through the bulbs, each lineage can evolve into what looks like a different species. In their native South Africa, there are a few Oxalis pes-caprae with evenly paired chromosomes that can reproduce sexually, but they are reproductively isolated from the sterile Oxalis individuals. To call each sterile lineage of Oxalis a separate species would be maddeningly complex, and yet each sterile lineage does function as if it were a separate species. Dandelions (Taraxacum officinale) have chromosomes in groups of three and are also unable to reproduce sexually. They produce seeds, but the seeds contain copies of the parental genes. Pollination is necessary to stimulate seed production but does not mix the genes of pollen and egg nuclei. Each clump of dandelion, then, functions as if it were a separate species. A single population of dandelions can contain dozens of distinct genetic lineages, which may have arisen by the multiple evolution of apomixis, or by somatic mutation, or both. Apomixis is not the only way that evolution can allow sterile plants to reproduce. When the reproductive cells of animals experience spontaneous chromosome doubling, the cell usually dies. Most animals tolerate only the most minor changes in the number of chromosomes; even then, as in Down syndrome (trisomy of chromosome 21) in humans, a single extra chromosome results in sterility and retardation. Plants, in contrast, frequently undergo spontaneous doubling in the number of chromosomes. A plant egg cell with doubled chromosomes may survive. A sexually sterile plant, if it undergoes chromosome doubling, may produce offspring that are not sterile, because the doubled chromosomes now form pairs, which allows meiosis to occur. Each

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chromosome can now match up with a copy of itself. These plants can now reproduce sexually. The population of plants with doubled chromosomes, however, may not be able to interbreed with either of the ancestral populations. The hybrid is then instantly isolated from both parents and has characteristics different from both; it becomes an “instant species.” New species have arisen by hybridization in the goatsbeard Tragopogon and in the sunflower Helianthus. This form of speciation is common in the plant kingdom. The study of chromosomes suggests that almost half of all plant species, and 95 percent of fern species, originated by chromosome doubling following hybridization.

Isolating Mechanisms Isolating mechanisms are biological processes, as opposed to geographical features, that keep populations apart and allow them to evolve into different species. They are particularly important in sympatric speciation (see above). Prezygotic isolating mechanisms prevent interbreeding from occurring in the first place, that is, the zygote (fertilized egg) does not form. Postzygotic isolating mechanisms operate after the formation of the zygote. Prezygotic isolating mechanisms include the following examples: Differences in pollination mechanisms. If a mutation occurs in a population of flowering plants that changes the characteristics of the flowers, the new kind of flower may not be recognized by the same pollinator that visits the old kind of flower. This is apparently what happened in California populations of monkeyflowers (genus Mimulus). Most species of Mimulus, including M. lewisii, have yellow flowers, which attract bees. Mimulus cardinalis, however, has red flowers, which attract hummingbirds. All of the monkeyflowers have the ability to produce red carotenoids, but in most of them a gene prevents carotenoid production in the flowers (except to form isolated spots, not enough to attract hummingbirds). A simple mutation occurred, causing a sudden surge in red carotenoid production. The flowers that had this mutation, though side by side with the yellow flowers, were reproductively isolated from them, because bees (which cannot see red) ignored them, and hummingbirds visited them instead. Subsequent to the reproductive isolation, further evolutionary changes occurred in the red- and ­yellow-flowered species. For example, the population of red flowers evolved a long, narrow tubular shape that was appropriate for hummingbirds, while the yellow flowers retained a short, wide tube that was appropriate for bees. The changes in flower shape reinforced the initial reproductive isolation that had occurred because of a change in flower

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color. While the change in flower color was sufficient to separate one species into two, natural selection subsequently favored changes in flower shape that enhanced the success of pollination in each species separately. What was once one species of monkeyflower evolved into two, side by side. Although nobody was there to observe the original formation of the red-flowered species, evolutionary biologists Douglas Schemske and Toby Bradshaw have experimentally re-created the sequence of events. They crossed the two monkeyflower species and produced a whole range of hybrids with intermediate shapes and colors. They found that the DNA sequences that enhanced carotenoid production, not the genes that controlled the shapes of the flowers, had an immediate and strong effect on pollinator preference. Another example of a change in pollination mechanism involves Schiedea salicaria, a small shrub that is native to Hawaii, investigated by ­evolutionary biologists Ann Sakai and Steve Weller. A few relatively minor genetic mutations appear to have caused some individuals in the population to rely more on pollination by wind and less on pollination by insects. These two groups can crosspollinate, but because they rely largely on different methods of pollination, they do not frequently do so. The individuals that have greater wind-pollination characteristics tend to live in drier locations, where insect pollinators are less common. Though not completely isolated from one another, these two groups of plants have apparently started on the road to separation, perhaps eventually into two different species. Natural selection often reinforces the dependence on different methods of pollination. For example, flowers that have characteristics intermediate in their appeal to hummingbirds and to bumblebees will probably not be pollinated very well by either hummingbirds or bumblebees. Differences in timing of reproduction. Each species has its own reproductive season. Mutations that cause some individuals in a population to have a different reproductive season will prevent those individuals from interbreeding with others. One example is the alder trees (genus Alnus) mentioned above. Early in their evolution, alder populations diverged into some that pollinated in the autumn (subgenus Clethropsis) and those that pollinated in the spring (subgenus Alnus). These subgenera can no longer interbreed. Another example is the flies that live on apple and hawthorn trees. Rhagoletis pomonella flies, native to North America, lay their eggs on the fruits of hawthorns, a wild bush that produces fruits that resemble small crabapples. When Europeans and white Americans began plant-

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speciation  493 ing apples in eastern North America, some populations of this fly species began to lay their eggs in apples. The populations of flies that lived in apple trees could potentially interbreed with the populations that lived on hawthorns but seldom did so, even if wild hawthorns and cultivated apples were side by side. An immediate reproductive isolation occurred because apple fruits mature three to four weeks earlier than those of hawthorns, with the result that the flies that hatch from apples are ready for reproduction weeks earlier than those that hatch from hawthorns. Differences in animal mating behavior. Animal populations may be reproductively isolated because of differences in mating rituals. Evolutionary biologists Peter and Rosemary Grant have extensively studied the beak sizes and mating preferences of several species of Darwin’s finches on some uninhabited islands in the Galápagos Archipelago. They have found that hybrids between finch species can occur, but occur rarely. Young male birds learn their mating songs from their fathers, and females use male mating songs to guide their choice of mates. Occasionally, a young male bird overhears and learns the song of a different species of finch nearby. When the young male bird grows up and sings, he attracts females of the wrong species. Hawaii has hundreds of species of fruit flies (genus Drosophila), all of them unique to the Hawaiian Islands, and all of them having recently evolved there (the islands are from 5 to one-half million years old). There may be scores of species living on a single island within the archipelago and close enough to one another to readily interbreed. They do not interbreed, however, because they have evolved different mating dances. The females of one species will not recognize the males of another species as being potential mates. Laboratory investigations of fruit flies (some species of which are the most intensively studied animals in the history of biology) indicate that small genetic mutations can cause major changes in mating behavior. Therefore, the reproductive isolation between two groups of flies may have occurred quickly after a relatively minor genetic change. Subsequent to the reproductive isolation caused by differences in mating dances in the Hawaiian flies, the populations evolved yet other differences, making them into recognizably different species. The species now differ in the anatomy of mating and reproductive anatomy, and other characteristics that make them look different to one another (for example, one species has its eyes on long stalks). These anatomical differences between species may or may not have anything to do with adaptation to their environments.

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Specialization on different food resources. Specialization of animals on different food resources will result in reproductive isolation only if individuals cross-breed primarily with other individuals that have the same specialization. The most famous examples of this are of insect populations within the same species that specialize on new food plants. They not only eat the plants but live and mate upon them, isolated from the insects on a different kind of food plant. A major example of this is the Rhagoletis flies that lay eggs on apples and hawthorns, as described previously. After a couple of centuries of isolation, the apple flies and the hawthorn flies will no longer interbreed, even when given the opportunity to do so in the laboratory. This process was observed by naturalist Benjamin Walsh, an American acquaintance of Charles Darwin, in the 19th century, and was more fully investigated in the 20th century. Another example of reproductive isolation occurring on newly introduced plant species involves the soapberry bug. Soapberry bugs have snouts about 0.36 inch (9 mm) in length that penetrate the fruit and consume contents from the seeds of soapberry trees, native to the southern United States. However, in southern Florida, golden rain trees have been imported from Asia and used as ornamentals, in the vicinity of soapberry trees. Golden rain tree fruits are smaller, thus a smaller snout is needed to penetrate it and get to the seed. Some populations of soapberry bugs have specialized on golden rain tree and seldom interbreed with the populations that still live on soapberry trees. The populations of bugs living on the golden rain trees have begun to evolve shorter beaks, about 0.28 inch (7 mm) in length. This process occurred recently, as golden rain trees were not extensively planted in Florida until the 1950s. In another example, fruit flies that resulted from the hybridization of a species of fly that lives and reproduces on blueberries and a species that lives and reproduces on snowberries have become reproductively isolated from both parental species by living on Japanese honeysuckle, which has been in North America for less than three centuries. Sometimes the isolation of populations on different food resources can result from just a small number of genetic changes. Two species of flies in the Seychelle Archipelago of the Indian Ocean are Drosophila simulans and Drosophila sechellia. The first species avoids the poisonous morinda fruit, while the second species is attracted to it, for laying their eggs. Researchers found that the species differed by only a small number of genes—just enough to produce tolerance of and attraction to morinda fruits in D. sechellia. Examples are not, however, limited to insects that live on and eat plants. Marine stickleback fishes

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494 speciation  494 invaded freshwater lakes of British Columbia after the most recent of the ice ages. Some of them had a tendency, apparently genetically based, to eat small plankton near the surface of the lakes; others preferred eating material that had settled to the bottoms of the lakes. Males and females mated preferentially in the same locations where they ate, which set them on the road to becoming two separate populations. Now, the surface- and the bottomdwelling populations have begun to evolve unique adaptations to their new modes of life: The mouths of the bottom dwellers are larger and turned downward, those of the surface dwellers smaller and not downturned. In each of these cases, natural selection has probably favored the isolating mechanism. Interbreeding between populations or species that specialize on different food resources would probably result in offspring that are inefficient at exploiting either of the parental food resources. Specialization on different symbionts. Symbiogenesis is the origin of new species as a result of the symbiotic merger of two or more species. For example, a population of bacteria may take up residence in a new kind of host cell, such as an amoeba, and reproduce inside that host cell. Whenever the amoeba reproduces, the bacteria are passed on to the new amoebae. The amoeba represents a new environment for this population of bacteria. This population is isolated from the bacteria from which it originally came and adapts to a new set of conditions. The amoebae, which have evolved a tolerance for the bacteria, may also be isolated from other amoebae if the other amoebae cannot tolerate the bacteria. By depending on each other, the amoebae and the bacteria are isolated from other amoebae and bacteria. The result can be a new species of amoeba and a new species of bacteria. In time, the bacteria may degenerate to such an extent that they are no longer recognizable as a distinct species. The first stages of this process were actually observed to occur in a laboratory setting. Differential success at fertilization. Even if individuals from two populations succeed in mating, their reproduction may still not be successful if the male reproductive cells (sperm of animals, or pollen nuclei of plants) are inferior at fertilizing the female reproductive cells (eggs of animals, or ovules of plants). The sperm cells from one population may swim faster and suffer fewer deaths on their way to the egg than the sperm cells from another population; this will tend to isolate the two populations. In flowering plants, pollen grains land on the stigma of the flower, germinate, and grow a pollen tube down into the ovary of the flower. Some pollen grains are better at doing this than others.

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first entry Frequently, the stigma of a flower will not even permit the wrong kind of pollen—either pollen that is genetically identical to it, or pollen that comes from the wrong species—to germinate in the first place. The female reproductive tract of many vertebrates represents a hostile environment through which only the hardiest sperm can travel—that is, the sperm that are best adapted to those particular conditions. As noted previously, the most famous of the postzygotic isolating mechanisms is the production of sterile hybrid offspring, as when horses and donkeys hybridize and produce sterile mules.

Investigations of Speciation Speciation has been investigated as it occurs, as described in the following sections. Experimental speciation. Speciation is difficult to observe in the wild or to demonstrate experimentally. Perhaps the best example is from fruit flies of the genus Drosophila. Researchers can raise many generations of fruit flies under laboratory conditions. Beginning with a single population of flies, they separated them into two populations: one kept in warm conditions, the other kept in cool conditions. After many generations, the two populations of flies had diverged enough that they did not interbreed when they were placed back together. This may have occurred partly from the gradual accumulation of genetic differences, but may also have involved symbiogenesis, since one of the populations lost microbes that had lived in the digestive system of its ancestors. In another fruit fly experiment, researchers kept some flies in the dark and others in the light. Not surprisingly, the flies in the dark lost the genetic ability to use visual cues for mating; they evolved mating cues based upon touch and vibration. The visual flies could not interbreed with the tactile flies. Reconstructing speciation in the wild. In natural populations where speciation may be impossible to observe in action, researchers have frequently found convincing evidence regarding how the speciation occurred. Evolutionary biologists Douglas Schemske and Toby Bradshaw (see above) have found the trait that was almost certainly responsible for the evolution of two species of Mimulus from a single ancestor, and botanist Loren Rieseberg has identified the two parental species of sunflowers whose chromosomes have come together to form the hybrid species Helianthus paradoxa. Evolutionary biologists Peter and Rosemary Grant have carefully measured divergence in beak size in two groups of Darwin’s finches, which, if it continues for a long time, may result in the formation of new species.

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speciation  495 A Few Examples of Speciation Organism

Divergence That Is Occurring

Flowering plants

Coevolution with pollinators

Hawaiian plants

Coevolution with birds for seed dispersal

Fireweeds

Polyploidy

Soapberry bugs

Different host plants

Goldenrod gall insects

Different host plants

Heliconius butterflies

Different warning colorations

Field crickets

Male courtship song

Stickleback fish

Bottom-dwelling vs. openwater-dwelling populations

Sockeye salmon

Populations that return from the sea vs. remained in lakes

Blue tits

Populations that breed in evergreen vs. deciduous oaks

Bowerbirds

Male courtship patterns

Speciation occurring in the wild. In some cases, two incipient species (not quite yet differentiated enough to be considered separate species) can exist in adjacent habitats. If there is a series of such species, each one grading into the next, it is possible that the species at the two ends of the series cannot interbreed. This would constitute a ring species. Examples include gulls of the genus Larus across the northern continents, salamanders of the genus Ensatina in the mountains of California, and the greenish warbler Phylloscopus trochiloides around the Himalayas. Evolutionary scientists have found numerous examples of speciation that is occurring in wild populations (see table). Evolution has produced far more species than any human observer would consider necessary. For example, there are well over 350,000 species of beetles. If evolution produced species only in response to environmental conditions, there would be far fewer species of organisms in the world: a few species of animals and plants best suited to moist, cool conditions, a few other species best suited to hot, dry conditions, etc. But speciation usually results when species evolve in response to one another after geographic and reproductive isolation has occurred in each.

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See also adaptation; coevolution; Darwin’s finches; Galápagos Islands; hybridization; island biogeography; natural selection; sexual selection; symbiogenesis. Further Reading Abrahamson, Warren G., et al. “Gall flies, inquilines, and goldenrods: A model for host-race formation and sympatric speciation.” American Zoologist 41 (2001): 928–938. Arnqvist, G., et al. “Sexual conflict promotes speciation in insects.” Proceedings of the National Academy of Sciences USA 97 (2000): 10,460–10,464. Blondel, Jacques, et al. “Selection-based biodiversity at a small spatial scale in a low-dispersing insular bird.” Science 285 (1999): 1,399–1,402. Carroll, Scott P., et al. “Genetic differentiation of fitnessassociated traits among rapidly evolving populations of the soapberry bug.” Evolution 51 (1997): 1,182–1,188. Condon, Marty A., et al. “Hidden neotropical diversity: Greater than the sum of its parts.” Science 320 (2008): 928–931. Dreckmann, U., and M. Doebeli. “On the origin of species by sympatric speciation.” Nature 400 (1999): 354–357. Freeman, Scott, and Jon C. Herron. “Mechanisms of speciation.” Chap. 16 of Evolutionary Analysis. 4th ed. Upper Saddle River N.J.: Pearson Prentice Hall, 2007. Futuyma, Douglas. Evolution. Sunderland, Mass.: Sinauer Associates, 2005. Grant, Peter, and Rosemary Grant. How and Why Species Multiply: The Radiation of Darwin’s Finches. Princeton, N.J.: Princeton University Press, 2008. Grant, Verne. Plant Speciation, 2nd ed. New York: Columbia University Press, 1981. Gray, D. A., and W. H. Cade. “Sexual selection and speciation in field crickets.” Proceedings of the National Academy of Sciences USA 97 (2000): 14,449– 14,454. Howard, D. J., and Stuart H. Berlocher, eds. Endless Forms: Species and Speciation. New York: Oxford University Press, 1998. Hunt, Dana E., et al. “Resource partitioning and sympatric differentiation among closely related bacterioplankton.” Science 320 (2008): 1,081–1,085. Irwin, Darren E., et al. “Speciation by distance in a ring species.” Science 307 (2005): 414–416. Jiggins, Chris D., et al. “Reproductive isolation caused by colour pattern mimicry.” Nature 411 (2001): 302–305. Martin, Robert A. Missing Links: Evolutionary Concepts and Transitions through Time. Sudbury, Mass.: Jones and Bartlett, 2004. Mayr, Ernst. What Evolution Is. New York: Basic Books, 2001.

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496 spiders  496 Ortíz-Barrientos, Daniel, and Mohamed A. F. Noor, “Evidence for a one-allele assortative mating locus.” Science 310 (2005): 1,467. Palumbi, Stephen R. The Evolution Explosion: How Humans Cause Rapid Evolutionary Change. New York: Norton, 2001. Price, Jonathan P., and Warren L. Wagner. “Speciation in Hawaiian angiosperm lineages: Cause, consequence, and mode.” Evolution 58 (2004): 2,185–2,200. Retchless, Adam C., and Jeffrey G. Lawrence. “Temporal fragmentation of speciation in bacteria.” Science 317 (2007): 1,093–1,096. Rieseberg, Loren, and John H. Willis. “Plant speciation.” Science 317 (2007): 910–914. Rundle, H. D., et al. “Natural selection and parallel speciation in sympatric sticklebacks.” Science 287 (2000): 306–308. Ryan, Peter G., et al. “Ecological speciation in South Atlantic island finches.” Science 315 (2007): 1,420–1,423. Sargent, Risa D. “Floral symmetry affects speciation rates in angiosperms.” Proceedings of the Royal Society of London B (Biology) 271 (2004): 603–608. Schilthuizen, Menno. Frogs, Flies, and Dandelions: The Making of Species. New York: Oxford University Press, 2001. Uy, J. A. C., and G. Borgia. “Sexual selection drives rapid divergence in bowerbird display traits.” Evolution 54 (2000): 273–278. Via, Sara. “Sympatric speciation in animals: The ugly duckling grows up.” Trends in Ecology and Evolution 16 (2001): 381–390. Wake, D. B. “Incipient species formation in salamanders of the Ensatina complex.” Proceedings of the National Academy of Sciences USA 94 (1997): 7,761–7,767. Weir, Jason T., and Dolph Schluter. “The latitudinal gradient in recent speciation and extinction rates of birds and mammals.” Science 315 (2007): 1,574–1,576. Whibley, Annabel C. “Evolutionary paths underlying flower color variation in Antirrhinum.” Science 313 (2006): 963–966. Zimmer, Carl. “What is a species?” Scientific American, June 2008, 72–79.

spiders  Spiders are the largest group of arachnids, which is the largest group of chelicerates, in the arthropod phylum. Arthropods have an external skeleton made primarily of chitin. This exoskeleton includes jointed appendages, which includes antennae, mouthparts, wings, and legs. Spiders have eight legs and no wings. Many arthropods have head, thorax, and abdomen body regions; in spiders, the head and thorax are fused into a cephalothorax. Therefore, a spider can be easily distinguished from an insect, because a spider has two body parts and

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first entry

Spiders usually eat insects, but this large tropical spider has captured a gecko lizard.  (Aidan Jones)

eight legs, while an insect has three body parts and six legs. Spiders live everywhere except Antarctica and the oceans (the small, delicate sea-spiders are arachnids but not spiders). Spiders have mouthpart appendages called chelicerae that have venom glands. The chelicerae of spiders have poison fangs, which retract inside a groove like the blade of a pocketknife. Almost all spiders are predators that paralyze their victims with venom and then inject enzymes that digest the victim; they suck the digested products. Spiders cannot chew. Because of this method of eating, spiders usually consume other arthropods, although spiders eat vertebrates (see photograph). If a small bird gets caught in a spider web, a large spider will not necessarily reject it. Most spider attacks on vertebrates, however, are defensive. One species of jumping spider, Bagheera kiplingi, is primarily vegetarian. Behind the chelicerae, ahead of the walking legs, are pedipalps that manipulate food. Spiders, like other arachnids, have an open circulatory system in which the blood bathes all of

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spiders  497 the internal organs. The blood contains blue, copper-based hemocyanin that carries oxygen. Some spiders, like most terrestrial arthropods, have tracheae, which are breathing passages that open to the outside. Some spiders, like most aquatic arthropods, have gills, but these gills are enclosed inside a body chamber; these chambers are called book lungs. Like most arthropods, spiders have a pair of nerve cords running along the lower (ventral) surface of the body. In most spiders, the nerves form a large ganglion in the cephalothorax—the spider version of a brain. Spiders have eight eyes. The smaller ones are capable only of detecting movement, but the large ones can, unlike the eyes of most arthropods, form images. Some jumping spiders have eyes with with four visual pigments, and may therefore discriminate colors more effectively than mammals, which have only three visual pigments. Spiders produce silk from an abdominal gland. Spider silk protein is one of the strongest materials known. Some spiders produce complex orb-shaped webs with sticky silk, in which small animals become entangled. The spider then paralyzes the animal and wraps it in silk. The spider knows which strands of the web are sticky and which are not, walking only on the latter. Other spiders produce cobwebs. Some spider webs are funnel-shaped, encouraging the prey to fall into the chamber of the waiting spider. The trapdoor spiders (family Ctenizidae) live in burrows that are covered with a hinged door made of soil, vegetation, and silk. When a prey animal comes by, the spider quickly opens the door and grabs the victim. Bolas spiders swing a line of silk, with adhesive compounds on the end, in the air to capture insects. They lure male moths within range by producing the female moth pheromone. Spiders often consume and reuse their own silk. All spiders produce silk, but many spiders do not use silk to obtain prey. Many, such as tarantulas, wander in search of prey. Jumping spiders (family Salticidae), the largest family of spiders, jump up to 80 times the distance of their own body lengths, first securing themselves with a strand of silk. To do this, they use not only strong muscles, but also pressurized body fluid. Crab spiders wait in vegetation, often near flowers the coloration of which they closely mimic, and grab prey with strong front legs (see photograph). Fishing spiders (see above) walk on the surface tension of water, and when they detect movements of prey underwater, they grab the prey and eat it. Spiders of the genus Argyroneta build an underwater structure of silk, which they fill with air that they carry from the surface.

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Some spiders live in societies of up to 50,000 individuals that cooperatively forage for prey and live together in common webs. They do not have social organization like that of the hymenopteran social insects. However, many spiders take advantage of the social organization of ants. Some spiders live near, or even inside of, ant colonies. They thereby gain protection from predators. Sometimes they feed on the ants or on the aphids that the ants tend as sources of honeydew. These spiders are ant mimics, and mimic ants in numerous ways, such as the following: ●●

●●

●●

●●

Spiders have two body parts, while ants have three. Ant-mimic spiders often have constrictions in the middle of the cephalothorax, giving the appearance of three body parts. Spiders do not have antennae, but ants do. Ant-mimic spiders often wave their front legs in apparent imitation of antennae. Spiders do not have large compound eyes, but ants do. Ant-mimic spiders often have large color patches around the largest two of their eight eyes, making them look larger. Ant-mimic spiders often imitate the behavior of ants. For example, jumping spiders that imitate ants do not jump, and antmimic spiders walk in a zig-zag, ant-like fashion. Synemosyna spiders imitate Pseudomyrmex ants by walking on the outside edges of leaves. While Amyciaea spiders do not closely resemble Oecophylla ants, they imitate the behavior of dying ants, thus attracting workers. Some ant-mimic spiders hold an ant that they have just killed in their jaws, concealing their identity behind that of the dead ant.

This crab spider waits for prey on a Mexican poppy (Eschscholzia mexicana) in the saguaro desert of ­Arizona.  (Stanley A. Rice)

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498 spiders  498 ●●

The spider Habronestes bradleyi releases 6-methyl-5-hepten-2-one, the same chemical that the ant Iridomyrmex purpureus uses as an alarm signal. This chemical attracts worker ants to the spider, which then eats them.

Ant-mimic spiders also produce a pheromone that makes the ants react to them as if they were ants that belong in the home colony. Although spiders are excellent predators, they are often prey. In particular, “tarantula hawk” wasps (family Pompilidae) sting tarantulas but do not kill them, drag them into burrows, and lay eggs in them. Sexual reproduction in spiders is a touchy and dangerous operation. After the final molt, the adult male stops eating. The male spider, often much smaller than the female, puts sperm on one of his front appendages and goes searching for a female. He uses special approach signals so that he is not mistaken for prey. The male inserts the appendage, with sperm, into a pore in the female’s abdomen. Mating in scorpions is even more risky than in spiders, involving complex dances and the transfer of sperm into the female’s abdomen by one of the male’s legs. In some species, the female spider eats the male after mating. Female spiders frequently take very good care of their offspring. They often protect the egg case. Female wolf spiders (family Lycosidae) carry their egg cases, and when the spiderlings hatch, the mother may carry them on her back until they are large enough to live by themselves (see photograph). Frequently, a female spider will paralyze a small animal, not killing it, and lay her eggs in it; her offspring eat the still-living victim. In some species, the mother spider allows her hatchlings to eat her body. The most primitive spiders (that is, those that most closely resemble the common chelicerate ancestor) are the tarantulas, which are large wandering predators. New World tarantulas have irritating, defensive hairs that can be poisonous to small animals. Their chelicerae point downwards. Most spiders, in contrast, have chelicerae that point diagonally forward. Tarantulas produce silk but use it for building nests or lining burrows. Most range in size from 1 to 4 inches (2.5 to 10 cm), although the Goliath birdeater (Theraphosa blondi) can be 10 inches (28 cm) in length (including the legs). Tarantulas prey mainly on other arthropods, but some can kill mice or birds. Nine of the most venomous spiders in the world live in Australia. Two of them are large funnel-web spiders. The Sydney funnel-web (Atrax robustus), found only within about 60 miles (100 km) of Sydney, is responsible for most deadly spider bites in

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first entry Australia, especially the males that wander into suburban areas. The northern tree funnel-web spider (Hadronyche formidabilis) is also dangerous. The Australian redback spider (Lactrodectus hasseltii) is a relative of the American black widow spider. In the United States, the two native species of poisonous spiders are the black widow ­( Lactrodectus mactans) and the brown recluse (Loxosceles reclusa). Venom from female black widow spiders causes a buildup of the neurotransmitter acetylcholine. This neurotransmitter normally stimulates muscle contractions; when it builds up, excessive muscle contractions and high blood pressure result. The toxin of the brown recluse destroys red blood cells and induces the white blood cells to attack surrounding tissues. Fortunately, these bites are seldom fatal. Most spiders bite in defense, although the Brazilian wandering spider Phoneutria nigriventer readily attacks larger animals, including humans. Despite the fear that humans have of spiders (exacerbated by the recognized psychological term arachnophobia), there were only about 100 confirmed cases of human deaths by spider bite in the 20th century. See also arthropods.

Some spiders take care of their offspring. This mother wolf spider carries baby spiders on her abdomen in the Badlands of South Dakota.  (Stanley A. Rice)

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succession, ecological  499 Further Reading Allen, Rachel A., et al. “Exploitation of an ant chemical alarm signal by the zodariid spider Habronestes bradleyi Walckenauer.” Proceedings of the Royal Society of London B (Biology) 263 (1996): 69–73. Andrade, Maydianne C. B. “Sexual selection for male sacrifice in the Australian redback spider.” Science 271 (1996): 70–72. Dalton, Stephen. Spiders: The Ultimate Predators. Richmond Hill, Ont.: Firefly Books, 2008. Elgar, Mark A., and Rachel A. Allan. “Chemical mimicry of the ant Oecophylla smaragdina by the myrmecophilous spider Cosmophasis bitaeniata: Is it colonyspecific?” Journal of Ethology 24 (2006): 239–246. Gastreich, K. R. “Trait-mediated indirect effects of a theridiid spider on an ant-plant mutualism.” Ecology 80 (1999): 1,066–1,070. Hillyard, Paul. Book of the Spider. New York: Harper Perennial, 1998. ———. The Private Life of Spiders. Princeton, N.J.: Princeton University Press, 2008. Johnson, J. Chadwick, and Andrew Sih. “Fear, food, sex, and parental care: A syndrome of boldness in the fishing spider, Dolomedes triton.” Animal Behaviour 74 (2007): 1,131–1,138. Maddison, Wayne, and Jerzy Proszynski. “Jumping spiders of the world: A confederation of projects on salticid systematics and diversity.” Available online. URL: http:// salticidae.org/jsotw.html. Accessed May 16, 2011. Nelson, Ximena J., and Robert R. Jackson. “Collective Batesian mimicry of ant groups by aggregating spiders.” Animal Behaviour 78 (2009): 123–129. ———. “Anti-predator crèches and aggregations of antmimicking jumping spiders (Araneae: Salticidae). Biological Journal of the Linnean Society 94 (2008): 475–481. ———, et al. “Living with the enemy: Jumping spiders that mimic weaver ants.” Journal of Arachnology 33 (2005): 813–819. Pechmann, Matthias, and Nikola-Michael Prpic. “Appendage patterning in the South American bird spider Acanthoscurria geniculata (Araneae: Mygalomorphae). Development Genes and Evolution 219 (2009): 189–198. Vollrath, Fritz, and Paul Selden. “The role of behavior in the evolution of spiders, silks, and webs.” Annual Review of Ecology, Evolution, and Systematics 38 (2007): 819–846. Wise, David H. Spiders in Ecological Webs. Cambridge, U.K.: Cambridge University Press, 1995.

succession, ecological  Areas disturbed by fire, storms, or landslides (ecological disturbances) are temporary microhabitats. These areas quickly fill with plant growth and are no longer open to

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new plant colonists that require open spaces to germinate. In early-successional habitats, soon after the disturbance, plants and animals may thrive in conditions of reduced competition, but as the areas fill with more species and become late-successional habitats, competition becomes more intense. Consider the case in which a plot of land from the deciduous forest of eastern North America has been cleared for farming (an example of an ecological disturbance), then abandoned (see the bottom photograph on page 504). Most of the first plants to live in the disturbed area are annuals, which are plants that live only one year (see table on page 503). They grow quickly in the abundant nutrients and light. These colonizing plants are often the familiar weeds of roadside and farm. They reproduce during their first year, then they die. If the seeds are small, they may disperse over a wide range, and a few of them may land in a newly disturbed area. Weed seeds may remain dormant but alive in the soil in that place for decades or even centuries, until the next disturbance occurs there. During the first season, the disturbed area is thick with annuals. In their shade, seedlings of herbaceous perennials (plants that live for several to many years, for example the goldenrod) grow slowly. Although they grow slowly during their first year, they store nutrients in their stems or roots. At the beginning of the second season, many seeds of the annuals may germinate, but the perennials grow faster, due to the food reserves they accumulated the previous year. During the second year, the annuals grow slowly in the shade and usually die without reproducing. Starting the second year or soon thereafter, the perennials dominate the field. These herbaceous perennials sprout from underground buds each year. Bushes and trees grow up through their shade, becoming more common until they in turn dominate. The first trees to dominate the field are the shadeintolerant trees, for example ashes, cherries, and locusts. They are called shade-intolerant because their seedlings must germinate in the bright light of an open field. Some shade-intolerant shrubs and trees spread not so much by seeds as by underground stems. They form a large clump of trunks (see figure on page 504). The seedlings cannot grow in the shade of the parents; therefore, shade-intolerant trees dominate the habitat only temporarily. The seedlings of shade-tolerant trees, such as maples, grow up in the shade of the shadeintolerant trees. Forest floor herbs that cannot tolerate open fields now grow in the shade. The plants in each stage shade out the plants of the preceding stage. Finally, the old forest clearing may be filled with the same kind of forest that was present prior to disturbance. A maple forest, for example, can perpetuate itself, since maple seedlings can grow up in the shade of adult maples. No further changes in

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500 succession, ecological 500

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During secondary succession, plants grow in disturbed areas with intact soil. Annual weeds grow most rapidly and are replaced in turn by perennial weeds, shrubs, and then trees. The trees that grow latest in the successional series are the species whose seedlings can grow in the shade of the adults.

species composition usually occur, in the absence of further disturbance, in such a community. ecologists often use metaphors to describe the self-perpetuating forest: it is called climax forest as if it is the culmination of a story, or mature forest, as if succession were the growth stages of an organism. in the eastern forests of the United States, between 100 and 200 years must pass before a climax species composition is reached. as the climax forest gets older, its dominant trees get larger. in the eastern deciduous forest zone of the United States, few people will ever see a true “virgin forest.” Practically all of the deciduous forests have been cut down within the past two centuries. although many of these forests have grown back and once again contain their original species (see the bottom photograph on page 504), they no longer contain the huge old trees that the native americans knew and that were described by the first european explorers. although some early-successional species die out during the process of succession, others persist near the edge of the developing forest. Many shade-tolerant forest-floor plants can survive only in the shade of the climax trees. net species diversity, therefore, increases during succession in these cases. along with plant succession, there is also a succession of animals. Being mobile, animals are not

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as confi ned to a particular successional stage as are most plants. Many mammals and birds may fi nd abundant food in early-successional zones but can also fly or run into the deep woods. Many insects specialize on certain food plants and are therefore restricted in the successional habitat in which they live. caterpillars of the monarch butterfly, for example, live exclusively upon milkweeds that grow in recently disturbed areas. Many species of small animals, and fungi, may be able to survive only in the cool, moist soils of the forest floor. During succession, the early colonists change the soil, light, temperature, and humidity conditions, which may facilitate the survival of species that arrive later. they might also inhibit the survival of species that arrive later. in other words, the early-successional species set the stage for many of the latersuccessional species. this is not true, however, of all of the later-successional species. Shade-tolerant tree species may begin to grow the very first season after disturbance, surviving in the shade of the weeds. they may dominate the habitat later not because they arrived later but because they grew more slowly. Other kinds of disturbances result in different patterns of succession. if the forest burned instead of being converted into a farm, succession would follow a different pattern. Some trees might escape the

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succession, ecological  501

“If Humans Vanished . . .”

W

hat would happen to the world if humans vanished from it? Such a thing is very unlikely to happen. Humans are so numerous and so adaptable that there will probably be at least a few people on the Earth until the Sun enters its final throes of death. What is more likely to happen is that human civilization could collapse. The modern human economy and system of food production depend entirely upon fossil fuels and advanced technology. While there would still be sunshine and photosynthesis, there would not be fuel and machinery for planting, growing, and harvesting crops, for processing food, or for transporting food to where people can obtain it. Even the availability of food does not guarantee survival, as was evidence during the Irish Potato Famine, when people starved because they could not buy the plentiful food in the marketplace. The human population of nearly 7 billion cannot conceivably be supported by hunting and gathering, especially by a mob of hungry people pouring out of cities and towns. Even rural people survive on groceries. The few that are lucky enough to find wild hickory nuts (or to even know what they are) will discover that the shells are too hard to break except with a very large hammer. To survive by cracking hickory nuts uses more calories than the nuts would provide. The few naturalists who know that greenbriar shoots are edible would find them only in the spring. As soon as the ammunition ran out, few hunters would know what to do, aside from wrestling a few turtles. Even though the extinction of humans is extremely unlikely, such a disappearance is a useful scenario for understanding human impact upon Earth. Much of what humans have done to the Earth would be quickly erased. Modern buildings, less sturdy than ancient ones, would soon collapse. Mayan buildings have been almost buried by soil and vegetation during the past millennium. Ancient buildings in dry environments have survived a bit longer.

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Nearly all of the plants and animals that humans have bred as crops and livestock would quickly become extinct. They largely depend upon humans for their survival. Tomatoes, for example, cannot produce seeds unless humans keep their fruits from touching the ground and rotting. Ears of corn would sprout into a dense mass of seedlings, all of which would probably die. Poodles would die instantly. Humans have bred crops and livestock for purposes other than survival in the wild. Some livestock, pets, and plants would become feral, as has happened with horses, swine, cats, and kudzu. Pest animals and weeds have adapted to the conditions that humans have created. Some of them, such as rats, would continue to thrive. But as humans are the major source of ecological disturbances, the weeds and pests that live in such conditions would eventually become rare. The weeds that thrive in agricultural fields are generally not the same ones that colonize after disturbances, such as floods and fires, in the natural world. For example, the velvetleaf weed (Abutilon theophrasti), which today thrives in soybean fields and in recently abandoned farmland, would grow only occasionally on the banks of streams and lakes. The human contribution to the diversity of species and, especially, varieties within species would vanish quickly. The new rulers of the Earth would be species that existed before humankind. Some disturbances would become more common after the disappearance of most humans than they now are. Fire suppression would cease, and fires might once again clear vast areas in which grassland and chaparral plant species, and the animals that live with them, could grow. Human population collapse has occurred before. When Europeans introduced diseases such as smallpox to North American native populations, the germs spread faster than the Europeans,

and annihilated up to 90 percent of the natives. At that time, population explosions of wild animal species occurred. Natives in the middle of North America had hunted bison and passenger pigeons; with the collapse of hunting, populations of pigeons and bison vastly increased. Natives in the southeastern part of North America had fished extensively; with their disappearance, populations of fish—and of alligators that ate them—exploded. This explains the observations of Europeans and Americans, such as botanist William Bartram, who marveled at the hundreds of alligators in every lake and river in Florida; and they assumed North America had always been this way. If humans vanished today, a similar phenomenon would probably not occur, since most sustenance comes from helpless livestock rather than wild game. One human artifact would persist for millennia: the high levels of carbon dioxide in the atmosphere, contributing to a greenhouse effect. The Earth would be warmer for thousands of years because humans had been on it. However, this greenhouse effect would not be very devastating, except for tundra species whose habitat would vanish forever. The main reason that the greenhouse effect threatens biodiversity is because humans have blocked the corridors of movement by which, in previous millennia, plants and animals have adjusted to global climate changes by migrating. With humans out of the way, global warming would probably cause even fewer extinctions than the end of the most recent ice age. Indeed, the leading explanation for the Pleistocene extinction is the overkill hypothesis, in which humans killed enough of the large animals in North America that their populations could not persist. Even coral reefs, already dying because carbon dioxide is acidifying ocean waters, would (continues )

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502 succession, ecological  502

(continues )

r­ ecuperate in a few hundred years after human disappearance. Perhaps the human artifact that would persist the longest, for several million years, would be the toxins that industry manufactures. Heavy metals and persistent organic molecules already recycle through the food web over and over. And then there is plastic. Plastic is forever. No known natural process breaks it down. Save for a little bit of plastic destroyed during incineration, every bit of plastic ever manufactured still exists. Ultraviolet radiation and oxygen in the air can make it brittle, but it simply fractures into smaller and smaller pieces. This makes plastic trash even more dangerous. When the fragments are small, many animals consume it with the plankton that they normally eat. Natural selection has not produced seabirds that can distinguish between a fish and a

first entry

floating piece of plastic. In some places, each handful of sand is 20 percent plastic, and plastic fragments are up to six times as abundant as plankton. There are seven major gyres of ocean current that trap even large pieces of plastic into large, and almost permanent, garbage dumps. Long after the lights of the cities cease to be visible on the dark side of the Earth, long after the last reservoirs fill with silt and their rivers rush over the dams like natural waterfalls, and entropy has scrambled the last of the digital data, flakes of plastic will still be swirling through the ecosystems of the Earth. See also disturbances, ecological; greenhouse effect; greenhouse effect and biodiversity; invasive species; Pleistocene extinction; succession, ecological.

Further Reading Cronon, William, ed. Uncommon Ground: Rethinking the Human Place in Nature. New York: Norton, 1995.

fire and serve as a source of seeds that would hasten the regrowth of that species. Many perennial plants in the forest may sprout from surviving underground parts. In many cases, the events that follow a fire are not succession at all. If a grassland burns, most of the plants that grow after the fire are simply sprouts from the plants that were there before. If a savanna burns, the grasses may simply spread underneath the charred tree trunks. Each region of the world has its own set of annuals, herbaceous perennials, shade-tolerant trees, and shade-intolerant trees and has its own unique trajectory of succession. In the Rocky Mountains, aspen (Populus tremuloides) is a common early-successional tree, while spruce (Picea glauca) is a common late-successional tree. In the Sierra Nevada, giant sequoia (Sequoiadendron giganteum) is an earlysuccessional tree, and white fir (Abies concolor) is a late-successional tree. Giant sequoias grow to prodigious sizes and live for millennia but do not reproduce well except in sunny openings. Fire suppression has resulted in reduced regeneration of sequoias and the spread of white firs. In tropical rain forests, large natural disturbances are rare. When a canopy tree falls, tree seedlings grow rapidly and fill the gap in a decade or less. In some cases, there are many seedlings of canopy trees growing slowly in the under-

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Donlan, Josh, et al. “Re-wilding North America.” Nature 436 (2005): 913–914. Quammen, David. “The weeds shall inherit the Earth.” The Independent, November 22, 1998, 30–39. Rathje, William, and Cullen Murphy. Rubbish! The Archaeology of Garbage. Tucson: University of Arizona, 2001. Sanderson, E. W., et al. “The human footprint and the last of the wild.” BioScience 52 (2002): 891–904. Tegmark, Max, and Nick Bostrum. “How unlikely is a doomsday catastrophe?” Nature 438 (2005): 754. Ward, Peter, and Donald Brownlee. The Life and Death of Planet Earth. New York: Henry Holt, 2002. Weisman, Alan. The World without Us. New York: Picador, 2008. Zalasiewicz, Jan. The Earth after Us. Oxford, U.K.: Oxford University Press, 2009.

story. If a disturbance does not happen soon, these seedlings will die. But if a disturbance does occur, these seedlings begin to grow rapidly. They win the competitive race by waiting in the shade as seedlings rather than seeds. Furthermore, within any given area, the plant species that dominate each successional stage will depend on the species of seeds that are in the soil or brought in by wind or animals. If there are no nearby maple forests, it may take a plot of land a very long time to grow back into a maple forest, for the seeds must travel from a great distance, and it may be two or three generations before maples form a continuous cover. Moreover, soil plays an important role in the makeup of the climax community. In Michigan forests on good soil, the climax species composition includes maples, beeches, and hemlocks; however, on glacial sand and gravel, the mature forest is dominated by jack pines. Secondary succession occurs when the vegetation is destroyed but the soil, even if disturbed, remains in place. Because soil is present, colonizing plants can grow immediately. The soil contains seeds that begin to grow immediately. Disturbances such as fires and floods do not usually remove the soil. Some kinds of disturbance, however, create new land surface, on which soil must be built before

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succession, ecological  503

Plant Species at Different Stages of Ecological Succession   in Eastern North America Stage

Scientific Name

Common Name

Herbaceous plants that stabilize the dunes:

Ammophila breviligulata Calamovilfa longifolia Lithospermum caroliniense Schizachyrium scoparium

American beach grass Prairie sandreed Puccoon Little bluestem

Shrubs

Arctostaphylos uva-ursi Juniperus communis Prunus pumila

Bearberry Common juniper Sand cherry

Early trees

Pinus resinosa Pinus strobus

Red pine White pine

Late trees

Acer rubrum Quercus rubra Tilia americana

Red maple Red oak Basswood

Annuals

Abutilon theophrasti Amaranthus retroflexus Chenopodium album Conyza canadensis Polygonum pensylvanicum Xanthium strumarium

Velvetleaf Pigweed Lamb’s-quarters Canada fleabane Knotweed Cocklebur

Herbaceous perennials

Aster pilosus Solidago canadensis

Hairy aster Canada goldenrod

Shade-intolerant trees and shrubs

Acer negundo Acer saccharinum Diospyros virginiana Gleditsia triacanthos Platanus occidentalis Populus deltoides Prunus serotina Rhus glabra Robinia pseudoacacia

Boxelder* Silver maple* Persimmon Honey locust Sycamore* Cottonwood* Black cherry Sumac Black locust

Shade-tolerant trees

Acer saccharum Fagus grandifolia Quercus velutina

Sugar maple Beech Black oak

Forest understory herbs and vines

Osmorhiza longistylis Parthenocissus quinquefolia Polygonatum biflorum Sanicula gregaria Smilax bona-nox Toxicodendron radicans Vitis rotundifolia

Sweet cicely Virginia creeper Solomon’s-seal Snakeroot Greenbriar Poison ivy Muscadine grape

Lake Michigan Dunes (primary succession)

Old-Field Succession (secondary succession)

*Primarily along rivers and lakes.

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504 succession, ecological  504

A persimmon tree (Diospyros virginiana) grows in a grassland, beginning the process of transforming the grassland into forest. The “tree” looks like numerous small trees, but they are all connected underground and are a singe individual.  (Stanley A. Rice)

plants can grow on it. During primary succession, plants contribute to the buildup of the soil. One of the earliest examples of primary succession to be studied, and still the most famous, is the development of a deciduous forest on top of sand dunes along Lake Michigan. Botanist Henry Chandler Cowles, like many other people, had visited the southern shores of Lake Michigan, near Chicago, an area now preserved in the Indiana Dunes National Lakeshore. However, Cowles saw more than just the beautiful sand and the oak forest. A graduate student and later a professor of botany at the University of Chicago, he realized that these dunes and forests were constantly changing. The changes were too slow to actually observe. Because Cowles used the present as the key to the past, he was able to conduct the first scientific study of ecological succession, which was published about 1900. Over thousands of years, sand dunes have accumulated along the southern shore of Lake Michigan. Even though the weather in this region is moist, the sand dunes are a dry microenvironment, because the sand cannot hold very much water. Plants that live in the open dunes near the lake must tolerate a wide range of challenges: The sand is dry, becomes very hot in the sun, and shifts in the wind, sometimes burying the leaves and sometimes exposing the roots of the plants. Only a couple of species of grass are able to colonize these sand dunes. The grasses not only survive in the dunes but also begin to change the dunes. Their stems and roots hold down the sand, while their dead leaves, stems, and roots contribute organic matter and humus to it, enriching it with nutrients (see table and figure). The humus begins to hold water from the

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first entry abundant rains. Lack of rain prevents this process from occurring very much in desert sand dunes. Other plants, such as bushes, grow in the sand once the grasses have stabilized and enriched it. The dune is no longer merely sand, although it is still mostly sand. Pine trees begin to grow amidst the bushes. In their shade, the dunes are cooler and do not dry out as much. Pine needles further enrich the soil. Other bushes and trees begin to grow that could not survive in the bright sun and dry sandy soil. Meanwhile, the original grasses have been shaded out. Forest trees such as oak and basswood grow up under and shade out the pines. After about a century, an oak forest is growing on what was once a sand dune (see photograph on page 506). Sugar maple (Acer saccharum) and beech (Fagus grandifolia) dominate the general region, but oak forests dominate the old dunes because the soil consists only of sand and leaf litter and holds less water than the loam soils in which maples grow. Because dunes accumulate along the shore, the dunes become progressively older inland. A visitor can walk away from the shore and, in effect, be walking along a time axis of succession. In just a

A forest of maples and hemlocks grows in what was a farm during Revolutionary War times at Teatown Lake, north of New York City.  (Stanley A. Rice)

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succession, ecological 505 hundred meters, a visitor or a scientific investigator can walk through centuries of succession. Primary succession also occurs on lava flows in Hawaii. When the lava cools into rock, it is a barren, sterile surface. Gradually, dust (with mineral nutrients) accumulates. Seeds and spores blow in, accumulating in the deeper fissures, where the most water is found. Ferns and ohia trees (Metrosideros polymorpha) begin to grow in these fissures (see photograph on page 507). their roots help crack the lava into smaller pieces, and their dead leaves help to build up a soil. Ferns and ohia trees will eventually dominate the mature forest. Primary succession depends upon the amount of rainfall; rain forest cannot grow on old lava flows in those areas of Hawaii that receive little rain. in some examples of succession, new land surface is formed, but this surface may consist of rich soil brought in from elsewhere. Ponds, for instance, gradually fi ll in with eroded soil and with dead plant material. the new soil thus created is rich and supports the growth of emergent plants such as cattails and rushes that grow in water but are rooted in soil. these plants also help build up the soil by contributing their dead leaves and by trapping silt. Once enough soil has accumulated that the standing

water has been replaced by mud, seedlings of trees such as willow and boxelder (Acer negundo) can begin growing. these kinds of trees are typically found only along streams, rivers, and pond margins (see table on page 503). they are shade-intolerant, however, and may be replaced by maples that grow in their shade. a pond is a temporary habitat, and may eventually be replaced by a maple forest, unless further disturbances (for example, flooding) occur. Succession can occur as a bog fi lls in, just as in a pond. However, when a bog becomes a forest, the soil remains acidic because the soil consists mostly of dead peatmoss. the acidity of the soil restricts the types of plants that can grow in the climax forest that grows where a bog once existed. Disturbance and succession continually occur along rivers, as soil erodes from or is deposited along the bank. in the new soil, seedlings of boxelder and other streamside trees germinate and grow, beginning the process of succession all over.

ExCESSIvE dISrupTIoNS of EColoGICal CommuNITIES a million years ago, when there were only a million people in the world, it did not really matter what

During primary succession, soil must build up before most plants can grow. The plants help to build up the soil. In the dunes south of Lake Michigan, grass rhizomes hold down the sand and contribute organic material to it, allowing shrubs and then trees to grow in turn. The plants themselves change the environmental conditions of moisture, nutrients, light, organic matter, and wind.

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506 succession, ecological  506

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On the sand dunes south of Lake Michigan, only a few seedlings can sprout, and most of these die (left). Once the seedlings and grass rhizomes have stabilized the soil, trees can grow. A forest of linden (Tilia americana) and red oak (Quercus rubra) grows on what was once a sand dune (right).  (Stanley A. Rice)

humans did to the Earth. When a caveman threw out a stone tool, it was just a rock. But today, there are 7 billion people, and when they throw out dead batteries, it is toxic waste. Both because of prodigious population and toxic technology, every little thing humans do now seems to be harmful to the Earth. Some disturbances caused by humans are more disruptive than others. Some human activities— particularly carrying species to new locations, causing extinctions, and creating new kinds of pollution—have disrupted ecological communities in ways that may require millions of years for recovery. Severe disturbances have occurred during the Earth’s history, for instance the giant asteroid believed to have struck the Earth 65 million years ago, causing the Cretaceous extinction. Severe disturbances continue to occur, for instance volcanic eruptions. The 1883 eruption of Krakatoa in Southeast Asia produced a noise that could be heard— and a tidal wave that reached—thousands of miles. Ecological communities have recovered from each of these disturbances, however. Communities do not so easily recover from repeated disturbances, such as mowing, soil compaction, and other disturbances caused by humans.

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Human technology creates many disturbances that are not only repeated but also quite different from natural ones. During the brief period of Earth history in which human technology has existed, species have not adapted to these new kinds of disturbances, particularly the discharge of poisonous pollutants. Around the world, extensive disruption of soil is occurring due to deforestation and overgrazing. The result is often the spread of deserts. Extensive soil erosion resulting from deforestation has contributed to the downfall of civilizations all over the world, for instance those of the Greeks and Romans, of the Anasazi of western North America, and of the Polynesians on Easter Island in the Pacific Ocean. No species has disturbed as many square miles of land surface or polluted as much ocean as have humans. See also Essay: “If Humans Vanished . . .”; competition, ecological; disturbances, ecological. Further Reading Bazzaz, Fakhri A. “Succession on abandoned fields in the Shawnee Hills, southern Illinois.” Ecology 49 (1968): 924–936. ———. “The physiological ecology of plant succession.” Annual Review of Ecology and Systematics 10 (1979): 351–371.

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symbiogenesis  507

Ohia trees (Metrosideros polymorpha) grow from the cracks of pahoehoe lava on the Kona coast of the Big Island of Hawaii. In this unusual pattern of succession, the first plants to grow on the lava are also the plants that dominate the forests that will later cover the lava.  (Stanley A. Rice) ———. Plants in Changing Environments: Linking Physiological, Population, and Community Ecology. New York: Cambridge University Press, 1996. Christensen, Norman L., and Robert K. Peet. “Convergence during secondary forest succession.” Journal of Ecology 72 (1984): 25–36. Cowles, Henry Chandler. “The ecological relations of the vegetation on the sand dunes of Lake Michigan.” Botanical Gazette 27 (1899): 95–117, 167–202, 281– 308, 361–391. Dale, Virginia H., Frederick J. Swanson, and Charles M. Crisafulli, eds. Ecological Responses to the 1980 Eruption of Mount St. Helens. New York: Springer, 2005. Foster, David R., and John D. Aber, eds. Forests in Time: The Environmental Consequences of 1,000 Years of Change in New England. New Haven, Conn.: Yale University Press, 2004. Gill, David S., and Peter L. Marks. “Tree and shrub seedling colonization of old fields in central New York.” Ecological Monographs 61 (1991): 183–205. Hopfensperger, Kristine N. “A review of similarity between seed bank and standing vegetation across ecosystems.” Oikos 116 (2007): 1,438–1,448. Körner, Christian, et al. “Small differences in arrival time influence composition and productivity of plant communities.” New Phytologist 177 (2008): 698–705.

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Lichter, John. “Colonization constraints during primary succession on coastal Lake Michigan sand dunes.” Journal of Ecology 88 (2000): 825–839. MacLeish, William H. The Day before America: Changing the Nature of a Continent. New York: Houghton Mifflin, 1994. Pickett, Steward T. A. “Succession: An evolutionary interpretation.” American Naturalist 110 (1976): 107–119. ———. “Population patterns through twenty years of oldfield succession.” Plant Ecology 49 (1982): 45–59. Pielou, E. C. After the Ice Age: The Return of Life to Glaciated North America. Chicago: University of Chicago Press, 1992. Rice, Stanley A. “Plants heal the landscape.” Chap. 9 in Green Planet: How Plants Keep the Earth Alive. Piscataway, N.J.: Rutgers University Press, 2009. Rosenzweig, Michael. Win-Win Ecology: How the Earth’s Species Can Survive in the Midst of Human Enterprise. New York: Oxford University Press, 2003. Wardle, David A., et al. “The response of plant diversity to ecosystem retrogression: Evidence from contrasting long-term chronosequences.” Oikos 117 (2008): 93–103. Yoon, Carol Kaesuk. “As Mt. St. Helens recovers, old wisdom crumbles.” New York Times, (May 16, 2000). Available online. URL: http://www.nytimes. com/2000/05/16/science/as-mt-st-helens-recovers-oldwisdom-crumbles.html?pagewanted=all. Accessed May 16, 2011.

symbiogenesis  Symbiogenesis is the generation of biodiversity and of evolutionary novelty through symbiosis. Symbiosis is the physiological association of members of two or more distinct kinds of organism, and it results from coevolution. When populations of two species form a close symbiotic partnership, natural selection may favor genetic changes that enhance the partnership of the two species. If these genetic changes are associated with reproductive isolation, then the partners may be considered new species distinct from their immediate ancestors. Further, the partners may merge their activities so closely, as when photosynthetic bacteria bocame chloroplasts or when algae merge with fungi to become lichens, that they are often named as a single new species. As a result, symbiogenesis can result in the origin of new species by merger of some populations of previously independent species. The principal modern scientist who has promoted awareness of symbiogenesis is Lynn Margulis of the University of Massachusetts at Amherst. The principal image that has dominated Darwinian evolutionary theory is the “tree of life,” in which ancestral species branch out to form new species. One

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508 symbiogenesis  508 of the earliest images of the tree of life is the single illustration that is found in Charles Darwin’s landmark 1859 book Origin of Species. In this image, the branches grow farther and farther apart but never merge. When symbiogenesis occurs, however, the tree of life experiences grafts, sometimes between branches that are very far apart from one another on the tree. The earliest statements of the idea of symbiogenesis were made by two Russian botanists, Konstantin S. Mereschkovsky and Andrey S. Famitsyn, prior to the Russian Revolution. After Mereschkovsky died in 1918 and Famitsyn in 1921, another Russian botanist, Boris M. Kozo-Polyansky, kept the idea alive. It was never, however, a major theory in the Soviet Union, especially in the Stalinist era, when the theories of Lysenkoism dominated genetics and evolution, and remained practically unknown in the United States until recently, when their ideas were promoted by Margulis and science writer Dorion Sagan. Independently of the Russian scientists, an American anatomist, Ivan E. Wallin (at the University of Colorado Medical Center in Denver), formulated an idea of symbiogenesis, which he called symbionticism in a 1927 book. His ideas were ignored, and he finished his career without pursuing symbiosis any further. Lynn Margulis investigated the inheritance patterns of some genetic traits that appeared to be passed on not through the nucleus but through the cytoplasm of the cell. In sexual reproduction, most of the cytoplasm of the fertilized egg cell comes from the unfertilized egg, rather than from the sperm; the cytoplasmic factors showed a pattern of inheritance that was passed on solely through the maternal line. This indicated that there was DNA in the cytoplasm, not just in the nucleus. And she had an idea where that DNA was located. All independently living cells (and most viruses as well) have genetic information encoded in DNA. In contrast, organelles (specialized structures within the cell) generally do not have their own DNA; their production and operation are dictated by the DNA in the cell’s nucleus. Margulis wrote a paper in 1967 in which she proposed that chloroplasts and mitochondria had used their own DNA. The DNA was there because these organelles are the evolutionary descendants of bacteria that had merged with ancestral eukaryotic cells. The bacteria remained, without killing their host cells, and the host cell lineages evolved processes that accommodated and made use of the bacteria. The bacteria became symbionts. If chloroplasts and mitochondria were merely cell structures, one would not expect them to have their own DNA. The chloroplasts had evolved from photosynthetic bacteria (often called blue-green algae), while the mitochondria had evolved from aerobic bacteria that consumed organic materials.

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first entry These symbiotic events happened more than a billion years ago. Frequently in cells, segments of DNA can move from one location to another. Many of the genes of the mitochondria and chloroplasts were transposed from the symbiotic bacteria to the nuclei of the host cells. The simplified symbionts were now incapable of surviving on their own, and they became the chloroplasts and mitochondria that are today found only in eukaryotic cells. Though not accepted by many scientists at first, Margulis’s proposal of symbiogenesis quickly advanced in the scientific community. As better chemical and microscopic techniques became available, convincing evidence of the bacterial origin of chloroplasts and mitochondria emerged. Chloroplasts and mitochondria: ●●

●●

●●

have their own DNA, which resembles bacterial DNA more than it resembles the DNA of eukaryotic chromosomes. have ribosomes, which are structures that use genetic information in DNA to produce proteins. As a result, mitochondria and chloroplasts produce some of their own proteins. In the case of an important photosynthetic enzyme called rubisco, part of the enzyme (the large subunit, rbcL) is produced by the chloroplasts, while the small subunit is produced by the ribosomes out in the chloroplast, using information not found in the nucleus. reproduce themselves, rather than being constructed by the cell. Small, immature mitochondria and chloroplasts may abound in eukaryotic cells; some of the immature structures mature into functional mitochondria and chloroplasts, which cannot reproduce, while other immature structures reproduce themselves.

In addition, some marine invertebrates consume algae but keep the algal chloroplasts alive in some of their cells. This strongly suggests that chloroplasts and mitochondria may have arisen in a similar way, as symbiotic bacteria that lost most of their genetic independence—but not quite all of it, thus betraying their symbiogenetic origins. As techniques became available to actually determine the sequence of nucleotides within DNA and other nucleic acids, it became possible to make comparisons between the DNA of different species to determine their evolutionary relationships. Following the initial lead of Carl R. Woese of the University of Illinois, biologists constructed a tree of life showing the branching patterns of evolution. The tree was based solely upon living species from which DNA and RNA could be obtained. Mitochondrial genes turned out to be very close to aerobic bacteria

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symbiogenesis  509 on the tree of life, and not at all similar to the genes in the nuclei of the cells in which mitochondria live. Chloroplast genes turned out to more closely resemble cyanobacteria on the tree of life than the genes in the nuclei of the plant cells in which they now live. This is precisely what would be expected as confirmation of Margulis’s symbiogenetic theory of their origins. While nearly all biologists accept Margulis’s symbiogenetic explanation of the origin of chloroplasts and mitochondria, some of her subsequent proposals have not met with widespread acceptance. Perhaps the most famous example is her proposal that the motile structures of eukaryotic cells were originally symbiotic bacteria as well. Margulis uses the term undulipodia (“undulating feet” in Greek) to denote structures in eukaryotic cells that are usually called cilia and eukaryotic flagella. Cilia are hairlike structures on the outside of many eukaryotic cells, for example free-living protists and the cells that line animal respiratory passages, and that have the power of movement. Cilia assist in the movement of protists such as Paramecium and some small aquatic animals. Flagella are whiplike structures with which many eukaryotic cells can swim, for example protists like Euglena and sperm cells. Many bacteria also have flagella with which they propel themselves, but the smaller rotary structure of bacterial flagella is totally unlike the more complex structure of eukaryotic flagella, which is why Margulis does not use the same term for both of them. Margulis claims that the protein strands within undulipodia are the remnants of spirochete bacteria. How might this have occurred? Today, there are examples of spirochete bacteria that burrow partway into protist cells. The protruding parts of the bacteria flap in a coordinated rhythm, propelling the protist cell. These protists, when viewed under the microscope, look just like ciliated or flagellated cells; one must look closely and watch the process of their formation to realize that they are not cilia at all but bacteria! In other words, spirochetes are, today, doing the very thing that Margulis claimed they did back when undulipodia came into existence. Another structure that may have had a symbiogenetic origin is the hydrogenosome, a structure that metabolizes hydrogen and is found in some protist cells. In some cases, the genes that control hydrogenosome activity are all together in the host cell nucleus and resemble bacterial rather than eukaryotic genes, as if they were transposed to the nucleus from the ancestral hydrogenosome, which may have been a mitochondrion or a bacterium. Margulis reconstructs the history of eukaryotic cells in four stages, which she calls Serial Endosymbiotic Theory:

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1.  The nucleus had a bacterial origin. The most likely ancestor for the nucleus is an archaebacterium similar to modern Thermoplasma. Some archaebacteria have proteins that resemble the histones associated with the DNA in eukaryotic chromosomes. The ancestral cell was now a eukaryote, with a nucleus. 2.  Spirochetes associated with this cell and eventually became undulipodia. 3.  Aerobic bacteria moved into some of these cells and eventually became mitochondria. Some of the protists that had mitochondria became the ancestors of animals, fungi, and plants. 4.  Photosynthetic cyanobacteria were consumed, but not digested, by cells that already had mitochondria, and eventually became chloroplasts. Some of the protists that had chloroplasts became the ancestors of plants. One of the strongest proofs of symbiogenesis is the fact that the structures now called chloroplasts have originated more than once. Most chloroplasts, like those of all terrestrial plants, resemble bacteria and are surrounded by a simple membrane. But the chloroplasts of some protists, such as dinoflagellates, have multiple membranes. This is also true of the apicoplast of the Plasmodium falciparum protist that causes malaria, which is a degenerate, multiple-membraned chloroplast. The Plasmodium does not use its apicoplasts for photosynthesis. The multiple membranes of these chloroplasts and apicoplasts suggest that they evolved when photosynthetic eukaryotic cells invaded other eukaryotic cells, stayed there, and simplified. In other words, regular chloroplasts are degenerate cells inside a cell; dinoflagellate chloroplasts and plasmodial apicoplasts represent degenerate cells inside of degenerate cells inside of a cell! There is even microscopic evidence that these chloroplasts have nucleomorphs, which appear to be small, vestigial nuclei. A dramatic experimental demonstration of symbiogenesis (albeit unintended) occurred when biologist Kwang Jeon of the University of Tennessee at Knoxville noticed that his cultures of the protist Amoeba proteus looked sick. Under the microscope, he could see that each amoeba was infected with thousands of rod-shaped bacteria. The amoebae usually digested bacteria, but these bacteria could resist the digestive enzymes of the amoebae. Most of the amoebae died from the bacterial infection. However, a few amoebae could resist the bacteria and survive. Jeon cultured the survivors over and over. He was artificially selecting for the amoebae that could best resist the bacterial infection, as well as for the bacteria that had the mildest effects on the amoebae. After about a year and a half, the amoebae and bacteria had developed

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510 symbiosis  510 a ­mutually beneficial relationship. After several years, the coevolution of amoebae and bacteria had progressed so far that neither of the species could survive without molecules supplied by the other. They had become an essential part of each other’s environment. Might the amoebae now be considered a new species of protist? Might the bacteria now be considered a new species as well? Perhaps they could even be considered one new species of organism? There are many examples of symbiogenetic processes that involve bacteria and insects. The bacterium Buchnera aphidicola infects aphids. Like an organelle, the Buchnera bacterium can be transmitted from one generation to the next through eggs. Because Buchnera manufactures certain amino acids that aphids cannot get from the sap that they eat, it can be considered mutualistic. The bacterium Cinara cedri does a similar thing. The endosymbiotic bacterium Carsonella ruddii has a set of DNA only about a quarter as large as that found in plant mitochondria. About 10 percent of insect species have endosymbiotic bacteria with reduced genomes that produce nutrients upon which they depend. Did mitochondria begin their evolution in a similar way? Evolutionary biologists Noriko Okamoto and Isao Inouye have found evidence of a secondary symbiosis that appears to be in progress. There is a green-algal symbiont that lives in certain protist host cells. The symbiont still has a nucleus, mitochondria, and a large green plastid, but the flagella, cytoskeleton, and internal membranes are gone. When the symbiont divides, it produces two cells: one with the plastid and one without. The cell without the green plastid then develops a feeding apparatus and engulfs the cell with the green plastid. This may represent a direct observation of a “missing link” in the evolution of chloroplasts by symbiosis. The symbiogenetic event that produced chloroplasts and other similar structures was not a single, freak event; symbiogenesis cannot, therefore, be safely ignored in evolutionary theory as a weird aberration. Symbiogenesis has occurred, and continues to occur, a lot. In fact, according to Margulis, it occurs so often that Earth should be considered a “symbiotic planet.” The worldwide tendency of organisms to associate with one another may, according to Margulis, help to explain why Earth operates as a single system. Symbiogenesis can occur more than once even in a single cell. One of the best examples is a protist that lives in the intestines of termites in Australia. This protist appears to have several different types of undulipodia. Actually, they are four different kinds of spirochetes that form a symbiotic association with the protist. And the symbiosis does not end there. The protist itself is a symbiont inside of termite intestines, and it helps the termites to digest wood. Termites

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first entry could not survive if they did not have protists living in their guts that aid with the digestion of wood. Whenever coevolution produces symbiosis, new opportunities for evolution result. Small mutualists living inside of larger cells may lose some of their genes to the host cell. When this occurs, symbiogenesis may very quickly produce new biodiversity. See also coevolution; eukaryotes; Margulis, Lynn; natural selection; protists. Further Reading Akhmanova, A., et al., “A hydrogenosome with a genome.” Nature 396 (1998): 527–528. Boxma, B., et al. “An anaerobic mitochondrion that produces hydrogen.” Nature 434 (2005): 74–79. Chapman, Michael J., Michael F. Dolan, and Lynn Margulis. “Centrioles and kinetosomes: Form, function, and evolution.” Quarterly Review of Biology 75 (2000): 409–429. Douglas, Susan, et al. “The highly reduced genome of an enslaved algal nucleus.” Nature 410 (2001): 1,091–1,096. Dyall, Sabrina, Mark T. Brown, and Patricia J. Johnson. “Ancient invasions: From endosymbionts to organelles.” Science 304 (2004): 253–257. Falkowski, Paul G., et al. “The evolution of modern eukaryotic phytoplankton.” Science 305 (2004): 354–727. Jeon, K. W. “Integration of bacterial endosymbionts in amoebae.” International Review of Cytology, Suppl. 14 (1983): 29–47. Margulis, Lynn. Symbiotic Planet: A New Look at Evolution. New York: Basic Books, 1998. ———. “Serial endosymbiotic theory (SET) and composite individuality: Transition from bacterial to eukaryotic genomes.” Microbiology Today 31 (2004): 172–174. Margulis, Lynn, and R. Fester, eds. Symbiosis as a Source of Evolutionary Innovation. Cambridge, Mass.: MIT Press, 1991. Margulis, Lynn, and Dorion Sagan. “The beast with five genomes.” Natural History, June 2001, 38–41. ———. Acquiring Genomes: A Theory of the Origins of Species. New York: Basic Books, 2002. Nakabachi, Natsushi, et al. “The 100-kilobase genome of the bacterial endosymbiont Carsonella.” Science 314 (2006): 267. Okamoto, Noriko, and Isao Inouye. “A secondary symbiosis in progress?” Science 310 (2005): 287. Pérez-Brocal, Vicente, et al. “A small microbial genome: The end of a long symbiotic relationship?” Science 314 (2006): 312–313. Summarized by Andersson, Siv G. E. “The bacterial world gets smaller.” Science 314 (2006): 259–260.

symbiosis  See coevolution; commensalism; mutualism; parasitism.

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T temperate coniferous forests  the temper-

temperate coniferous forests intergrade into boreal and subalpine forests. Some trees, such as the Scots pine (Pinus sylvestris) and the norway spruce (Picea abies), grow in boreal forests as well as temperate ones. temperate coniferous forests also intergrade into temperate deciduous forests. Many species of pines are abundant in moist deciduous forests. examples include white pines (P. strobus) and hemlocks (Tsuga canadensis) in eastern north america and Japanese black pines (P. thunbergii) in asia. in dry regions, such as western north america, they can intergrade into cool desert sagebrush. in some moist coves of the Pacific slope of the Sierra nevada, giant sequoia trees (Sequoiadendron giganteum) dominate the temperate coniferous forests. On the average, giant sequoias are the largest trees in the world. Many of them live more than 2,000 years. Because of their thick bark, giant sequoias survive fi res that kill many other trees. these same fi res create the sunny conditions in which sequoia seedlings grow. See also conifers; temperate deciduous forests; temperate dry forests.

ate coniferous forests are found primarily in moderately dry mountainous regions. they have cold, snowy winters and warm summers. they receive less summer rain than the temperate deciduous forests, and this is one important reason that the temperate coniferous forests are found in drier regions of western north america while deciduous forests are found in the wetter regions of the east. they receive more rain than the temperate dry evergreen oak forests. in western north america and Mexico, three zones within the temperate coniferous forests may be distinguished (see the following table): ●





the driest coniferous forests are the piñonjuniper woodlands, which are found on the ranges in the Great Basin and on the slopes of the Rockies and the Sierra Madre. coniferous forests that receive a little more precipitation are mostly dominated by ponderosa pines in the Great Basin and the Rockies, arizona pines in the Sierra Madre, and Jeffrey pines in california. the temperate coniferous forests with the greatest amount of precipitation are dominated by trees such as Douglas fi rs, white fi rs, lodgepole pines, and sugar pines.

Further reading coultrap, D. e., et al. “Relationships between western juniper (Juniperus occidentalis) and understory vegetation.” Invasive Plant Science and Management 1 (2008): 3–11. Delucia, evan H., and William H. Schlesinger. “Resourceuse efficiency and drought tolerance in adjacent Great Basin and Sierran plants.” Ecology 72 (1991): 51– 58. Rehfeldt, Gerald e., et al. “Physiologic plasticity, evolution, and impacts of a changing climate on Pinus contorta.” Climatic Change 50 (2001): 355–376.

temperate coniferous forests are also found throughout europe and asia. Small patches of hardwood trees may occur in temperate coniferous forests. in the Black Hills of South Dakota and Wyoming, bur oaks (Quercus macrocarpa) may grow in moist microhabitats. Understory hardwood trees include chokecherry (Prunus virginiana). 511

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512 temperate deciduous forests  512

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Some Dominant Trees and Mammals of the Temperate Coniferous Forests Scientific Name

Common Name

Principal Location

Juniperus deppeana

Alligator juniper

Mexico

Juniperus flaccida

Weeping juniper

Mexico

Juniperus monticola

Mountain juniper

Mexico

Juniperus occidentalis

Western juniper

Great Basin, Rockies

Juniperus osteosperma

Utah juniper

Great Basin, Rockies

Pinus cembroides

Mexican piñon

Mexico

Pinus edulis

Piñon

Great Basin, Rockies

Pinus monophylla

Piñon

California, Nevada

Pinus arizonica

Arizona pine

Arizona, Mexico

Pinus jeffreyi

Jeffrey pine

California, Mexico

Pinus ponderosa

Ponderosa pine

Great Basin, Rockies

Abies concolor

White fir

Western ranges, Rockies

Calocedrus decurrens

Incense cedar

Western ranges

Pinus contorta

Lodgepole pine

Canada, Western ranges, Mexico

Pinus lambertiana

Sugar pine

Western ranges, Rockies, Mexico

Pseudotsuga lindleyana

Mexican Douglas-fir

Mexico

Pseudotsuga menziesii

Douglas-fir

Western ranges, Rockies

Trees of Piñon-Juniper Woodlands

Trees of Ponderosa Woodlands

Trees of Moist Coniferous Woodlands

Trees of Eurasian Temperate Coniferous Forests Abies alba

European silver fir

Central Europe

Cedrus libani

Cedar of Lebanon

Mediterranean mountains

Picea abies

Norway spruce

Europe

Pinus heldreichii

Bosnian pine

Southeastern Europe

Pinus nigra

European black pine

Southern Europe

Pinus roxburghii

Chir pine

Lower Himalayas

Pinus sylvestris

Scots pine

Eurasia

Mammals of Temperate Coniferous Forests Odocoileus virginianus

White-tailed deer

Western ranges, Rockies

Oreamnos americanus

Mountain goat

Rockies

Ovis canadensis

Bighorn sheep

Western ranges, Rockies

Ursus americanus

Black bear

Western ranges, Rockies, Mexico

Riegel, Gregg M., et al. “Competition for resources between understory vegetation and overstory Pinus ponderosa in northeastern Oregon.” Ecological Applications 2 (1992): 71–85. Sherman, Robert J., and R. Keith Warren. “Factors in Pinus ponderosa and Calocedrus decurrens mortality in Yosemite Valley, USA.” Plant Ecology 77 (1988): 79–85. Stephens, S. L., and D. L. Fry. “Spatial distribution of regeneration patches in old-growth Pinus jeffreyi–mixed conifer forests in northwestern Mexico.” Journal of Vegetation Science 16 (2005): 693–702.

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Stone, Joseph E., et al. “Effects of restoration thinning on presettlement Pinus ponderosa in northern Arizona.” Restoration Ecology 7 (2002): 172–182.

temperate deciduous forests  Temperate deciduous forests grow in relatively moist regions of the Earth with freezing winters and warm summers that are of roughly equal duration. They have a moderate climate and a growing season of 140 to 200 days during four to six frost-free months. Precipita-

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temperate deciduous forests  513

Deciduous forests are renowned for their autumn colors. Not all the colorful deciduous trees are broadleafed trees: The bright red trees growing in the water at Beaver’s Bend State Park in Oklahoma are bald cypresses (Taxodium distichum).  (Stanley A. Rice)

tion is usually distributed evenly throughout the year, ranging from 39 to 59 inches (75 to 150 cm), falling as snow in winter and rain in summer. Soils are typically fertile and enriched with decaying litter (humus). Temperate forests occur in eastern North America, northeastern Asia, and western and central Europe. The dominant tree species shed their leaves every autumn (see figure). If they did not do so, a heavy weight of snow would accumulate on the broad leaves and damage the branches. They produce new leaves every spring. Trees of boreal forests do not shed their leaves each autumn, primarily because the boreal summers are so short that there is insufficient time for a new crop of leaves to grow every year. Trees of tropical forests do not seasonally shed their leaves, primarily because tropical regions have year-round summer. Deciduous forests, therefore, live in climatic zones with winters that are intermediate in length between those of boreal and tropical zones. The broad leaves of the deciduous trees have higher rates of photosynthesis than do needle-shaped leaves. Trees of boreal forests have needle-shaped leaves, despite their lower photosynthesis, because needle-shaped leaves are better than broad leaves at surviving the winter. Needle leaves result in less accumulation of snow than broad leaves. The leaves of deciduous trees are adapted to rapid photosynthesis in the summer, and the leaves of boreal trees are adapted to surviving the winter.

Biodiversity in Deciduous Forests Deciduous forests do not have as much biodiversity as the tropical rain forests, for reasons such as the following: Winter and wind. As in the rain forests, a great deal of coevolution occurs between plants and their

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herbivores and their pollinators. Selection for chemical defenses against herbivores, which can lead to speciation, is less intense in the deciduous forest because many insect populations are reduced by winter death. Selection for pollinator specialization is not as strong because many temperate plants, especially dominant forest trees, depend on wind pollination. Broad ranges of tolerance. Because each species has to tolerate wide fluctuations of temperature each year, and often moisture as well, each species is able to grow over a more extensive geographical range than is often the case with rain forest species. Specialization on microhabitats. Deciduous forest species are able to specialize within their habitat. For example, when the snow melts in the spring, sunlight penetrates the bare branches and warms the ground, allowing shrubs to burst their buds and spring ephemeral wildflowers to grow. These wildflowers, such as the spring beauty (Claytonia virginica), are perennials that resprout each year from underground food storage organs. Meanwhile, the wind remains chilly and the buds of the trees remain dormant. For about a month, the spring ephemerals receive abundant sunlight and relative warmth. Once the tree buds begin to open, casting shade, the ephemerals begin to senesce, until the next year. Then the shade-adapted summer wildflowers grow and dominate the forest floor. There are also lianas, such as grapes, in deciduous forests, as in rain forests. Drier conditions, however, make epiphytes (plants whose roots obtain moisture and minerals from accumulated leaf litter up in the branches of trees) very rare, in contrast to their tropical exuberance. Deciduous forests contain a few evergreen species. Some, such as hemlocks (Tsuga canadensis), are trees. Many, like the hollies (Ilex opaca and I. americana), are shrubs. They may be protected from winter conditions by the larger deciduous trees around them, and they make use of the sunlight of the early spring before the deciduous trees have opened their leaves. The deciduous forests of Asia, having been less disrupted by the ice ages than the forests of North America and Europe, have many coniferous tree species, including the dawn redwood (Metasequoia glyptostroboides) and the Japanese cypress (Cryptomeria japonica). Within the deciduous forest zone, there are differences in climatic conditions, and, therefore, species composition; the deciduous forest species have evolved separately in North America, Europe, and Asia for millions of years, as indicated in the table on pages 514–515. The major North American deciduous forests are the following: ●●

The beech-maple forests of North America are dominated by American beeches (Fagus

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514 temperate deciduous forests  514

first entry

Examples of Deciduous Forest Canopy Tree and Mammal Species Trees Tree Species

Common Name

Family

Acer saccharum

Sugar maple

Aceraceae (maple)

Fagus grandifolia

Beech

Fagaceae (oak/beech)

Liriodendron tulipifera

Tuliptree

Magnoliaceae (magnolia)

Tilia americana

Basswood

Tiliaceae (basswood)

Ulmus americana

American elm

Ulmaceae (elm)

Carya illinoensis

Pecan

Juglandaceae (walnut)

Carya tomentosa

Mockernut hickory

Juglandaceae (walnut)

Juglans nigra

Black walnut

Juglandaceae (walnut)

Quercus alba

White oak

Fagaceae (oak/beech)

Quercus macrocarpa

Bur oak

Fagaceae (oak/beech)

Quercus marilandica

Blackjack oak

Fagaceae (oak/beech)

Quercus stellata

Post oak

Fagaceae (oak/beech)

Beech-maple forests, North America

Oak-hickory forests, North America

Cross Timbers forest, North America

Appalachian forests, North America (in addition to maples, oaks, hickories) Cladrastis kentuckea

Yellowwood

Fabaceae (legume)

Gymnocladus dioicus

Kentucky coffeetree

Fabaceae (legume)

Halesia tetraptera

Carolina silverbell

Styracaceae (styrax)

Oxydendrum arboretum

Sourwood

Ericaceae (heath)

Bursera simaruba

Gumbo-limbo

Burseraceae (incense tree)

Liquidambar styraciflua

Sweetgum

Altingiaceae (sweetgum)

Magnolia grandiflora

Magnolia

Magnoliaceae (magnolia)

Nyssa sylvatica

Tupelo

Nyssaceae (tupelo)

Quercus falcata

Southern red oak

Fagaceae (oak/beech)

Quercus shumardi

Shumard oak

Fagaceae (oak/beech)

Quercus virginiana

Live oak

Fagaceae (oak/beech)

Acer platanoides

Norway maple

Aceraceae (maple)

Fagus sylvatica

European beech

Fagaceae (oak/beech)

Juglans regia

English walnut

Juglandaceae (walnut)

Quercus petraea

Sessile oak

Fagaceae (oak/beech)

Quercus robur

English oak

Fagaceae (oak/beech)

Tilia cordata

Linden

Tiliaceae (basswood)

Ulmus laevis

European white elm

Ulmaceae (elm)

Acer davidii

Père David’s maple

Aceraceae (maple)

Carya cathayensis

Chinese hickory

Juglandaceae (walnut)

Castanea seguinii

Chinese chinquapin

Fagaceae (oak/beech)

Fagus engleriana

Chinese beech

Fagaceae (oak/beech)

Juglans cathayensis

Chinese walnut

Juglandaceae (walnut)

Southern forests, North America

Europe

China

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temperate deciduous forests  515 Liriodendron chinensis

Chinese tulip tree

Magnoliaceae (magnolia)

Nyssa sinensis

Chinese tupelo

Nyssaceae (tupelo)

Quercus variabilis

Chinese cork oak

Fagaceae (oak/beech)

Styrax japonicus

Japanese snowbell

Styracaceae (styrax)

Tilia chinensis

Chinese linden

Tiliaceae (basswood)

Mammals Mammal Species

Common Name

Order

Erethizon dorsatum

Porcupine

Rodent

Felis concolor

Mountain lion

Carnivore

Odocoileus virginianus

White-tail deer

Even-toed ungulate

Procyon lotor

Raccoon

Carnivore

Ursus arctos

Brown bear

Carnivore

Capreolus capreolus

Roe deer

Even-toed ungulate

Felis silvestris

Wild cat

Carnivore

Hystrix cristata

Porcupine

Rodent

Lynx lynx

Eurasian lynx

Carnivore

Ursus arctos

Brown bear

Carnivore

Ailuropoda melanoleuca

Panda

Carnivore

Atherurus macrourus

Brush-tailed porcupine

Rodent

Pardofelis temminckii

Asian golden cat

Carnivore

North America

Europe

China

grandifolia) and sugar maples (Acer saccharum). They grow in moist, lowland areas, primarily from Indiana to New England (see figure).

●●

●●

●●

Sugar maples (Acer saccharum) in the eastern deciduous forest of North America have thin leaves that efficiently absorb light in the shade. Therefore, sugar maple seedlings grow up beneath and replace adult sugar maples.  (Stanley A. Rice; Shades State Park, Indiana)

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The oak-hickory forests of North America live in mountainous and drier regions, from Oklahoma to the Atlantic coast. Many species of oaks (genus Quercus) and hickory (such as the pecan, Carya illinoensis) make up these forests. The southern forests of North America have mild winters. Because snow is rare, they even contain some evergreen trees, such as Magnolia grandiflora and the live oak (Quercus virginiana). These forests intergrade into the rain forests of the Caribbean, with the gumbo-limbo tree (Bursera simaruba) spanning the transition. The driest deciduous forest region in North America is the Cross Timbers forest of Oklahoma and Texas. Post oaks (Quercus stellata) and blackjack oaks (Q. marilandica) dominate these forests and are much shorter than the trees of other deciduous forests. Cross Timbers forest soils are very poor and rocky. Post and blackjack oaks are uncommon and specialize on dry outcrops in the deciduous forests of the moist regions to the north and east.

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516 temperate deciduous forests  516 European forests have evolved separately from North American forests for at least 50 million years. European forests have maples, beeches, and oaks, just as do American deciduous forests, but not the same species. The same is true of the deciduous forests of China and Japan, whose species also differ from one another. Fagus crenata, the Japanese beech, is not found in China. The deciduous forests of North America, Europe, and Asia also contain similar types of mammals, although usually different species of each (see table on pages 514–515). The brown bear Ursus arctos lives in both Europe and North America. Before North America separated from Europe, and before the ice ages began, the deciduous forests formed a more or less continuous band across the northern continents. Ancestral populations of forest trees and other plants evolved separately in these places, but the large animals continued to migrate across the Bering land bridge until the ice ages began, and in some cases until the end of the most recent ice age. The North American deciduous forests with the greatest diversity of species are found in the southern Appalachians, where abundant rainfall and mild winters allow the coexistence of hundreds of tree species from both the beech-maple and oak-hickory forests, and many species, such as Kentucky coffee­ tree (Gymnocladus dioicus), which are not abundant anywhere else. Many species of deciduous trees grow rapidly and specialize on growing in disturbed areas before they are eventually replaced by the dominant tree species. Examples include black cherry (Prunus serotina), cottonwood (Populus deltoides), and sycamore (Platanus occidentalis). Chestnut trees (Castanea americana) once dominated the oak-hickory forests, until a disease, the chestnut blight, was introduced into New York about 1900. This fungal disease killed all adult chestnut trees, except for very rare isolated stands, reaching Georgia by the 1950s. Today, chestnuts can be found only as resprouts from surviving rootstocks. Today, only scattered remnants of original oldgrowth temperate forests remain. Because of their proximity to major centers of civilization, most of these forests were cut early in civilization: the Mediterranean forests before 2000 b.c.e., the central European forests by about 1000 c.e., and the North American deciduous forests by about 1900. Many of these forests have grown back, though with smaller trees and lower diversity of tree species. Hemlocks and maples have grown back where there were once farms in New England, but most modern people will never see examples of the huge trees that the first European settlers encountered on the North

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first entry American continent. Since 1970, however, deciduous forest area in the United States has declined by about 4 percent, mainly due to the expansion of suburbs and to mountaintop-removal coal mining. The animal that had perhaps the most significant impact on these forests immediately before white American settlement was the passenger pigeon. When white Americans were traveling and homesteading across the eastern forest, they saw flocks of billions of passenger pigeons. They assumed that this is the way it had always been. Recent scholarship has suggested, however, that hunting by Native Americans had kept the pigeon populations under control for thousands of years, and the pigeon population exploded only after diseases such as smallpox reduced Native populations by as much as 90 percent. A similar explanation has been offered for why there were so many millions of bison in the prairies just prior to white American expansion. According to the earliest explorers who visited Native tribes prior to their decimation by smallpox, Native Americans extensively transformed the landscape by agriculture and fire. Though they farmed and burned much of what the poet Henry Wadsworth Longfellow called the “primeval forest,” they had only stone tools and did not cut down the largest trees. Perhaps the most extensive deciduous forest in the world that has largely escaped recent destruction lies on the border of Belarus (where it is called Belovezhskaya Pushcha) and Poland (where it is called Białowiez˙a Puszcza). As in Appalachian and Asian forests, there are some abundant conifers, such as Norway spruce and Scotch pine. The deciduous tree species include alders, oaks, birches, ashes, basswoods, maples, aspen, elms, and hornbeams. Many of the trees are quite large. This forest is the home of some of the last wisent (Bison bonasus) herds, which are separated by the fence that divides Belarus and Poland. Despite the centuries of protection that this forest has received, it remains extensively disturbed by humans; the average age of a forest stand in the protected zone is only 130 years. See also temperate coniferous forests; temperate dry forests. Further Reading Abrams, Marc D. “The red maple paradox.” BioScience 48 (1998): 355–364. Association for Ecotourism Development (Poland). “In the heart of Bialowieza National Park.” Available online. URL: http://www.puszczabialowieska.org/eng/flora. htm. Accessed July 25, 2010. Bonnicksen, Thomas M. America’s Ancient Forests: From the Ice Age to the Age of Discovery. New York: John Wiley, 2000.

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temperate dry forests  517 Clebsch, Edward E. C., and Richard T. Busing. “Secondary succession, gap dynamics, and community structure in a southern Appalachian cove forest.” Ecology 70 (1989): 728–735. Delcourt, Hazel R. Forests in Peril: Tracking Deciduous Trees from Ice-Age Refuges into the Greenhouse World. Granville, Ohio: McDonald and Woodward, 2002. Duffy, David Cameron, and Albert J. Meier. “Do Appalachian herbaceous understories ever recover from clearcutting?” Conservation Biology 6 (2003): 196–201. Francaviglia, Richard V. The Cast Iron Forest: A Natural and Cultural History of the North American Cross Timbers. Austin: University of Texas Press, 2000. Macleish, William H. The Day before America: Changing the Nature of a Continent. New York: Houghton Mifflin, 1994. Mann, Charles C. 1491: New Revelations of the Americas before Columbus. New York: Knopf, 2005. McCormick, J. Frank, and Robert B. Platt. “Recovery of an Appalachian forest following the chestnut blight or Catherine Keever—you were right!” American Midland Naturalist 104 (1980): 264–273. Parker, G. R., et al. “Tree dynamics in an old-growth, deciduous forest.” Forest Ecology and Management 11 (1985): 31–57. Rice, Stanley A. “Plants create habitats.” Chap. 8 in Green Planet: How Plants Keep the Earth Alive. Piscataway, N.J.: Rutgers University Press, 2009. Whigham, Dennis F. “Ecology of woodland herbs in temperate deciduous forests.” Annual Review of Ecology, Evolution, and Systematics 35 (2004): 583–622. Yahner, Richard H. Eastern Deciduous Forests: Ecology and Wildlife Conservation, 2nd ed. Minneapolis: University of Minnesota Press, 2000.

temperate dry forests  Temperate dry for-

ests consist of evergreen broadleaf trees. The summers are hot and dry, and the winters are cool and wet. These conditions are usually called “Mediterranean” because they are widespread in southern Europe, the Middle East, and North Africa. These conditions are also found in California, Chile, South Africa, and Australia. The trees are short and seldom form a continuous canopy. Temperate dry forests are also found in the dry mountains of northern Mexico, where, because of summer rainfall, the climate is not Mediterranean. African dry forests are subtropical and are considered tropical seasonal forests. The dry evergreen forests of the Mediterranean Basin, California, and Mexico are dominated by oaks (see table). The dry evergreen forests of Australia are dominated by eucalypts. Unlike the other dry forests here mentioned, eucalypt forests regenerate abundantly after fires. Moist forests

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Some Temperate Dry Forest Trees Scientific Name

Common Name

Mediterranean Quercus calliprinos

Palestine oak

Quercus coccifera

Kermes oak

Quercus ilex

Holm oak

Quercus suber

Cork oak

California Quercus agrifolia

Coast live oak

Quercus chrysolepis

Canyon live oak

Quercus dumosa

Scrub oak

Quercus englemannii

Englemann oak

Quercus wislizeni

Interior live oak

Mexico Quercus arizonica

Arizona white oak

Quercus chihuahuaensis

Chihuahua oak

Quercus emoryi

Emory oak

Quercus rugosa

Netleaf oak

Australia Corymbia (Eucalyptus) calophylla

Marri

Eucalyptus globulus

Tasmanian blue gum

Eucalyptus marginata

Jarrah

Eucalyptus radiata

Narrow-leaved peppermint

in the Mediterranean Basin and California contain oak species as well, some of them deciduous. Moist forests in Australia are also dominated by evergreen eucalypts, but they grow taller. Pines may grow among or rise above the small evergreen oaks, such as Pinus halepensis and P. pinea in the Mediterranean, and P. coulteri and P. sabiniana in California. Temperate dry forests intergrade with other ecological communities, such as the following: ●● ●●

Dry forests have a grass layer and may intergrade into grasslands. Chaparral, matorral, and other fire-cycle shrublands are often adjacent to dry forests. In such cases, fires maintain the shrublands at the expense of the forests. Some oak trees

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518 temperate rain forests  518

●●

●●

●●

●●

are found both in dry forests and shrublands. Examples include Quercus wislizeni and Q. dumosa in California and Q. coccifera in the Middle East. In Mexico, temperate dry forests may intergrade with temperate coniferous forests. Mexican piñon (Pinus cembroides) dominate the drier coniferous forests, while the ocote blanco (P. leiophylla) and Mexican subspecies of sugar pine (P. lambertiana) and ponderosa pine (P. ponderosa) dominate the coniferous forests that receive more rainfall and snow. In California, temperate dry forests intergrade with a mixture of deciduous broadleaf trees (such as the California black oak, Quercus kelloggii; the blue oak, Q. douglasii; the valley oak, Q. lobata; and the tanbark oak, Lithocarpus densiflorus) and conifers (such as ponderosa pine, Pinus ponderosa; Douglas fir, Pseudotsuga menziesii; Santa Lucia fir, Abies bracteata; and incense cedar, Calocedrus decurrens). In the Mediterranean, temperate dry forests may intergrade with temperate deciduous forests, often dominated by deciduous oaks, such as Quercus robur. Dry eucalypt forests in Australia intergrade into temperate rain forests dominated by other eucalypts and by kauri trees (Agathis australis).

Temperate dry forests often grow on dry, nutrient-poor soil. The dry conditions and the thick evergreen leaves discourage rapid decomposition and humus formation. The similarity in climatic conditions between Australia, California, and New Zealand has allowed an exchange of invasive species. Railroad workers planted Eucalyptus globulus from Australia in California in the 19th century, after which it took over large areas that were formerly shrubland and grassland. The native range of the Monterey pine (Pinus radiata) is just three small groves in California, but after being planted in New Zealand, it displaced much of the native forest. Unlike tropical seasonal forests and savannas in Africa, the dry evergreen forests are not well known for wildlife. White-tailed deer (Odocoileus virginianus) and black bears (Ursus americanus) live in the dry forests in California and Mexico. Many marsupials, most famously the koalas (Phasolarctos cinereus), live in dry eucalyptus forests of Australia. Thousands of years of human contact have eliminated many game animals from Mediterranean forests. However, cork oak forests in North Africa

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first entry are the home of the endangered Barbary macaque (Macaca sylvanus). See also invasive species; shrublands; temperate coniferous forests; temperate deciduous forests.

temperate rain forests  Temperate rain for-

ests are cool coastal forests that receive moisture, much of it in the form of fog, all year. Because the winters are mild, the dominant trees are evergreen conifers or broadleaf trees. Because the air is usually humid, water can rise to the tops of very tall trees. The three tallest tree species in the world—the coast redwood, the Douglas fir, and the Sitka spruce— all grow in the temperate rain forest of the Pacific Northwest of North America. The tallest tree in the world is a coast redwood (Sequoia sempervirens) 378 feet (116 m) tall. The range of these redwoods extends inland only as far as the coastal fog. The almost continuous moisture also allows many epiphytes, such as ferns and mosses, to grow in the branches of the large conifers and broadleaf trees. Some temperate rain forests in Australia and Taiwan are in coastal mountains. Because of thick undergrowth and wet soil, seedlings often germinate more readily on fallen logs (“nurse logs”) than on the ground. Long after the log has rotted away, the roots of large trees still form a tunnel formerly occupied by the log (see photograph). The relatively mild, wet conditions of temperate rain forests resemble climate conditions that were widespread earlier in the Cenozoic era. They have therefore served as refugia for tree species, especially conifers other than pines, which used to be much more widespread in temperate regions. The dominant broadleaf trees of temperate rain forests tend to be relatives of oaks (tanbark oaks, southern beeches)

These trees in the Olympic rain forest in Washington began their growth on a log that decomposed long ago.  (Stanley A. Rice)

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temperate rain forests  519 or in the plant family Cunoniaceae (Ceratopealum and Eucryphya) (see table). Temperate rain forests intergrade into other ecological communities such as the following: ●●

Tropical forests. Tree species such as the camphor tree (Cinnamomum camphora) are found not only in wet coastal areas of Asia but also just north of the Southeast Asian rain forest. In Australia, the southeastern temperate rain forests of New South Wales,

●●

●●

Victoria, and Tasmania come in contact with the northeastern tropical rain forests of Queensland. North and South American temperate rain forests are far from tropical rain forests. Temperate coniferous forests. Temperate rain forests along the Pacific coasts of North America and Japan intergrade into inland temperate coniferous forests. In the Pacific Northwest, temperate rain forests intergrade into subalpine forests.

Some Major Temperate Rain Forest Trees Scientific Name

Common Name

Primary Location

Acer macrophyllum

Bigleaf maple

Coastal Alaska to California

Chamaecyparis lawsoniana*

Port Orford cedar

Oregon, California

Lithocarpus densiflorus

Tanbark oak

Oregon, California

Picea sitchensis*

Sitka spruce

Coastal Alaska to California

Pseudotsuga menziesii*

Douglas fir

Coastal Alaska to California

Sequoia sempervirens*

Coast redwood

Coastal Oregon, California

Thuja plicata*

Western red cedar

British Columbia to California

Tsuga heterophylla*

Western hemlock

Coastal Alaska to California

Aextoxicon punctatum

Olivillo

South coastal Chile

Eucryphya cordifolia

Ulmo

South coastal Chile

Fitzroya cupressoides*

Alerce

South coastal Chile

Nothofagus obliqua

Roble beech

South coastal Chile

Chamaecyparis formosensis*

Formosan cypress

Taiwan

Cryptomeria japonica*

Japanese cedar

Southeast coastal Japan

Lithocarpus edulis

Japanese stone oak

Southeast coastal Japan

Pseudotsuga chinensis*

Chinese Douglas fir

Taiwan, coastal China

Agathis australis*

Kauri

New Zealand

Atherospermum moschatum

Southern sassafras

Australia, Tasmania

Ceratopetalum apetalum

Satinwood

Southeastern Australia

Eucalyptus regnans

Mountain ash

Australia, Tasmania

Eucryphya moorei

Pinkwood

Southeastern Australia

Nothofagus moorei

Antarctic beech

Southeastern Australia

Pacific Northwest of North America

South America

Asia

Australia

*Conifers.

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520 Thoreau, Henry David 520 There are cloud forests in some mountainous areas in the tropical latitudes. They are treated in a separate entry in this encyclopedia. Temperate rain forests are not noted for large animals. Besides bears and foxes, the main keystone predator in the Pacific Northwest rain forest is the spotted owl (Strix occidentalis). Temperate rain forests, like tropical rain forests, have many animals that require continuous moisture, such as amphibians and mollusks. The banana slug (genus Ariolimax) is a famous inhabitant of the Pacific Northwest rain forest. The temperate rain forest of the Pacific Northwest has been heavily logged, since the trees are so large and each log is worth a lot of money. Only about one-tenth of the old-growth Northwest forest remains. Timber corporations have frequently insisted on logging the old-growth forests, even though they have for decades been raising (and boasting about) sustainable tree plantations. Protesters and loggers have sometimes had violent confrontations. Environmentalist Julia Butterfly Hill spent 738 days in one of the largest trees to prevent loggers from cutting it down. The loggers spared the tree but a vandal attacked it later. The spotted owl, instead of the entire ecological community, became the focus of much of the controversy. See also boreal and subalpine forests; cloud forests; temperate coniferous forests; temperate deciduous forests. Further Reading Antos, Joseph A., and Donald B. Zobel. “Habitat relationships of Chamaecyparis nootkatensis in southern Washington, Oregon, and California.” Canadian Journal of Botany 64 (1986): 1,898–1,909. Bourne, Joel. “The super trees.” National Geographic, August 2009. Burgess, S. S. O., and T. E. Dawson. “The contribution of fog to the water relations of Sequoia sempervirens (D. Don): Foliar uptake and prevention of dehydration.” Plant, Cell, and Environment 27 (2004): 1,023–1,034. Chen, Jiquan, et al. “Vegetation responses to edge environments in old-growth Douglas-fir forests.” Ecological Applications 2 (1992): 387–396. Christy, E. Jennifer. “Effect of root competition and shading on growth of suppressed western hemlock (Tsuga heterophylla).” Plant Ecology 65 (1986): 21–28. Collins, Brian D., and David R. Montgomery. “Forest development, wood jams, and restoration of floodplain rivers in the Puget Lowland, Washington.” Restoration Ecology 10 (2002): 237–247. Dietrich, William. The Final Forest: The Battle for the Last Great Trees of the Pacific Northwest. New York: Penguin, 1993.

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first entry Fonda, R. W. “Forest succession in relation to river terrace development in Olympic National Park, Washington.” Ecology 55 (1974): 927–942. Halpern, Charles B., and Thomas A. Spies. “Plant species diversity in natural and managed forests of the Pacific Northwest.” Ecological Applications 5 (1995): 913–934. Hill, Julia Butterfly. The Legacy of Luna: The Story of a Tree, a Woman, and the Struggle to Save the Redwoods. New York: Harper, 2001. Lyons, Betsy, Nalini M. Nadkarni, and Malcolm P. North. “Spatial distribution and succession of epiphytes on Tsuga heterophylla (western hemlock) in an oldgrowth Douglas-fir forest.” Canadian Journal of Botany 78 (2000): 957–968. Preston, Richard. The Wild Trees: A Story of Passion and Daring. New York: Random House, 2008. Rodríguez-Cabal, Mariano A., et al. “Habitat fragmentation disrupts a plant-disperser mutualism in the temperate forest of South America.” Biological Conservation 139 (2007): 195–202. Traveset, Anna, and Mary F. Willson. “Effect of birds and bears on seed germination of fleshy-fruited plants in temperate rain forests of southeast Alaska.” Oikos 80 (1997): 89–95. Willson, Mary F., et al. “Avian communities of fragmented south-temperate rain forests in Chile.” Conservation Biology 8 (2002): 508–520.

Thoreau, Henry David  (1817–1862)  American  Naturalist, writer  Henry David Thoreau is widely revered as a “prophet of environmentalism” because the ideas he wrote and put into action appear to have been at least a century ahead of their time. He is less often mentioned as one of the leading scientists of early 19th-century America. He was an amateur scientist, but he laid the groundwork for the ecological study of seed dispersal and ecological succession. He collected data that constitute one of the earliest studies of the adjustment of organisms to changing seasons. His data sets have been used by modern scientists to document climate change that has occurred since his time. David Henry Thoreau (who never changed his legal name) was born on July 12, 1817, in Concord, Massachusetts, where he spent his entire life. He attended Harvard University from 1833 to 1837. He studied classics, philosophy, and science, earning but not bothering to accept a degree that Harvard awarded to students for persistence rather than merit. He became a schoolteacher at the Concord Academy, run by his brother John, but was dismissed from the faculty for refusing to administer corporal punishment. Several Massachusetts writers were transcendentalists, who believed that the world

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Thoreau, Henry David 521 of nature reflected an inner spiritual reality that also manifests itself in the human mind. One of them, Ralph Waldo Emerson, became his lifelong friend. For most of the period from 1841 to 1844, Thoreau lived with Emerson’s family and was the tutor of Emerson’s children. Thoreau’s father owned a pencil-making factory, where the son worked on and off for the rest of his life, in addition to odd jobs as surveyor and carpenter. Thoreau invented an improved method of preparing graphite for pencils and might have been headed for wealth in the pencil business. He rejected this path when, in 1845, he decided to live in the woods. Thoreau went out into a woodlot owned by Emerson (one of the few forest tracts near Concord that had not been cut down) and built a cabin near Walden Pond. The woodlot was not wilderness but was a second-growth forest and was less than two miles (a little more than 2 km) from Concord. He started his work on July 4 of that year, intending it as a statement of independence from the pursuit of wealth (which, he said, led most people into “lives of quiet desperation”), just as July 4 marked American independence and just as Concord was the site of the first battle of the Revolutionary War. But he also intended his cabin as an experiment. He kept a journal the rest of his life, some of which he published in the book Walden; or, Life in the Woods, which has become the environmental classic of the 19th century. In the journal, and book, Thoreau wrote detailed records of how much it cost him to build the cabin, and how he raised or caught much of his own food, going to town only for a few staple food items. He even built the cabin from wood and nails left over from a laborer family’s shanty. He spent only a couple of years in the cabin. He did not intend it as a permanent change in lifestyle but to demonstrate that it could be done. Thoreau was also famous for his essay “Resistance to Civil Government,” later known as “On Civil Disobedience,” which was based on an experience he had in 1846. For six years, he had refused to pay poll taxes because of his opposition to slavery and to the Mexican-American War. Massachusetts had no slaves but profited from goods produced by slaves, and the federal Fugitive Slave Act required all citizens to aid in the capture of slaves who had escaped from the South. He also considered the war to be nothing more than aggression. The Concord tax collector liked Thoreau but was obligated to arrest him. Thoreau was ready to spend a long period of time in jail as a protest, but his aunt paid his taxes, and he was released after one night. Thoreau’s civil disobedience inspired generations of social reformers, such as Russian writer Leo Tolstoy, Indian leader Mohandas Gandhi, and American

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reformer Martin Luther King, Jr. But his insistence that frugal living (what today would be called “having a small ecological footprint”) is not only possible but enjoyable contributed to his modern reputation as the prophet of environmentalism. Since the most ancient times, prophets have predicted disastrous outcomes to the way most people in their society lived, called for repentance from that way, and themselves lived in a way that was a constant reminder of the way of repentance. This is exactly what Henry David Thoreau did. Like all prophets, Thoreau was an inconvenient man. Though by no means a hermit (he went to town every couple of days even during his cabin phase), he was always separated from the normal crowd: When in town, he observed people as might an anthropologist from another planet. His presence was a prophetic denouncement of materialistic society. Thoreau was particularly vivid (and virtually alone) in his criticism of people who did not take care of their land. Thoreau wrote that Flint’s Pond (also near Concord) was named after an “unclean and stupid” farmer who laid its shores bare, loved a shiny dollar more than a shiny pond, reflecting “his own brazen face; who regarded even the wild ducks . . . as trespassers. . . . Who never saw it, who never bathed in it, who never loved it, who never protected it, who never spoke a good word for it, nor thanked God that He had made it. . . . Who exhausted the land around it.  .  .  . He would carry his God to market; . . . whose fields bear no crops, whose meadows no flowers, whose trees no fruits, but dollars.” Thoreau defended biodiversity against an agricultural mindset that, then as now, reduced a farm or a woodlot to its economic value and evaluated every plot of land on Earth, however different each was from the other, according to just one scale of value. Thoreau was also a scientist, though without formal training. His observations of nature suggested hypotheses to him, which he (however imperfectly) investigated. He was passionate about making observations (for example, the colors of Walden Pond ice and the stages by which it thawed) and measurement (the depths of Walden Pond). Scholars puzzle that his last writings were all mere observations of seed dispersal and spring budburst dates of plants. But his observations were the basis upon which important aspects of ecological science were later based, such as the following: ●●

Seed dispersal. In his long essays “The Dispersion of Seeds” and “The Succession of Forest Trees,” Thoreau presented many detailed observations to prove that trees grew only where their seeds had been planted by wind, water, or animals. As unbelievable

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522 Thoreau, Henry David 522

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as it may sound today, some intellectuals (none of them scientists) believed that trees just sprang up from the ground. Thoreau demonstrated that wild cherry trees grew where birds had carried their seeds, and that cherry seeds would not grow unless they had passed through a bird’s digestive system. He tested a hypothesis that mice dispersed hazelnut seeds by microscopically comparing tooth marks on a hazel nut with the teeth of a mouse skull. Forest succession. He also systematically surveyed tree stumps, counting the rings to reconstruct forest history by determining when each tree had begun to grow. He applied his observations to an understanding of the successional processes by which forests changed over time: Oaks grew up underneath pines, not underneath oaks, not only because oak forests cast too much shade upon the seedlings and oak leaf litter contained toxins, but also because animals such as squirrels and jays carried acorns preferentially into pine forests. Thoreau also knew about natural disturbances, as well as human disturbances (he noted that Native Americans deliberately set fire to forests). Stochastic processes. Thoreau recognized what scientists today call stochastic processes. Ecological succession is not a deterministic process, always occurring in the same way, but by stochastic chance, depending upon which species of plants as a seed source might happen to be near the disturbance. Spatial patterns of plants. Thoreau also studied spatial patterns in plants, noting that species whose seeds were dispersed by wind tended to grow in clumps, while animal-dispersed plants were more evenly spread on the landscape. Seasonal patterns. Thoreau also kept copious notes about the dates on which trees burst their buds in the spring, on which birds migrated, on which the ice thawed, and on which wild fruits matured. Modern scientists, such as botanist A. J. Miller-Rushing, have used Thoreau’s data to document that springtime comes earlier, and winter comes later, in New England today than in Thoreau’s day. Thus Thoreau started the science of phenology, which is the study of seasonal adaptations of the life cycles of plants and animals.

The most famous Thoreau quote, which reflects his important insights into the environment and sci-

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first entry ence, was “In wildness is the preservation of the world,” often misquoted as “wilderness.” To Thoreau, wildness could be found in a well-managed woodlot as easily as in the Maine woods that he visited as a young man. Thoreau was inspired by the writings of scientists who closely observed the world during their travels, particularly American botanist William Bartram, who traveled among the Cherokee of the Appalachians in the late 18th century, and Charles Darwin’s Voyage of the Beagle. Thoreau strongly believed in the complete connectedness of humans and nature (“Am I not partly leaves and vegetable mold myself?”) but did not fully understand it until he read Darwin’s Origin of Species shortly before his death. Previous to this, he had believed, as a transcendentalist, that all of nature reflected spiritual patterns. He was very serious when he observed leaf-like patterns in thawing clay and said that it was the same natural law that produced the shapes of real leaves and also of human internal organs. The Earth had a body, but its organs were on the outside: “What is man but a mass of thawing clay?” When he saw a mouse girdling a pine tree (chewing a ring of bark), he thought it was the Earth’s way of thinning out the pines. Darwin’s Origin of Species undermined Thoreau’s faith, and Thoreau spent his last years making scientific observations with few transcendentalist insights. Without Ralph Waldo Emerson, there would have been no remembrance of Thoreau. It was Emerson’s woodlot in which Thoreau briefly lived. Emerson popularized Thoreau after the latter’s death. But they were very different. Emerson would write long flowery-tongued passages about things, whether about the world of nature or the breathlessness of love, which he had not closely observed. To Thoreau, nature was a living world from which to learn; to Emerson, it was a canvas upon which to paint his grand ideas. For example, Emerson said that “savage” languages were simple and consisted mostly of nouns. Had he even bothered to ask anyone who had learned Native American languages—and there were plenty in his scholarly circle—he would have known this was wrong. But Thoreau was fascinated by what he could learn from Native Americans. (His last words were “moose” and “Indian.”) Thoreau caught pneumonia when he was in the woods counting tree rings. He was only 44 years old when he died on May 6, 1862. See also disturbances, ecological; seed dispersal; succession, ecological. Further Reading Cain, William, ed. A Historical Guide to Henry David Thoreau. Cambridge, U.K.: Oxford University Press, 2006.

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Triassic period, biodiversity in  523 Cramer, Jeffrey S., ed. Walden: A Fully Annotated Edition. New Haven, Conn.: Yale University Press, 2004. Dassow, Laura. Seeing New Worlds: Henry David Thoreau and 19th Century Science. Madison: University of Wisconsin, 1995. Dean, Bradley P., ed. Faith in a Seed: The First Publication of Thoreau’s Last Manuscript. Covelo, Calif.: Island Press, 1993. Henry David Thoreau Online. “The Succession of Forest Trees.” Available online. URL: http://www.tho reau-online.org/the-succession-of-forest-trees.html. Accessed May 16, 2011. Miller-Rushing, Abraham J., et al. “Photographs and herbarium specimens as tools to document phenological changes in response to global warming.” American Journal of Botany 93 (2006): 1,667–1,674. Richardson, Robert D. Henry Thoreau: A Life of the Mind. Berkeley: University of California Press, 1988. Robinson, David M. Natural Life: Thoreau’s Worldly Transcendentalism. Ithaca, N.Y.: Cornell University Press, 2004. Sullivan, Robert. The Thoreau You Don’t Know: What the Prophet of Environmentalism Really Meant. New York: Harper, 2009.

Triassic period, biodiversity in  The Triassic period (250 to 210 million years ago) was the first period of the Mesozoic era. It followed the Permian period, which ended with the Permian extinction. Climate. Because the continent of Pangaea was so large, and centered on the equator, the middle of the continent had hot, arid conditions. The edges of the continent were warm and humid. Low oxygen levels and high levels of carbon dioxide created a greenhouse world (see table). Continents. A single worldwide continent, Pangaea, had formed during the Permian period. The Panthalassian (“world ocean”) Sea surrounded it, and the Tethys Sea penetrated into it. The widening of the Tethys Sea separated Pangaea into the northern Laurasia and the southern Gondwana by the end of the Triassic period. Marine life. Many lineages of marine animals had become extinct at the end of the Permian period, but the surviving lines began to evolve into many new forms. ●●

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Invertebrates. The trilobites became extinct at the end of the Permian period. Brachiopods survived the extinction, but since the Triassic period they have been much less common than the superficially similar bivalve mollusks. Vertebrates. Both sharks and bony fishes continued to be abundant in the oceans. A

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Multicellular Biodiversity   in the Triassic Period Conditions Atmospheric oxygen

80% of modern level

Atmospheric carbon dioxide

5 times modern level

Global temperature

5°F (3°C) higher than today

Sea level

same as today

Approximate number of families* Continental

150

Marine

300

Total

450

Examples of marine animals Acrodus cuneocostatus

shark

Anasibirites sp.

cephalopod mollusk

Mysidiella sp.

bivalve mollusk

Shonisaurus popularis

ichthyosaur reptile

Traumatocrinus caudex

crinoid echinoderm

Examples of continental animals Cleithrolepis granulatus

bony fish

Coelophysis bauri

dinosaur

Dinodontosaurus oliveirai

mammal-like reptile

Eudimorphodon ranzii

pterosaur reptile

Ornithosuchus longidens

crocodile-like reptile

Mollenia rieki

hymenopteran insect

Parasuchus sp.

crocodile

Plateosaurus longiceps

dinosaur

Proganochelys sp.

turtle

Tanystropheus conspicuus

archosaur reptile

Tetracoleus minimus

beetle

Thrinaxodon brasiliensis

reptilelike mammal

Triadobatrachus massinoti

frog

Triassaraneus andersonorum

spider

Triassopsychoda olseni

fly

Examples of land plants Antarcticycas schopfi

cycad

Caytonia sp.

seed fern

Telemachus elongatus

conifer

*Based on Benton.

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524 Triassic period, biodiversity in 524

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triassic period, the mammallike reptile Lystrosaurus was overwhelmingly abundant (see figure). this small generalist reptile could tolerate the low oxygen of, and fi nd food in, the post-extinction world. after about 10 million years, reptiles began to evolve into numerous forms. the fi rst turtles are known from this time. the mammal-like reptiles continued to evolve, and the fi rst reptilelike mammals (such as Thrinaxodon) evolved during the triassic. During the early Triassic period, right after the Permian extinction, there Other mammal-like reptiles were few animal species. Lystrosaurus, a mammal-like reptile, was abunevolved along a separate path, dant in many parts of the world. becoming very large animals, such as Dinodontosaunew group of bony fishes, the teleosts, fi rst rus, but they became extinct appeared in the triassic period. they were at the end of the triassic. archosaur replighter and faster than earlier bony fishes. tiles evolved legs that were underneath the On the continents, reptiles proliferated body, which allowed them to run faster; this into many forms, and some of these repincluded the early crocodile Parasuchus and tiles evolved into marine forms. Tanystrothe dinosaur-like Ornithosuchus, which pheus lived on the seashore, and half of its could run on two legs. the fi rst pterosaurs 22-foot (7 m) length was neck, with which (flying reptiles) evolved at this time also. the it captured fish. the fi rst ichthyosaurs (such fi rst dinosaurs evolved during the triassic as Shonisaurus) evolved during the triasbut were a minor component of biodiversic. these reptiles were so fully adapted to sity. Some, like Coelophysis, were small, marine life that they looked very much like rapid carnivores that ran on two legs, while fish and could not come onto dry land. some herbivorous dinosaurs (such as Plateosaurus) were large (up to 26 feet, or 8 m), Continental life. Scientists speculate that the though not as large as the ones that would dry conditions in the middle of Pangaea provided an evolve in the Jurassic period. advantage to seed plants over plants that reproduced by spores and to reptiles over amphibians. Extinction. another of the mass extinctions occurred at the end of the triassic period, which ● Plant life. the seed fern Glossopteris domimay have allowed the dinosaurs to become the overnated vast forest areas at the beginning of whelmingly most abundant terrestrial vertebrates. the triassic. Seed plants later dominated See also mass extinctions; Permian over seedless plants, forming the fi rst extenextinction. sive forests of conifers, which had fi rst evolved in the late Paleozoic era. Further reading ● Invertebrates. insect lineages that evolved Benton, Michael J. “Diversification and extinction in the in the Permian, such as fl ies and beetles, history of life.” Science 268 (1995): 52–58. continued to diversify during the triassic. ———. “Four feet on the ground.” in The Book of Life: An the fi rst hymenopterans (today represented Illustrated History of the Evolution of Life on Earth, by ants, bees, and wasps) evolved during edited by Stephen J. Gould. new york: norton, 2001. the triassic but represented only a single Kubo, tai, and Michael J. Benton. “tetrapod postural shift family. estimated from Permian and triassic trackways.” Pal● Vertebrates. Some lineages of amphibaeontology 52 (2009): 1,029–1,037. ians survived the Permian extinction and Marshall, charles R., and David K. Jacobs. “Flourishing evolved into new forms. Frogs evolved durafter the end-Permian mass extinction.” Science 325 ing the triassic. at the beginning of the (2009): 1,078–1,080.

xviii+598_Biodiversity_F.indd 524

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tropical rain forests and deforestation  525 McElwain, Jennifer C., et al. “Fossil plant relative abundances indicate sudden loss of late Triassic biodiversity in East Greenland.” Science 324 (2009): 1,554–1,556.

tropical rain forests and deforestation 

Tropical forests have no winter and receive abundant rainfall during at least part of the year. Tropical seasonal forests have a rainy season and a dry season, while tropical rain forests receive rain all year (see figure). In some rain forests, the rain comes predictably every afternoon. Tropical forests exist just north and south of the equator and are called tropical because they are found between the tropic of Cancer (23.5° N) and the tropic of Capricorn (23.5° S). Temperatures remain relatively constant, within

the range of 68–77°F (20–25°C). Precipitation (all of it rain) exceeds 78 inches (200 cm) per year. Along with the lack of temperature variation, the tropical forests have relatively little wind. Tropical rain forests cover less than 5 percent of the land surface of the Earth but contain nearly half of its species and can therefore be considered the most important repositories of biodiversity in the world. However, only a few of the small biodiversity hotspots are tropical.

Biodiversity in Tropical Forests Tropical rain forest trees are evergreen. Up to half of the rain that falls comes from the transpiration of water vapor from the leaves of the trees themselves. Deforestation interrupts transpiration and allows water that would otherwise have transpired back

A rainbow appears as rain retreats from a forest in the Ecuadorian Amazon. In many rain forests, rain is a daily occurrence.  (Stanley A. Rice)

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526 tropical rain forests and deforestation  526

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up into the sky to flow out into the ocean instead. Extensive deforestation of rain forests may therefore produce a drier climate that will not support the regrowth of those forests, resulting in a destruction of the rain forest that is permanent over a time span meaningful to the human economy. Tropical rain forests have the greatest productivity of plant growth (in weight of plant material produced per area per year) as well as the highest biodiversity of species of any region of the Earth. A few acres or hectares of rain forest near Manaus, Peru, may contain as many tree and bird species as all of Europe. Each tree species may be separated from the nearest other member of its species by up to a mile (1.4 km). Borneo has 2,500 species of orchids, and it has at least 60 different tree species in an acre of forest. Among the reasons that rain forests have such prodigious species diversity are the following:

branches coil amidst the canopy branches of the trees. Many epiphytes, especially bromeliads and orchids, are rooted in litter and tree bark up in the tree branches and obtain all their water from rain and nutrients from dead leaves shed by the trees around them (see figure). Lianas are less common, and epiphytes rare, in temperate forests, where there is not enough rain to keep epiphytes alive. Because the plants divide up the layers of rain forest so finely among themselves, they also create a lot of different habitats for animals, most of which—with the exception of a few such as tapirs—spend most of their lives up in the tree branches. However, there is little evidence for horizontal specialization in rain forests; many tropical trees grow, widely spaced, over a large geographical area.

No winter. The lack of winter allows ecological interactions and thus coevolution to occur all year long. Coevolution not only produces evolutionary change but can also result in speciation. Plants, for example, cannot rely upon winter to diminish the populations of herbivorous insects. Each species of plant evolves its own set of chemical and other defenses, and each species of herbivorous animal evolves its own way of avoiding or tolerating those defenses. Many of these toxins, when used in small quantities, function as pharmaceutical compounds. Because of their high biodiversity and because so many species (especially of plants) produce toxins, tropical forests have been a gold mine in the discovery of pharmaceutical compounds. Lack of wind pollination. The lack of wind, and the persistent moisture, makes wind pollination relatively ineffective. Each flowering plant specializes upon an animal that can carry its pollen reliably over the considerable distance that separates it from the next plant of the same species. Specialization on microhabitats. The incredible abundance of moisture, warmth, and sunlight allows plants to specialize on different vertical microhabitat layers within the rain forest. The forest canopy contains many tree species, while some tree species (such as Cecropia sp.) emerge above the canopy. The dark understory contains relatively few plants, but there are many woody vines (lianas). They are rooted in the soil, but their

Not only do tropical rain forests have incredible diversity within them, but tropical forests differ markedly in species composition from place to place. Evolution has produced patterns of biogeography among different tropical forests, just as it has with other ecological communities. Tropical rain forests are famous for their endemic species. For example, Borneo has the world’s largest orchid, the largest moth, and the largest carnivorous plant; it also has squirrels, lizards, colugos, frogs, and even snakes that glide through the air. Forty-four of its 222 mammal species, 74 of its 420 bird species, 91 of its 254 reptile species, 114 of its 149 amphibian species, 160 of its 430 fish species, and 155 of its 265 species of dipterocarp trees are endemic to the island.

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Epiphytes on a tree near Santa Elena, Costa Rica. They are common in tropical rain forest trees.  (Dirk van der Made)

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tropical rain forests and deforestation  527 The vine that produces the world’s largest flower, Rafflesia arnoldii, is found only on the slopes of Mt. Kinabalu on Borneo. The rain forests of Madagascar consist mostly of species found nowhere else, including a little species of periwinkle (Catharanthus roseus) that was the original source of the important antileukemia drugs vincristine and vinblastine. Consider these patterns of canopy trees and mammals (see table on pages 528–530): ●●

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The rain forest tree species of the New World (the neotropics) are completely different from those of the Old World (the paleotropics), with few exceptions. (West Africa, like the Amazon, contains the kapok tree Ceiba pentandra, although its subspecies are unique to the neotropics.) Within the neotropics and the paleotropics, the rain forests are also largely unique. The Atlantic rain forest of South America, a narrow belt of forest in the vicinity of Rio de Janeiro and São Paulo, is distinct from the Amazon rain forest, although they share some tree species such as Slonea guianensis. Tree species in the Pacific rain forest of Colombia and coastal Ecuador differ from those of the Amazon, which is just on the other side of the Andes. The Yucatán and Central American rain forests are largely distinct from the Amazon rain forest, though they also share some species. The Indonesian and Malaysian rain forests are overwhelmingly dominated by tree species in the plant family Dipterocarpaceae, a family that is rare elsewhere in the Old World. The forests of Indonesia have a different set of species from those of India and Sri Lanka and those of northern Australia. The rain forest of eastern Madagascar is likewise unique. The plant families that are important in the Tropics are those that evolved there and tend to be less common in temperate zones. The ebony family (Ebenaceae), common in the Tropics, is represented in the United States by the persimmon tree (Diospyros virginiana). The mulberry family, which has thousands of fig and other species in the rain forests, is represented in the United States by mulberries (such as Morus rubra) and by the bois d’arc (Maclura pomifera), none of which are dominant forest tree species. Kapok trees (genus Ceiba) are in the mallow family, represented mainly by shrubs and wildflowers outside the Tropics.

xviii+598_Biodiversity_F.indd 527

Animal species differ markedly from one tropical forest to another, as in these examples: ●●

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Primates. The New World monkeys evolved separately from the Old World monkeys. Each neotropical rain forest has different monkeys. The golden lion tamarin is unique to the Atlantic rain forest, while capuchin monkeys range more widely. In the paleotropics, proboscis monkeys live in Sumatra, rhesus monkeys in and around India, and colobus monkeys in Africa. The neotropical rain forests have no apes. Among the apes, gibbons and orangutans live only in Asian rain forests, and chimpanzees and gorillas only in African rain forests. Madagascar is famous for having no monkeys or apes but only lemurs. Other placental mammals. Neotropical mammals are completely distinct from paleotropical mammals. Some neotropical mammals, such as sloths, jaguars, and tapirs, live in all neotropical rain forests. Some mammals are unique to certain rain forests, such as the okapi in Africa. Once again, Madagascar is unique. Its top predator is the fossa, which is a type of mongoose. Marsupials and monotremes. Perhaps the most distinctive feature of tropical mammal distribution is the prevalence of marsupials, and the presence of monotremes, in Australia and nearby regions such as New Guinea. The 19th-century naturalist Alfred Russel Wallace first noticed that placental mammals dominated Indonesia and that marsupials dominated the islands near Australia and proposed the now-famous Wallace’s line. Scientists now understand that this line corresponds closely to the junction of the Eurasian and Australian crustal plates. Mammals evolved separately in Asia and Australia, which came close together only recently in geological history. The dipterocarps that dominate Indonesian forests are also rare in the Australian zone. Both trees and mammals make Australia and New Guinea a world unto itself in terms of biodiversity.

Similar patterns of tropical biodiversity are found in all kinds of fungi, plants, and animals— and no doubt protists and bacteria also, although these have not yet been studied as much as animals and plants. (continues on page 530)

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528 tropical rain forests and deforestation  528

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Examples of Rain Forest Canopy Tree and Mammal Species Tree Species

Common Name

Family

Brosimum alicastrum

Breadnut

Moraceae (mulberry)

Cecropia schreberiana

Pumpwood

Moraceae (mulberry)

Ceiba pentandra

Ceiba

Malvaceae (mallow)

Dacryodes excelsa

Candlewood

Burseraceae (incense tree)

Ficus obtusifolia

Amate fig

Moraceae (mulberry)

Guarea guidonia

American muskwood

Meliaceae (mahogany)

Manilkara zapata

Sapodilla

Sapotaceae (soapwood)

Central America and Caribbean

Atlantic rain forest (Brazil) Combretaceae (Indian almond)

Buchenavia kleinii Cryptocarya moschata

Nutmeg

Lauraceae (laurel)

Euterpe edulis

Açai palm

Arecaceae (palm) Euphorbiaceae (spurge)

Sapium glandulatum Bullwood

Elaeocarpaceae (Jamaican cherry)

Astrocaryum murumuru

Murumuru palm

Arecaceae (palm)

Bertholletia excelsa

Brazil nut

Lecythidaceae (Brazil nut)

Brosimum utile

Cow tree

Moraceae (mulberry)

Carapa guianensis

Brazilian mahogany

Meliaceae (mahogany)

Cecropia peltata

Trumpet tree

Moraceae (mulberry)

Ceiba pentandra

Kapok

Malvaceae (mallow)

Cinchona officinalis

Quinine

Rubiaceae (coffee)

Platonia insignis

Bacuri

Clusiaceae (St. John’s wort)

Slonea guianensis

Bullwood

Elaeocarpaceae (Jamaican cherry)

Slonea guianensis

Amazon

Australia Flindersia brayleyana

Rutaceae (citrus)

Syzygium cormiflorum

Myrtaceae (myrtle)

Toona ciliata

Meliaceae (mahogany)

Indonesia and Malaysia Dipterocarpus gracilis

Dipterocarpaceae (dipterocarp)

Dryobalanops aromatica

Dipterocarpaceae (dipterocarp)

Shorea confusa

Dipterocarpaceae (dipterocarp)

Shorea robusta

Dipterocarpaceae (dipterocarp)

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tropical rain forests and deforestation  529 Tree Species

Common Name

Family

India and Sri Lanka Meliaceae (mahogany)

Azadirachta indica Diospyros ebenum

Ebony

Ebenaceae (ebony) Bignoniaceae (catalpa)

Millingtonia hortensis

Madagascar Albizia gummifera

Mimosaceae (mimosa)

Brochoneura acuminata

Myristicaceae

Diospyros perrierii

Ebenaceae (ebony)

Symphonia louvelii

Clusiaceae (St. John’s wort)

Africa Ceiba pentandra guineensis

African kapok

Malvaceae (mallow)

Chlorophora excelsa

Moraceae (mulberry)

Funtumia elastica

Euphorbiaceae (spurge)

Mammal Species

Common Name

Order

Ateles geoffroyi

Spider monkey

Primates

Bradypus variegatus

Three-toed sloth

Sloth/anteater

Cebus capucinus

Capuchin monkey

Primates

Panthera onca

Jaguar

Feline

Saimiri sciureus

Squirrel monkey

Primates

Tapirus terrestris

Tapir

Odd-toed ungulate

Brachyteles arachnoides

Woolly spider monkey

Primates

Bradypus variegatus

Three-toed sloth

Sloth/anteater

Leontopithecus chrysomelas

Golden lion tamarin

Primates

Panthera onca

Jaguar

Feline

Tapirus terrestris

Tapir

Odd-toed ungulate

Alouatta caraya

Black howler monkey

Primates

Ateles geoffroyi

Spider monkey

Primates

Bradypus variegatus

Three-toed sloth

Sloth/anteater

Cebus capucinus

Capuchin monkey

Primates

Hydrochaerus hydrochaerus

Capybara

Rodent

Panthera onca

Jaguar

Feline

Saimiri oerstedii

Squirrel monkey

Primates

Central America and Caribbean

Atlantic rain forest (Brazil)

Amazon

(table continues)

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Examples of Rain Forest Canopy Tree and Mammal Species (continued) Mammal Species

Common Name

Order

Ornithorhynthus anatinus

Duckbilled platypus

Monotreme

Perameles nasuta

Long-nosed bandicoot

Marsupial

Dicerorhinus sumatrensis

Sumatra rhinoceros

Odd-toed ungulate

Hylobates moloch

Gibbon

Primates

Nasalis larvatus

Proboscis monkey

Primates

Panthera tigris

Tiger

Feline

Pongo borneo

Orangutan

Primates

Hoolock hoolock

Hoolock gibbon

Primates

Macca mulatta

Rhesus monkey

Primates

Panthera tigris

Tiger

Feline

Tapirus indicus

Malayan tapir

Odd-toed ungulate

Cryptoprocta ferox

Fossa

Carnivore

Daubentonia madagascariensis

Aye-aye

Primates

Eulemur macaco

Black lemur

Primates

Colobus angolensis

Colobus monkey

Primates

Gorilla gorilla

Gorilla

Primates

Hippopotamus amphibius

Hippopotamus

Even-toed ungulate

Hystrix cristata

Porcupine

Rodent

Okapia johnstoni

Okapi

Even-toed ungulate

Pan paniscus

Bonobo

Primates

Pan troglodytes

Chimpanzee

Primates

Australia

Indonesia and Malaysia

India and Sri Lanka

Madagascar

Africa

(continued from page 527) The extreme productivity and biodiversity of tropical rain forests creates the impression that the soils must be very rich. Indeed, this was what some Europeans and Americans initially believed when they tried to establish large plantations. They discovered, however, that most tropical forest soil is very poor in nutrients and acidic. Not only do the soils have few nutrients, but they cannot hold

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onto the nutrients that are introduced by decomposition. Decomposition is rapid due to the high heat and humidity, and soils are subject to heavy leaching. Leaching is the removal in solution of mineral salts or organic matter from an upper to a lower soil horizon by the action of percolating water either naturally (by rainwater) or artificially (by irrigation). Therefore, many tropical forests are

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tropical rain forests and deforestation  531 tree trunks and bromeliad leaf bases, and parasitize treetop animals living in the canopy. Destruction of these forests often has the unintended side effect of bringing humans and mosquitoes into more intense contact, thereby enhancing the spread of diseases such as malaria and yellow fever. Scientists who study rain forests now often work in treetop perches, traveling by rope bridges or cables from one tree to another, and often coming and going by means of helicopters, largely ignoring the shade underneath them.

Destruction of Tropical Forests Tropical deforestation in Brazil. The red soil, where trees have been cut down, is poor in nutrients and will raise meager crops. Biodiversity has been degraded in the remaining forest fragment.  (Alberto Cesar; Greenpeace; courtesy Rechargenews.com)

sitting on top of, rather than growing in, the soil. As soon as leaf litter decomposes, the roots of the trees absorb the nutrients. When the forests are cut down, the nutrients are lost, leaving a ravaged landscape in which relatively few plants, including few agricultural plants, can grow. Recent evidence suggests that some small regions of “black soil” (terra preta de Indio) in South American rain forests were artificially produced by composting by Native tribes in Precolumbian times to produce soil suitable for agriculture. Some tropical forests near volcanoes, such as those of the western Amazon Basin and the Philippines, have rich soils continually replenished by nutrients from volcanic ash. Rain forest soils near major rivers may receive nutrients from river silt. However, in most tropical forests, it takes a very long time for forests to grow back, so long that tropical forest destruction may be permanent on time scales that matter to the human economy. In many tropical rain forests, there is sufficient rainfall that many plant species can grow without being rooted in the soil. These epiphytes include vines, bromeliads, and orchids. The competition for light is so intense that most of the plant species and most of the leaf area of the trees are found in the canopy. The understory of a tropical rain forest may have extensive areas without very much plant growth, except for tree trunks. The popular image of the “jungle” being nearly impenetrable without machetes is true of the edges of these forests and of areas where the original forest has been disturbed. Most animal species also live in the canopy. This includes many of the vectors of disease, such as mosquitoes, which grow in small pools of water in

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Tropical rain forests are being lost at an alarming rate: 46,300 square miles (120,000 km 2) per year. Half of the original 5.4 to 7 million square miles (14–18 million km 2) of rain forest has been destroyed (see photograph). Tropical rain forests are just as capable of responding to natural disturbances as are any other ecological communities. In temperate forests, many seeds remain dormant in the soil until a disturbance occurs, at which time they germinate. In tropical forests, seeds have little dormancy and will often germinate in the shade and grow slowly. If a disturbance clears away some of the canopy overhead, they begin growing quickly. In the Amazon rain forest, some Native American tribes and peasants of European descent make their living partly by raising crops in small clearings. Tribal peoples in rain forests all over the world have done the same. In this slash and burn or shifting agriculture, a small plot of rain forest trees is cut, allowed to dry, and burned. The ashes contribute nutrients to the poor soil, allowing a rich growth of crops. The poor soil, however, does not hold the nutrients, which soon wash away. The farmers then abandon the field and allow secondary succession to occur. The rain forest recovers from these small disturbances, as leaf litter and tree seeds come in from the nearby forest. Within decades, the rain forest reclaims the opening (see figure on page 532). This kind of shifting agriculture is not permanently dangerous to tropical forests unless it occurs at a high frequency due to the activity of dense human populations. However, when a very large rain forest clearing is created and then abandoned, most of the clearing is far away from the forest edge from which seeds and leaf litter would come to begin the successional process. Seeds of rain forest species, unlike the colonizing species of temperate zones, do not remain dormant in the soil, but die within months of being shed. Moreover, while a small clearing is partially shaded by the nearby forest, the middle of a large

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Governments of tropical countries could not believe that the forests would ever run out. However, forests even larger than the amazon rain forest (such as the eastern deciduous forest of the United States) have been cut down. therefore, the destruction of the amazon rain forest is not impossible. certainly, smaller tropical forests, such as the atlantic forest of Brazil, are vulnerable. conservationists proclaimed that rain forest destruction would lead to disaster, not only for tropical countries but for the whole world. about 1990, governments all over the world began to realize that the conservationists had been right: Rain forests were threatened with annihilation, a prospect with consequences for the whole earth. By then, the forces of destruction had become so great that they can hardly be slowed, much less stopped. the Brazilian government, which had once waged war on its green hell, Seedling regrowth and seed dispersal occur rapidly in a small gap disturnow used satellite imagery to help bance in a tropical forest but much more slowly in a large disturbed area. government officials track down and stop people from cutting the clearing is baked by the tropical sun, which kills forests. But even this has not rescued the rain forests. seedlings and dries the thin soil despite frequent Here are some of the seemingly unstoppable forces rains (see figure). the few plants that live in the dry of destruction: open area are more prone to fi re, which further sets back the successional process. Soil erosion occurs ● Pastures. Many central and South ameriseverely in large clearings, making the chances of can rain forests have been cut down to prorecovery even slimmer. Gradually, succession occurs duce pastureland for cattle. Some american along the edges of the clearing. if the extensive and multinational fast-food corporations destruction of forests causes a local reduction in have imported beef from pastures that had rainfall, the large clearing may become a permanent once been central american rain forest. arid zone, and the reduced rainfall may harm even Because the soil is bad, lands that had once the rain forest that remains uncut. the good news is been the world’s richest forests now became that when forest succession does occur, most of the the world’s poorest pastures. plant species (more than 90 percent, according to ● Agriculture. the large coastal cities of Braplant ecologist Robin chazdon) return. zil teem with poor people. the government Just a few decades ago, the rain forests of the believed that the solution to their poverty world seemed not only eternal but impenetrable. was to bus them out into the amazon rain Many people believed that “the jungle” was merely a forest and give them free land. this soluhindrance to the development of useful land. calling tion has not worked, for the poor soil of the it a “green hell,” the Brazilian government launched rain forest makes terrible farmland, leava campaign to conquer the amazon rain forest, even ing the peasants as poor in the rain forest moving their capital from the coast to the jungle as they had been back in the city. Further, outpost of Brasília. During the 1970s and even more the population of poor in the cities has not during the 1980s, rain forests all over the world were diminished noticeably. Peasants destroy demolished. only about one-quarter as much forest as

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tropical rain forests and deforestation  533

●●

●●

●●

●●

pastures in Brazil. But peasant agriculture is a small force compared to large-scale commercial agriculture. In Borneo, one-third of the rain forest that existed in 1985 had been destroyed by 2005, a great deal of it to create plantations of oil palm. In Brazil, soybean plantations are having a similar effect on the Amazon rain forest. Logging. Some tropical trees provide the world’s best wood for carpentry and musical instruments. Logging of these trees, however, accounts for very little deforestation. Most trees that are cut by tropical loggers are simply burned; those that are used mostly end up as wood chips for paper, a tragic waste of some of the world’s best wood. Many Southeast Asian rain forests have been destroyed largely to produce cardboard. Selective logging removes trees with high economic value and leaves the others. Although selective logging does not destroy a rain forest, it may alter it considerably by reducing the canopy cover and allowing drier conditions. Extraction of underground resources. The rain forests of Ecuador are rich in petroleum. Much rain forest has been destroyed during the exploration for and extraction of oil, as well as by the spilling of toxic materials. Rich gold deposits in Brazilian rain forests have tempted thousands of miners to strip away whole mountainsides of soil. Gold extraction uses mercury, which severely pollutes rivers downstream far from the actual site of destruction. In Africa, rain forests have been destroyed for diamond mining. On Borneo, large tracts of rain forest are destroyed for coal mining. War. A great deal of rain forest destruction occurred during the Vietnam War, much of it by the aerial spraying of defoliant chemicals. Some destruction of the Amazon rain forest was apparently intended to bring independent Native tribes under the control of the central government. Dams. Some tropical countries have built dams for hydroelectric power. In low-lying tropical areas, these reservoirs are often shallow and very extensive, destroying much rain forest. Many farmers cut down forests on slopes surrounding the reservoir, leading to soil erosion, which clogs the reservoirs and makes them useless soon after they are built.

Can anything be done to stop the direct destruction of the rain forests? A few promising trends are

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occurring, although they may be too little too late. They include the following: Policy decisions. Governments of tropical countries, such as Brazil, are beginning to prohibit deforestation. Costa Rica has set aside almost one-quarter of its area as land managed for conservation. The World Bank has begun requiring tropical countries to protect their rain forests before it agrees to lend money to them. In several cases, some debts that tropical countries owe to the major industrialized countries have been waived in return for rain forest preservation projects. Political leaders around the world are beginning to discuss the possibility that industrial countries, which benefit because tropical rain forests remove carbon dioxide from the atmosphere, should pay the developing tropical countries for these important environmental services. Perhaps the major example is the United Nations REDD Program (Reducing Emissions from Deforestation and Forest Degradation). While government and bank policy decisions are not enough by themselves, there would be no hope of rain forest conservation without them. Meanwhile, many countries with a lot of rain forest land continue to have corrupt governments. Indonesia has emerged from the Suharto regime, in which concessions to “develop” rain forest land were given almost for free to the dictator’s associates. At local levels, corruption continues almost unabated. Agreements to save rain forests mean absolutely nothing in countries with corrupt governments. Sustainable use of rain forest lands and securing land rights. Many countries have realized that the intact rain forest is more profitable than one that has been cut down. Brazil has established several extractive preserves in which people live in the rain forest, have small garden plots, and hunt a limited amount of game. They collect sap from native rubber trees and make it into rubber, a process that does not kill the trees. They also gather and sell many native forest nuts (including Brazil nuts), fruits, and cocoa pods. These preserves have been successful; however, the people who live in them are poor, and not many people have chosen to move into the rain forest preserves to pursue this career. Extractive preserves cannot by themselves save the rain forests. As noted above, many pharmaceutical compounds were first discovered in the leaves of rain forest plants. Pharmaceutical companies formerly obtained plant specimens for free but now must pay for the privilege of pharmaceutical prospecting. Their money helps make the preservation of intact rain forests profitable. Reclaiming degraded tropical lands. Former rain forest lands that have been severely degraded seem almost beyond hope for reclamation. However, in some cases, trees have been replanted. Some rain forest seedlings can survive bright sunlight and can

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534 tropical rain forests and deforestation  534 be planted in the middle of the denuded wasteland. These seedlings require much care from humans to survive. However, once these trees become large enough to survive on their own, birds and bats will roost in them and drop seeds under them. The seeds grow into yet more tree seedlings. The large trees cast shade in which seedlings of shade-tolerant tree species can survive. These replanted trees, though few in number, may serve as nuclei for natural successional processes. The legal basis of the extractive preserves and pharmaceutical prospecting is perhaps more important than their profitability. The rights of indigenous tribes and of rain forest peasants to their lands must be recognized. In the past, governments acted as if the rain forests were free, empty land, whereas in reality they were filled with tribal peoples. This is the same policy that the United States took toward the Native American lands in the 19th century. Only now in Brazil and Southeast Asia are tribal peoples beginning to receive the right to pursue their traditional styles of life, on their own lands, safe from agriculture, pastures, mining, and lumbering by outsiders. It is widely understood that there is no way to save the rain forests unless the poor people of tropical countries have a way of making a living. In a few places, rain forest destruction has been slowed, as tropical governments and citizens all over the world have begun to recognize the importance of rain forests. But deforestation rates seemed to be more closely connected to the economy than to conservation sentiments. In Brazil, for example, deforestation decreased during times of recession and increased during times of recovery. Because a great deal of rain forest destruction in Brazil is due to creating soybean fields, deforestation rates rise and fall with soybean prices. Brazilian deforestation in 2005–2009 was only 36 percent as great as its 1996–2005 average, largely because the international timber market now demands that rain forest timber come from certified plantations rather than wild rain forests. The Brazilian government has the power to make banks cancel credit extended to large landowners who are logging rain forest land illegally. Although 51 percent of the remaining rain forest in Brazil is protected, enforcement is difficult and imperfect. Much destruction will continue even after everyone agrees that the rain forests should be saved, for the forces of destruction may have taken on a momentum of their own.

Tropical Deforestation and Global Warming Recent estimates have indicated that the rates of tropical deforestation are less than had previously been estimated and that fewer species are threat-

xviii+598_Biodiversity_F.indd 534

first entry ened with extinction than had been thought. At the same time that this good news emerged, however, scientists began making predictions about the effects of global warming on ecosystems around the world. Like every other ecosystem, tropical forests will experience climatic shifts. The consequences are almost certain to be more dramatic than any that could have resulted from deforestation. Some tropical forests, such as those of the southern Amazon Basin, will experience warmer, drier conditions, which will not only cause the death of many trees, smaller plants, and animals that require a moist habitat but will encourage the spread of fires, which will encourage the spread of fire-adapted vegetation. Fires have already become more common in rain forest lands. Tropical trees, with thin bark, are very easily killed by fires. Some tropical forests, however, such as those of the northern Amazon Basin, will experience warmer, wetter conditions, which is a set of conditions found no place in the world today. As a result, the consequences for these forests cannot be predicted. As with nearly every other environmental challenge described in this book, the protection of the tropical rain forests will primarily depend upon the prevention of an excessive greenhouse effect. Tropical deforestation is one of the major contributors to the greenhouse effect. On Borneo, 11 percent of the land is peat swamp, which has organic matter up to 60 feet (almost 20 m) deep. When an acre of regular rain forest land is cleared and burned, about 300 tons of carbon dioxide (702 metric tons per hectare) are released into the air; clearing of peat swamp puts about 725 tons per acre (1,650 metric tons per hectare) into the air. Every year thereafter, an acre of peat soil puts almost 25 tons of carbon dioxide (55 metric tons per hectare) into the air just because the peat decomposes in the sunny dry conditions. This contrasts with the one ton (2.5 metric tonnes) per year that a typical American household releases. These are the principal reasons that Indonesia is the number-three emitter of carbon, after the United States and China. The tropical rain forests collectively have the greatest biodiversity of any ecological community on the planet and are also being destroyed more rapidly than any other. Their destruction not only reduces global biodiversity but contributes to the greenhouse effect, both by releasing carbon and by reducing photosynthesis. It is in the political and economic interest, not just the scientific interest, of the developed world to reward developing nations for protecting their rain forests, in a manner pioneered by the United Nations REDD program. See also biodiversity, resources for medicine; biogeography; coevolution; disturbances, ecological; endemic species;

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tropical seasonal forests  535 greenhouse effect and biodiversity; speciation; succession, ecological; tropical seasonal forests. Further Reading Anderson, Anthony B. Alternatives to Deforestation: Steps toward Sustainable Use of the Amazon Rain Forest. New York: Columbia University Press, 1990. Cole, R. J., K. D. Holl, and R. A. Zahawi. “Seed rain under tree islands planted to restore degraded lands in a tropical agricultural landscape.” Ecological Application, 20 (2010): 1,255–1,269. Cowell, Adrian. The Decade of Destruction: The Crusade to Save the Amazon Rain Forest. New York: Henry Holt, 1990. Dauvergne, Peter. Shadows in the Forest: Japan and the Politics of Timber in Southeast Asia. Cambridge, Mass.: MIT Press, 1997. De Onis, Juan. The Green Cathedral: Sustainable Development of Amazonia. New York: Oxford University Press, 1992. Klanderud, Kari, et al. “Recovery of plant species richness and composition after slash-and-burn agriculture in a tropical rain forest in Madagascar.” Biodiversity and Conservation 19 (2010): 187–204. Laborde, Javier, et al. “Tree and shrub seed dispersal in pastures: The importance of rain forest trees outside of forest fragments.” Ecoscience 15 (2008): 6–16. Laurance, William F., and Carlos A. Peres, eds. Emerging Threats to Tropical Forests. Chicago: University of Chicago Press, 2006. Leigh, Egbert Giles. Tropical Forest Ecology: A View from Barro Colorado Island. Oxford, U.K.: Oxford University Press, 1999. Guevara, Sergio, et al. “The role of remnant forest trees in tropical secondary succession.” Plant Ecology 66 (1986): 77–84. Hecht, Susanna, and Alexander Cockburn. The Fate of the Forest: Developers, Destroyers, and Defenders of the Amazon. Updated ed. Chicago: University of Chicago Press, 2010. Hooper, Elaine R., et al. “Factors affecting composition of forest regeneration of deforested, abandoned land in Panama.” Ecology 85 (2004): 3,313–3,326. Marcus, Bernard. Tropical Forests. Sudbury, Mass.: Jones and Bartlett, 2008. Martin, Patrick H., Ruth E. Sherman, and Timothy J. Fahey. “Forty years of tropical forest recovery from agriculture: Structure and floristics of secondary and old-growth riparian forests in the Dominican Republic.” Biotropica 36 (2004): 297–317. Montagnini, Florencia, and Carl F. Jordan. Tropical Forest Ecology: The Basis for Conservation and Management. New York: Springer, 2005. Nepstad, Daniel, et al. “The end of deforestation in the Brazilian Amazon.” Science 326 (2009): 1,350–1,351.

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Phillips, Oliver L., et al. “Drought sensitivity of the Amazon rain forest.” Science 323 (2009): 1,344–1,347. Plotkin, Mark J. Tales of a Shaman’s Apprentice: An Ethnobotanist Searches for New Medicines in the Amazon Rain Forest. New York: Viking, 1993. Rice, Stanley A. “An injured paradise.” Chap. 1 in Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. Royte, Elizabeth. The Tapir’s Morning Bath: Mysteries of the Tropical Rain Forest and the Scientists Who Are Trying to Solve Them. Boston: Houghton Mifflin, 2001. Schlawin, Justin R., and R. A. Zahawi. “ ‘Nucleating’ succession in recovering neotropical wet forests: The legacy of remnant trees.” Journal of Vegetation Science 19 (2008): 485–492. Spray, Sharon L., and Matthew D. Moran. Tropical Deforestation. Lanham, Md.: Rowman and Littlefield, 2006. Stokstad, Erik. “Debate continues over rain forest fate— with a climate twist.” Science 323 (2009): 448. Terborgh, John. Requiem for Nature. Covelo, Calif.: Island Press, 1999. United Nations. “UN-REDD Programme: The United Nations Collaborative Programme on Reducing Emissions from Deforestation and Forest Degradation in Developing Countries.” Available online. URL: http:// www.un-redd.org. Accessed August 8, 2011. Vazquez-Yanes, C., and A. Orozco-Segovia. “Patterns of seed longevity and germination in the tropical rain forest.” Annual Review of Ecology and Systematics 24 (1993): 69–87. Vieira, I. C. G., Christopher Uhl, and Daniel Nepstad. “The role of the shrub Cordia multispicata Cham. as a succession ‘facilitator’ in an abandoned pasture, Paragominas, Amazonia.” Vegetatio 115 (1994): 91–99. White, Mel. “Borneo’s moment of truth.” National Geographic, November 2008, 36–63. Willson, Mary F., and F. H. J. Crome. “Patterns of seed rain at the edge of a tropical Queensland rain forest.” Journal of Tropical Ecology 5 (1989): 301–308. Zahawi, R. A. “Instant trees: Using giant vegetative stakes in tropical forest restoration.” Forest Ecology and Management 255 (2008): 3,013–3,016.

tropical seasonal forests  Tropical forests,

found between the tropic of Cancer and the tropic of Capricorn, do not have winters. Most tropical forests are rain forests, in which there is no dry season. The year-round rainfall occurs because water vapor condenses and rains down upon the Tropics. Near the northern and southern edges of the tropical zone, however, air from which the moisture has rained out descends toward the surface of the Earth, causing drier conditions. At about 30° north

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536 tropical seasonal forests  536

first entry

Some Trees of the Tropical Seasonal Forests Scientific Name

Common Name

Plant Family

Albizia saman

Monkey pod

Fabaceae (legume)

Bursera grandifolia

Elephant tree

Burseraceae

Central America, Mexico

Euphorbiaceae (spurge)

Calaenodendron mexicanum Cordia alliodora

Tropical laurel

Boraginaceae

Enterolobium cyclocarpum

Guanacaste

Fabaceae (legume)

Leucaena leucocephala

White leadtree

Fabaceae (legume)

Schizolobium parahyba

Brazilian fire tree

Fabaceae (legume)

Swietenia macrophylla

Mahogany

Meliaceae (mahogany)

Vachellia farnesiana

Needle bush

Fabaceae (legume)

South America Fabaceae (legume)

Acosmium cardenasii Amburana cearensis

Amburana

Fabaceae (legume)

Anadenanthera macrocarpa

Red angico

Fabaceae (legume)

Cavanillesia arborea

Barriguda

Malvaceae (mallow)

Cedrela fissilis

Brazilian cedarwood

Meliaceae (mahogany)

Centrolobium microchaete

Canarywood

Fabaceae (legume)

Copernicia prunifera

carnauba palm

Arecaceae (palm)

Cordia alliodora

Tropical laurel

Boraginaceae

Myracrodruon urundeuva

Aroeira-do-sertão

Anacardiaceae (sumac)

Phyllostylon rhamnoides

Palo amarillo

Ulmaceae (elm)

Schinopsis brasiliensis

Ironwood

Anacardiaceae (sumac)

Tabebuia impetiginosa

Pink trumpet tree

Bignoniaceae (catalpa)

Acacia xanthophloea

Fever tree

Fabaceae (legume)

Brachystegia glaucescens

Mu’unze

Fabaceae (legume)

Cynometra alexandri

Muhimbi

Fabaceae (legume)

Orchid tree

Fabaceae (legume)

Africa

Asia Bauhinia variegata

Dipterocarpaceae

Dipterocarpus obtusifolius Ficus religiosa

Bo, peepal

Moraceae (mulberry)

Shorea robusta

Sal

Dipterocarpaceae Dipterocarpaceae

Shorea siamensis Tectona grandis

xviii+598_Biodiversity_F.indd 536

Teak

Lamiaceae (mint)

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tundra  537 and south latitude, the dry air results in a band of deserts. In the transitional zone between tropics and deserts, between about 10° and 20° north and south latitude, there are tropical forests that have dry seasons: the tropical seasonal forests. The dominant trees of these forests are usually deciduous, losing their leaves during the dry season. Evergreen broadleaf trees may dominate tropical seasonal forests with access to groundwater supplies, or that have infertile soil. In Asia, where the wet season comes from monsoon rains, the forests are called monsoon forests. Tropical seasonal forests are common in Mexico and Central America, where leguminous trees predominate (see table on page 536). When the larger trees shed their leaves at the beginning of the dry season, many smaller trees of the genus Acacia retain their leaves. Retaining leaves during the dry season may make a tree the highly visible target of herbivores, but these acacia trees are protected by ferocious ants with which they have a mutualistic relationship. Tropical seasonal forests also dominate areas around the Amazon rain forest. The caatinga of northeastern Brazil has short deciduous trees mixed with evergreen palm trees. Cacti may grow in the openings between these trees. Some areas of Bolivia also have tropical dry forests. Acacias and related leguminous trees also dominate the tropical dry forests of Africa, which are between the rain forests and the savannas. Acacias are also the most important trees in the savannas. The dry forests of India and Indochina contain trees that are relatives of South Asian rain forest species, for example the dipterocarps. Teak, a tree whose timber was very important in shipbuilding in earlier centuries, is one of the few tree-sized species in the mint family. Many mammal and bird species live in these forests, including gibbons (Hylobates concolor), monkeys such as the langur Pygathrix nemaeus, Asian elephants (Elephas maximus), and tigers (Panthera tigris), which also live in rain forests. See also tropical rain forests and deforestation. Further Reading Becerra, Judith X. “Timing the origin and expansion of the Mexican tropical dry forest.” Proceedings of the National Academy of Sciences USA 102 (2005): 10,919–10,923. Bowden, Charles, and Jack W. Dykinga. The Secret Forest. Albuquerque: University of New Mexico Press, 1993. Bullock, Stephen H., and J. Arturo Solis-Magallanes. “Phenology of canopy trees of a tropical deciduous forest in Mexico.” Biotropica 22 (1990): 22–35. Espiríto-Santo, Mário M., et al. “Sustainability of tropical dry forests: Two case studies in southeastern and

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central Brazil.” Forest Ecology and Management 258 (2009): 922–930. Högberg, Peter. “Root symbioses of trees in African dry tropical forests.” Journal of Vegetation Science 25 (2009): 393–400. Justiniano, Marcos Joaquin, and Todd S. Fredericksen. “Phenology of tree species in Bolivian dry forests.” Biotropica 32 (2000): 276–281. Kennard, Deborah K. “Secondary forest succession in a tropical dry forest: Patterns of development across a 50-year chronosequence in lowland Bolivia.” Journal of Tropical Ecology (2002) 18: 53–66. Marod, Dokrak. “Effects of drought and fire on seedling survival and growth under contrasting light conditions in a seasonal tropical forest.” Journal of Vegetation Science 15 (2004): 691–700. Swaine, M. D. “Characteristics of dry forest in West Africa and the influence of fire.” Journal of Vegetation Science 8 (1992): 365–374. Vieira, Daniel L. M., et al. “Effects of habitat, cattle grazing and selective logging on seedling survival and growth in dry forests of central Brazil.” Biotropica 39 (2006): 269–274. ———, and Aldicir Scariot. “Principles of natural regeneration of tropical dry forests for restoration.” Restoration Ecology 14 (2006): 11–20.

tundra  Tundra is the plant community that lives in the coldest parts of the Earth that are capable of supporting a plant cover. It consists of short perennial plants, both herbaceous and woody. Only the polar deserts, in which very few plants grow, are colder. Arctic tundra is found in a ring around the Arctic Ocean: northern Alaska and Canada, extreme northern Europe, and northern Siberia. Alpine tundra is found on the tops of the tallest mountains in North America, Europe, and Asia. During the most recent ice age, tundra was found in a latitudinal line across the middle of what is now the United States. As the glaciers retreated, many tundra plants moved northward by seed dispersal to their present arctic locations. Some of the plants, however, migrated up to the tops of mountains, where they are found today in the highest elevations of the Rocky Mountain system (see photograph on page 538). The alpine tundra of the Sierra Nevada of California also has some of the same species of plants as the arctic tundra. Because the alpine tundra of the Sierra Nevada is drier than the tundra of the Cascades and the Arctic, it has a much less extensive plant cover and includes some plant species whose evolutionary ancestors came from the desert rather than from the arctic tundra. Extensive alpine tundra can be found in Sequoia, Yellowstone, and Rocky Mountain National Parks.

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538 tundra  538

Flowers bloom abundantly in the alpine tundra during the brief summer in the Rocky Mountains of Colorado.  (Stanley A. Rice)

It is the overwhelmingly cold conditions that define nearly every characteristic of the tundra. The winters are long and extremely cold. The only plants that can survive are those that are short enough to be protected by the snow in the winter. The effect is also a cause: There are no tall trees to slow down the wind. In the brief summer, the snow melts, as does the surface layer of soil. However, below this depth, the soil remains permanently frozen (permafrost). The shallow soil is another reason that tall trees do not live in the tundra. The tundra plants include sedges, wildflowers, and short willows (see table on page 539). Nearly all are perennials, for the growing season is too short to allow an annual plant to complete its life cycle in a single season. The permafrost also inhibits the ability of melted water to drain away. The tundra is very wet, even though in some cases the amount of precipitation is low enough that the habitat would, were it not for the permafrost, qualify as a desert. The cold, wet conditions mean that what little soil is available to the plants is poor and acidic. The pools

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first entry of water also hatch massive hordes of mosquitoes. The alpine tundra does, however, provide food for large herds of grazing mammals, such as caribou and musk oxen. The mammals of the alpine tundra are small, such as the pika (see table on page 539). Some tundra plant species, such as the mountain avens (Dryas octopetala) and the dwarf azaelea (Loiseleuria procumbens), grow in arctic and alpine tundra worldwide. Other genera of plants, such as the Ranunculus buttercups and Polemonium sky pilots, have different species in each tundra region. This has occurred because speciation has proceeded to different extents in different plant genera. A completely different set of plant species has evolved in the páramo tundra of South America, because this region was never connected with the alpine tundra during the ice ages. Despite its low productivity, the tundra supports many animals, such as reindeer and musk oxen. The large size of these mammals (and also of the nowextinct mammoths and mastodons) is beneficial for retaining body heat during cold winters. Smaller tundra mammals, such as pikas, hibernate. Some tundra mammals, such as the reindeer (called caribou in North America), range across the entire arctic tundra. Musk oxen are native only to North American arctic tundra. Pikas, which are small relatives of the rabbit, live in alpine tundra worldwide, but each region has different species. In some drier spots in the tundra, wildflowers occur in the form of cushion plants, such as the dwarf azalea. Composed of several different species, cushion plants really look like little cushions or pillows on the ground. This condensed growth form protects the stems from the effects of the wind and allows dead leaves to build up a rich soil directly underneath the plants. They therefore create tiny zones of good growing conditions immediately around them. Pollination is a risky business in the tundra, as the weather conditions do not reliably allow insect pollinators to be present. Some plant species, such as the bistort Polygonum viviparum and the grass Poa alpina var. vivipara, have evolved the ability to produce bulblets where they would otherwise produce flowers. Because the bulblets fall to the ground after they have already begun to grow, these plants are said to be viviparous (having “live birth”). Despite their similarities in temperature conditions, arctic and alpine tundra experience very different sunlight conditions. In the arctic tundra, the winter has long and often continuous nights, whereas the summer has long days when the sun may not set for several weeks. In the alpine tundra, days and nights are of more equal length: The Ecuadorean páramo region and the alpine grasslands of Papua New Guinea experience approximately

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tundra  539 Examples of Tundra Plant and Mammal Species Plant Species

Common Name

North America

Eurasia

Arctic

Alpine

Arctic

Alpine

x

x

x

x

x

Wildflowers Dryas octopetala

mountain avens

x

Polygonum bistorta

bistort

x

Polygonum bistortoides

bistort

x

Polemonium boreale

Jacob’s ladder

Polemonium caeruleum

Jacob’s ladder

Polemonium viscosum

sky pilot

x

Ranunculus adoneus

alpine buttercup

x

Ranunculus altaicus

Siberian buttercup

Ranunculus glacialis

glacier buttercup

Ranunculus nivalis

snow buttercup

x

Carex aquatilis

water sedge

x

x

x

x

Eriophorum vaginatum

cottonsedge

x

x

x

x

Poa alpina

alpine meadowgrass

x

x

x

x

Betula nana

dwarf birch

x

x

x

Cassiope tetragona

arctic bell

x

x

x

Loiseleuria procumbens

dwarf azaelea

x

x

x

Salix nivalis

snow willow

Salix polaris

polar willow

Salix reticulata

netleaf willow

Mammal Species

Common Name

x x

x x

x

x x x

Sedges and grasses

Shrubs

x

x x x

Habitat North America

Eurasia

Arctic Lemmus lemmus

Norway lemming

x

Lemmus sibiricus

Siberian lemming

x

Lemmus trimuconatus

American lemming

x

Ovibos moschatus

musk oxen

x

Rangifer tarandus

reindeer/caribou

x

x

Alpine Ochotona himalayana

Himalayan pika

Ochotona princeps

American pika

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x x

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540 tundra  540

A whitebark pine (Pinus albicaulis) grows in a krummholz form near Lassen Peak in California. By growing near the ground, the tree is protected by the snowpack from winter winds.  (Stanley A. Rice)

12-hour days all year. Tropical alpine tundra, unlike the arctic tundra, is bombarded with intense ultraviolet radiation. Tundra intergrades with boreal forest. A transitional zone that can be 60 miles (100 km) in width connects the arctic tundra and the boreal forest in Canada. The boreal forest dominates the warm south-facing well-drained slopes in this zone. The transitional zone between alpine tundra and subalpine forest is characterized by stunted subalpine trees (krummholz) that are often short enough to be protected by snow in the winter and which may have branches only on the leeward side where winter winds have not killed them (see figure). The krummholz trees form a vaguely defined timberline. Because alpine tundra is wet, acidic, and poor in nutrients, many arctic tundra plant species found refuge in bogs as the glaciers retreated northward. Examples include sphagnum moss and the sedges Eriophorum vaginatum and Carex aquatilis. Global warming threatens the tundra in two ways. Alpine tundra can only survive on cold mountaintops; if mountaintops become even a little bit

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first entry warmer, as a consequence of global warming, forests may grow all the way to the top, resulting in the elimination of the alpine tundra. In addition, arctic tundra now experiences warmer and drier conditions. In 2007, a fire spread through the tundra of Alaska’s North Slope, burning more area than all North Slope fires back to 1950 combined. Fires are sufficiently rare in the tundra that recovery from them is very slow. Because global warming is occurring more rapidly in the Arctic than anywhere else in the world, the arctic tundra is being closely studied. The deep organic matter in the soils, accumulated and frozen over millennia, will almost certainly be a major source of carbon dioxide and methane in the atmosphere. The arctic tundra on the north slope of Alaska is also threatened by oil extraction. While controversy surrounded the opening of the Arctic National Wildlife Refuge to oil extraction, the federal government went ahead and leased petroleum rights on the adjacent land and offshore areas. The reason that oil extraction may prove disastrous is that the slow growth of tundra plants will not allow significant recovery from any disturbances from construction. Ruts caused by vehicles driving through tundra mud often look as fresh as new even decades after they are formed. See also boreal and subalpine forests; deserts, polar; disturbances, ecological; ice ages. Further Reading Aerts, Rien. “Nitrogen-dependent recovery of subarctic tundra vegetation after simulation of extreme winter warming damage to Empetrum hermaphroditicum.” Global Change Biology 16 (2010): 1,071–1,081. Auger, Sarah, and Serge Payetfe. “Four millennia of woodland structure and dynamics at the Arctic treeline of eastern Canada.” Ecology 91 (2010): 1,367–1,379. Blok, D., et al. “Shrub expansion may reduce summer permafrost thaw in Siberian tundra.” Global Change Biology 16 (2010): 1,296–1,305. Campbell, Barbara J., et al. “The effect of nutrient deposition on bacterial communities in Arctic tundra soil.” Environmental Microbiology 12 (2010): 1,842–1,854. Forbes, Bruce C., et al. “Russian Arctic warming and ‘greening’ are closely tracked by tundra shrub willows.” Global Change Biology 16 (2010): 1,542–1,554. Hallinger, Martin, et al. “Establishing a missing link: Warm summers and winter snow cover promote shrub expansion into alpine tundra in Scandinavia.” New Phytologist 186 (2010): 890–899. Jones, Michael T., and Scott D. Smyers. “Occurrence of pond-breeding amphibians at alpine ponds in the

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tundra  541 White Mountains, New Hampshire.” Northeastern Naturalist 17 (2010): 161–166. Nagy, Laszlo, and Georg Grabherr. The Biology of Alpine Habitats. Oxford, U.K.: Oxford University Press, 2009. Rice, Stanley A. “Plants create habitats.” Chap. 8 in Green Planet: How Plants Keep the Earth Alive. Piscataway, N.J.: Rutgers University Press, 2009.

xviii+598_Biodiversity_F.indd 541

Sturm, Matthew. “Arctic plants feel the heat.” Scientific American, May 2010, 66–73. Sullivan, Patrick F. “Snow distribution, soil temperature, and late winter CO2 efflux from soils near the Arctic treeline in northwest Alaska.” Biogeochemistry 99 (2010): 65–77. Thomas, D. N., et al. The Biology of Polar Regions, 2nd ed. Oxford, U.K.: Oxford University Press, 2008.

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W Wallace,  alfred  russel (1823–1913) British Evolutionary biologist alfred Russel Wallace (see photograph on page 543) is famous principally as the codiscoverer, along with charles Darwin, of natural selection as the principal mechanism of evolution. However, he was famous also for his travel writings, his contributions to the study of what is now called biodiversity, and his social activism. He was perhaps the most famous British naturalist of the late 19th century. Born January 8, 1823, Wallace came from an intellectually active and sometimes fi nancially challenged family. He worked with his brother as a surveyor, and then taught surveying skills at a small British college. He found increasingly more time for the study of local natural history (insects, plants, geology), especially after he began a friendship with another young naturalist, Henry Walter Bates. Wallace and Bates decided to travel to South america to collect plant and animal specimens. Since neither was rich, they planned to sell the specimens to pay for the expedition. they went separate ways in South america. Both amassed large collections. Bates remained many years, studying the butterfl ies that were the fi rst and still most famous example of mimicry, a type still called Batesian mimicry. Wallace spent four years in South america and traveled farther in some of the river systems of South america than any european had ever gone. His studies in the amazon basin formed the basis of his developing thoughts about biogeography and about the process of evolution. He lived among, and closely studied, the ways and languages of the native peoples. in so doing, he developed an appreciation that tribal peoples have an intellectual capacity equal to that of civilized peoples, a belief that few european intel-

lectuals held at that time. as he returned to england with his collections, the ship caught fi re, and he lost everything except some of his drawings and notes. Upon returning home, he published and spoke about some of his observations to scientific societies and the general public. Wallace’s accomplishments as a naturalist were not yet famous but were sufficient for him to obtain support from the Royal Geographic Society for a journey to indonesia and new Guinea (at that time called the Malay archipelago). He spent nearly eight years there, from 1854 to 1862. He traveled 14,000 miles (22,530.8 km) and collected 125,660 biological specimens (including more than 1,000 species new to science). the book that he wrote upon his return, The Malay Archipelago, ranks as one of the most popular pieces of travel writing from the 19th century, partly because he published some of the earliest information about birds of paradise, orangutans, and the native peoples of new Guinea. the book is still in print. Wallace’s work in indonesia would have been sufficient to guarantee him lifelong fame as a naturalist; he certainly had a lifetime of work awaiting him upon his return just to analyze and write about his specimens and travels. But it was an event that occurred at the midpoint of his journey, in 1858, that changed the course of scientific history. He had contracted malaria and was lying ill with it when his fevered mind came up with an explanation for how the process of evolution could work, a process that we today call natural selection. When he was well enough, he wrote his ideas in an article entitled “On the tendency of Varieties to Depart indefinitely from the Original type.” it was the word indefi nitely (meaning “without limit”) that made 542

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Wallace, Alfred Russel 543 Wallace’s proposal distinct from orthodox scientific views. Wallace was ready to send the article back to England for publication. He knew, but did not much care, that his views might be controversial. However, he decided to let another, more experienced, scientist review his article before publication. He sent his article to Charles Darwin. Wallace could not have known what an effect his article would have. Like Wallace, Darwin had traveled extensively in tropical regions of the world and had spent much time (while ill) thinking about evolution. Like Wallace, Darwin had come up with natural selection as a way of explaining how evolution could occur. However, Darwin had done all of this almost exactly 20 years earlier. Darwin had not published any of his hypotheses on evolution, however, because he knew they would be controversial, and he wanted to amass all available evidence into a huge book that would answer every possible objection and settle the question. Therefore, Darwin delayed 20 years, while Wallace was ready to publish right away. Darwin was astounded that, after this long delay, another scientist had come up with the same ideas, even using the same term to describe the process. Darwin said, “I never saw a more striking coincidence. If Wallace had my manuscript sketch written out in 1842, he could not have made a better short abstract.” In consultation with the famous geologist Sir Charles Lyell, Darwin decided that his 1842 summary of natural selection should be presented and published jointly with Wallace’s article. Darwin was ill, so Lyell presented the joint Darwin-Wallace paper to the Linnaean Society in 1858. Strangely, the scientists in attendance took little notice of the paper, nor did the president of the Linnaean Society, who summarized the events of 1858 as unremarkable. Wallace, still in Indonesia, knew nothing of this. While in Indonesia, Wallace noticed that the animals on the island of Lombok differed strikingly from the animals of Bali, and those of Borneo differed from those of Sulawesi. The mammals of Lombok and Borneo included many marsupials and few large predators, while the animals of Bali and Sulawesi were mostly placental mammals and included large predators, such as tigers. He noticed a difference also in the birds. In some cases, the islands with different animals were almost within sight of one another. The line he drew on the map to separate the two faunas is now known as Wallace’s line, and that part of Indonesia is frequently called Wallacea. Wallace interpreted this, correctly, as resulting from the separate evolution of the two groups of animals. He could not have known that a deep ocean trench separated the two groups, which

xviii+598_Biodiversity_F.indd 543

Alfred Russel Wallace in old age  (The Linnean Society)

were on different continental plates and therefore had little contact throughout geological history. Wallace’s line is considered one of the earliest major contributions to the science of biogeography. After returning to England in 1862, Wallace spent three years organizing his specimens, presenting papers to scientific meetings, and writing. He earned money from his famously interesting public presentations; one speaking tour took him as far as California. His striking appearance (he was tall, had a long beard, and snow-white hair for the last 40 years of his life) contributed to his public success. He married a woman almost 20 years younger than he but who shared his passion for gardening and natural history. Later, they journeyed overseas on botanizing expeditions. Although his collections and writings proved profitable, his investments did not. He had to take on small editing and speaking assignments for pay and move his family progressively farther from London to find cheaper accommodations. Eventually, Darwin intervened to convince the British government to give Wallace an annual stipend in recognition of his services to science. Wallace continued his studies of evolution and advanced into other areas of science. His paper,

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544 Wallace, Alfred Russel 544 “The Origin of Human Races and the Antiquity of Man Deduced from the Theory of Natural Selection,” presented in 1864, preceded Darwin’s book The Descent of Man by seven years. Wallace published a paper in 1863 that gave an evolutionary explanation for the hexagonal construction of the cells in beehives, a topic Darwin incorporated into later editions of the Origin of Species. Wallace also published a theory of glaciation and evolutionary explanations of mimicry, protective coloration and color vision in animals, bird migration, and the necessity of aging. He was one of the first to present evidence that the Pleistocene extinction may have been caused by overhunting by humans. His writings were among the earliest that contrasted different kinds of life history in animals. His ideas about the evolution of reproductive isolation have even been called the Wallace Effect. He wrote in 1907 that the ice caps of Mars were carbon dioxide (dry ice), not water. Wallace also expanded his studies into many different areas throughout the remainder of his life. He began to give serious time and attention to social issues, in which he defended the causes of the working man and the oppressed. His views may be mainly attributed to his experiences with Amazonian, Indonesian, and Papuan peoples and to his exposure to socialism when he worked as a surveyor. Among the social issues he championed are: ●●

●●

●●

Land nationalization. Wallace called for the protection of rural lands and historical monuments, as well as the formation of greenbelts and parks, for the preservation of nature but also for the recreation of the lower and middle classes. Labor reform. Rather than calling for strikes, Wallace in 1899 called for working men to lay aside a portion of their salaries into a fund that would allow them to buy stock in the company and thereby partly or wholly control the company. He also called for double-overtime pay rates. Later in life he fully converted to socialism. Opposition to vaccination. This issue puzzles many modern scientists: Why would one of the most prominent scientists in Europe oppose vaccination? Wallace had both scientific and social reasons for it. Scientifically, he could demonstrate with epidemiological data that the incidence of contagious diseases began to decline before the introduction of vaccination. Today, scientists know that he was correct: Advances in public hygiene have proven at least as important as vaccination in improving pub-

xviii+598_Biodiversity_F.indd 544

first entry

●●

●●

●●

lic health. Socially, Wallace saw vaccination as the government’s way of trying to improve the lot of the poor without having to spend the money necessary for public sanitation. It was much cheaper and easier to jab poor people in the arm than to build sewers and provide safe drinking water. Women’s suffrage. He was one of the earliest proponents of voting rights for women in male intellectual society. Consumer safety. Wallace proposed in 1885 that all manufactured items have labels that identify their component materials and that the government regulate standards for these materials—practices that are standard in all industrialized countries today. Eugenics. Wallace criticized the attempt, then popular among scientists, including Darwin’s nephew Francis Galton, to attribute social problems to the supposed genetic inferiority of the lower classes and nonwhite races. Wallace saw this as an abuse of science and an attempt to justify oppression.

In the late 1860s, Wallace became an adherent of spiritualism, which he remained for the rest of his life. As a scientist, he sought experimental confirmation, but he was satisfied with demonstrations that more skeptical scientists would not accept. He wrote more than 100 publications on spiritualism. His lecture on life after death, delivered mainly during his California speaking tour, was one of his most popular. His outspoken association with spiritualism, however, did not prevent him from receiving a continuous stream of scientific awards and honors. Related to his belief in spiritualism was his acceptance of what is now called the anthropic principle, in which he believed that the universe was designed for man—a perfect universe in which humans were intended to evolve. The rebuttal written by Samuel Clemens (Mark Twain), “Was the World Made for Man?” has become much more famous than Wallace’s original writings on the subject. The publication of Wallace’s first article about natural selection jointly with Charles Darwin in 1858 created the impression that Darwin and Wallace believed the same things about evolution. Wallace’s publications about evolution were to prove that this was not the case, at least with human evolution. Wallace distinguished between the material process of natural selection that produced the human body and a spiritual one that produced the human mind, a distinction Darwin never made. Today, nearly all evolutionary scientists explain the origin of human behavior patterns in terms of evolutionary processes acting upon the brain. Many scholars assume that

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Wilson, Edward O. 545 Wallace’s rejection of natural selection as an explanation for the origin of the human mind resulted from his irrational attraction to spiritualism. However, evolutionary biologist Stephen Jay Gould and others have pointed out a different possibility. Both Darwin and Wallace were aware that tribal peoples had intelligence equal to that of civilized peoples: Darwin knew this from his experience with the Fuegians, and Wallace from the Amazonians and Indonesians. But Wallace pointed out, further, that the tribal peoples did not need or use the high levels of intelligence of which they proved themselves capable when given European education. Wallace reasoned that if natural selection were the sole explanation of the origin of the human mind, then scientists would see tribal peoples with low intelligence. Why did these people have so much more intelligence than they used? (This argument is now rejected by anthropologists, who recognize that tribal peoples have very complex languages, customs, and oral traditions.) Wallace, in other words, was taking natural selection more seriously, not less seriously, than Darwin. Of course, Wallace’s acceptance of spiritualism made his rejection of the evolution of mind much easier. Wallace remained intellectually active well into his old age. Between 1898 and 1910, mostly in his ninth decade, he published more than 4,000 pages of material. Wallace died November 7, 1913. See also Bates, Henry Walter; biodiversity, concept of; biogeography; camouflage and mimicry; Darwin, Charles; natural selection; Pleistocene extinction. Further Reading Brackman, Arnold C. A Delicate Arrangement: The Strange Case of Charles Darwin and Alfred Russel Wallace. New York: Times Books, 1980. Camerini, Jane, ed. The Alfred Russel Wallace Reader: A Selection of Writings from the Field. Baltimore, Md.: Johns Hopkins University Press, 2001. Fichman, Martin. An Elusive Victorian: The Evolution of Alfred Russel Wallace. Chicago: University of Chicago Press, 2004. Raby, Peter. Alfred Russel Wallace: A Life. Princeton, N.J.: Princeton University Press, 2002. Smith, Charles H. “The Alfred Russel Wallace Page.” Available online. URL: http://www.wku.edu/~smithch/ index1.htm. Accessed August 4, 2010. Wallace, Alfred Russel. The Malay Archipelago. Oxford, U.K.: John Beaufoy Publishing, 2009.

Wilson, Edward O.  (1929–  )  American  Evolutionary biologist Edward Osborne Wilson has been at the leading edge of breakthroughs in evo-

xviii+598_Biodiversity_F.indd 545

lutionary science, entomology, biogeography, and the study of the diversity of species. He even helped to invent some of the terms that are now central to these subjects, such as biodiversity, biophilia, island biogeography, and sociobiology. He has also been an immensely popular writer on these subjects: On Human Nature and The Ants (with entomologist Bert Hölldobler) have won Pulitzer Prizes, and The Diversity of Life and The Future of Life have been immensely popular books about biodiversity. In 2010 he published a novel, Anthill, that explores similarities between human and ant societies in an environmental context. Born June 10, 1929, in Birmingham, Alabama, Wilson grew up primarily in Alabama and Florida. At a young age he became fascinated with the natural world, and as a Boy Scout he spent a lot of time exploring the marshes and swamps, collecting insects. He became an amateur expert on things that most people did not see even if they looked straight at them. It was Wilson who, at about 12 years of age, was the first to report the presence of the red imported fire ant, which is now a major problem, in the United States. His youthful passion for understanding the diversity of the natural world was the force that impelled his entire subsequent career. He earned bachelor’s and master’s degrees at the University of Alabama and worked as an entomologist for the Alabama Department of Conservation, primarily studying the fire ants whose invasion he had discovered. It was at the university that he learned about evolutionary science, and from that point onward he questioned the religious foundations he had embraced as a youth. He completed his Ph.D. at Harvard University in 1955. He was invited to join the Harvard faculty in 1956, and he is still there, as Pellegrino University professor emeritus. He works as honorary curator in entomology at the Museum of Comparative Zoology. Receipt of a Harvard fellowship allowed him to travel soon after he began his faculty appointment in 1956. He studied ants in New Guinea and other Pacific Islands. He was the first outsider to climb Mt. Boana, the crest of the central Sarawaget Mountains of New Guinea. He also traveled in the American tropics. He collected lots of ants, always with the goal of understanding the evolutionary history of the entire ant family Formicidae. Wilson’s observations also made him think about how species diversity developed on islands. Curious as always, when he returned to Harvard, he sat in on mathematics classes, recognizing that he needed to know more math if he was to develop general theories of population biology. He shared his understanding with the world in A Primer of Population Biology (with geneticist William H. Bossert),

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546 Wilson, Edward O. 546 which is still one of the fundamental texts on the subject. With Robert H. MacArthur, an ecologist at Princeton University, Wilson developed the theory of island biogeography, which tied species immigration and extinction to the area of islands and their distance from the mainland. But is it possible to study island biogeography experimentally? In the late 1960s Wilson, with ecologist Daniel Simberloff, removed all of the animals from mangrove islands of various sizes and distances from the mainland in the Florida Keys—a difficult task, especially when a hurricane is coming—and then documented the colonization of these islands by animals. His work transformed the study of island species from stories to a science and made island biogeography theory useful to conservation efforts. Wilson’s studies of ants created breakthroughs of understanding in how insects communicate. He and collaborators worked out the principles of how insects communicate by chemicals. Subsequently, many researchers have found examples of chemical communication among vertebrates and even among plants. Wherever he traveled, at home or abroad, he could not help but notice that human activity was destroying natural habitats and, in the process, replacing high-diversity ecological communities with low-diversity artificial habitats. He could see, before most scientists had thought about it, that species were being driven into extinction faster than anyone could even recognize them let alone study them. He knew that there was yet a lot to be learned from wild species of ants. For example, ants have high population densities yet they hardly ever experience epidemic diseases. This is because their metapleural glands and some symbiotic bacteria produce chemicals that kill bacteria. Humanity needs new antibiotics, yet humans are driving many ant species into extinction. Wilson’s 1984 Biophilia argued that humans have a psychological need for contact with the natural world. In The Diversity of Life and The Future of Life, Wilson explained the causes and consequences of the sixth mass extinction, which humans are bringing upon the world, and what humans might be able to do to slow or stop it. Not content with writing, Wilson has been active with the American Museum of Natural History, Conservation International, the Nature Conservancy, and the World Wildlife Fund. The destruction of biodiversity, he writes, “is the folly our descendants are least likely to forgive us.” Wilson was largely responsible for synthesizing the modern understanding of insect behavior in his 1971 book, The Insect Societies. He applied these concepts across the entire animal kingdom

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first entry in his 1975 book, Sociobiology: The New Synthesis. There was only a little bit, the last chapter, about humans, but it sparked a vigorous controversy about the role of evolutionary biology in human behavior and created a field of study now sometimes called evolutionary psychology. Wilson did not hesitate to make his message clear to the general public in his 1979 book, On Human Nature. Strong disagreement came from other scientists, including Harvard colleagues Stephen Jay Gould and Richard Lewontin. Outside the academic world, many activists believed that sociobiology provided an intellectual justification for oppression. At a 1978 meeting of the American Association for the Advancement of Science in Washington, D.C., Wilson was one of the platform scientists at a discussion of human evolution. Protesters chanted, “Racist Wilson you can’t hide, we charge you with genocide!” A protester jumped up on stage with a pitcher of water and poured it all over Wilson, saying, “Wilson, you are all wet!” Evolutionary anthropologist Napoleon Chagnon helped push the protester off the stage, while Stephen Jay Gould took the microphone to denounce the protesters’ tactics. Meanwhile, Wilson just wiped off the water and continued with the meeting. No one who has met Wilson can believe that he in any way condones the misuse of sociobiology as a rationalization for political oppression. If anyone could handle the challenge of trying to bring together all fields of knowledge into a single unified structure, it would be Edward Wilson. His 1998 Consilience called for a return to original Enlightenment ideals for bridging the sciences and the humanities. College education is a smorgasbord of largely disconnected subjects that leaves undergraduates more annoyed than enlightened; the typical divisions of a newspaper (news, business, sports, leisure) are even more disconnected. Rather than to have science as just one area of study— equal perhaps to music, or as an occasional page in a newspaper—Wilson wants science, particularly evolutionary science, to be understood as the foundation of all human history and activity. Naturally this approach has drawn attacks from scholars in the humanities who do not want their field to be seen as a subset of science. Wilson writes, “My truths, three in number, are the following: first, humanity is ultimately the product of biological evolution; second, the diversity of life is the cradle and greatest natural heritage of the human species; and third, philosophy and religion make little sense without taking into account these first two conceptions.” Although Wilson admits his approach to consilience may be wrong, it is widely recognized as one of the most concise and organized attempts ever made.

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Wilson, Edward O. 547 Wilson has received many of the highest awards that are available. There is no Nobel Prize for evolutionary biology, but Wilson has received the Crafoord Prize, the award given by the Royal Swedish Academy of Sciences for areas not covered by the Nobel Prize, as well as the U.S. National Medal of Science. In addition to his two Pulitzer Prizes, Wilson has received prestigious prizes in Japan, France, Italy, and Saudi Arabia and from world conservation organizations. As much as he cherishes these prizes, he is still very grateful for the teaching awards he has received from the students of Harvard University. Even though most people his age have decided to take it easy, Wilson still has major projects. His primary goal is to work on the “Encyclopedia of Life,” a project he helped launch, which will use modern Internet technology to speed up the process of documenting the Earth’s rapidly disappearing biodiversity. His motto might be reflected in this quote: “Love the organisms for themselves first, then strain for general explanations, and, with good fortune, discoveries will follow. If they don’t, the love and the pleasure will have been enough.” Even though he is one of the most respected scientists of modern times, he will not hesitate to crouch down on the ground to look at an ant. He is still, at heart, a Boy Scout working on an insect merit badge. See also biodiversity, concept of; invasive species; island biogeography.

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Further Reading Cowley, Geoffrey. “Wilson’s world.” Newsweek, June 22, 1998, 58–62. MacArthur, Robert H., and Edward O. Wilson. Theory of Island Biogeography. Princeton, N.J.: Princeton University Press, 1967. Wilson, Edward O. Anthill: A Novel. New York: Norton, 2010. ———. Biophilia. Cambridge, Mass.: Harvard University Press, 1984. ———. Consilience: The Unity of Knowledge. New York: Vintage Press, 1998. ———. The Creation: An Appeal to Save Life on Earth. New York: Norton, 2006. ———. The Diversity of Life. Cambridge, Mass.: Harvard University Press, 1992. ———. “The encyclopedia of life.” Trends in Ecology and Evolution 18 (2003): 77–80. ———. The Future of Life. New York: Vintage Press, 2002. ———. Naturalist. Washington, D.C.: Island Press, 1994. ———. Nature Revealed: Selected Writings, 1949–2006. Baltimore, Md.: Johns Hopkins University Press, 2006. ———. On Human Nature. Cambridge, Mass.: Harvard University Press, 1978. ———. Sociobiology: The New Synthesis. Cambridge, Mass.: Harvard University Press, 1975. ———, and William H. Bossert. A Primer of Population Biology. Sunderland, Mass.: Sinauer Associates, 1971. ———, and Bert Hölldobler. The Ants. Cambridge, Mass.: Harvard University Press, 1990.

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Appendix I Chronology

ca. 350 B.C.E.

aristotle attempts to classify all animals

1859

charles Darwin publishes On the Origin of Species

ca. 250 B.C.E.

theophrastus describes about 500 species of plants in his 10-volume Historia Plantarum

1864

ernst Haeckel publishes two volumes of Generelle Morphologie der Organismen, in which he proposes a new kingdom, Protista; George Perkins Marsh publishes Man and Nature, one of the earliest books of environmentalism

1865

Gregor Mendel investigates inheritance patterns in peas

1866

Haeckel introduces the term ecology

1872

Sir c. Wyville thomson begins the Challenger expedition, during which thousands of new marine organisms are discovered; yellowstone becomes the fi rst United States national Park; fi rst tree-Planting Day (now arbor Day)

ca. 50

Pliny the elder publishes 37-volume Historia Naturalis

1682

John Ray defi nes the concept of a species and describes monocots and dicots in Methodus Plantarum Novae

1736

carolus linnaeus publishes the fi rst of 12 editions of Systema Naturae, a book that outlined a system for classification of plants, animals, and minerals

1749

Georges-louis leclerc, comte de Buffon, publishes fi rst volume of Histoire Naturelle, the series in which he states that species are mutable

1875

carl linnaeus publishes Species Plantarum, introducing bionomial nomenclature

congress prohibits unauthorized cutting of trees on federal government property

1878

thomas Malthus publishes Essay on the Principle of Population, which later stimulates the theory of natural selection by charles Darwin and alfred Russel Wallace

John Wesley Powell publishes Report on the Lands of the Arid Regions of the United States, which calls for environmentally responsible development of western lands

1891

1799

alexander von Humboldt begins scientific exploration of latin america

establishment of fi rst Forest Reserve (later called national Forests)

1892

1802

Jean-Baptiste lamarck presents a theory of evolution based on the inheritance of modified traits

John Muir founds the Sierra club, devoted to wilderness preservation

1898

1831

charles Darwin begins a scientific journey around the world on HMS Beagle

Gifford Pinchot becomes chief of the Division of Forestry of the U.S. Department of agriculture and begins modern conservation-based forest management

1848

Henry Walter Bates and alfred Russel Wallace begin an insect-collecting expedition through amazonia, discovering astonishing levels of biodiversity

1903

President theodore Roosevelt establishes the fi rst federal wildlife refuge at Pelican island, Florida

1914

Death of the last passenger pigeon

1916

national Park Service created

1753

1798

548

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Chronology 549

1935 Arthur Tansley introduces the ecosystem concept; due to efforts of Hugh Hammond Bennett, the U.S. Soil Conservation Service is established



1936 Death in Australian zoo of the last thylacine (Tasmanian tiger)



1949 Aldo Leopold’s Sand County Almanac proposes the land ethic



1951 The Nature Conservancy is established to promote ecological preservation of private lands



1959 G. Evelyn Hutchinson publishes “Santa Rosalia” article that focuses attention on processes that determine biodiversity



1962 Rachel Carson publishes Silent Spring



1964 Wilderness Act designates millions of acres of wilderness area in United States



1970 First Earth Day; National Environmental Policy Act (NEPA) establishes the Environmental Protection Agency; Clean Air Act



1972 Clean Water Act; pesticide DDT banned



1973 Endangered Species Act



1977 Robert Ballard and his team discover ecological communities based on

xviii+598_Biodiversity_F.indd 549

bacterial chemosynthesis surrounding hydrothermal vents; Carl Woese proposes a third domain of life, Archaea

1988 James Hansen brings evidence of the greenhouse effect to the attention of U.S. Congress



1992 UN Convention on Biological Diversity and UN Framework Convention on Climate Change are adopted in Rio de Janeiro, Brazil, at the UN Earth Summit meeting



1994 Discovery of newest animal phylum, Cycliophora



1997 Kyoto Protocol adopted as first step in implementation of the UN Framework Convention on Climate Change



2009 United Nations Climate Change Conference in Copenhagen negotiated targets for carbon emission reductions to succeed the Kyoto Protocol



2010 Nagoya Protocol adopted, updating the UN Convention on Biological Diversity



2010 Deepwater Horizon oil spill (BP) in Gulf of Mexico, largest oil spill to date



2011 Major earthquake in Japan causes meltdown of nuclear plants and release of radiation

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Appendix II Glossary

biogeochemical  cycles  movement of atoms or

acclimatization  physiological adjustments by an

molecules (e.g., water, carbon, nitrogen, minerals) from the physical environment, through a food web, and back into the physical environment biogeography  the patterns of which kinds of organisms live in which locations biomagnifi cation  the concentration of toxic minerals persistent organic pollutants (POPs) at higher trophic levels biomimicry  the conscious imitation of biological adaptations by human technology biophilia  human innate psychological love of nature and biodiversity bioremediation  use of organisms (primarily plants) to remove toxic compounds from natural environments, usually soil birds  terrestrial two-legged vertebrates with feathers bog  a wetland with acidic water that is low in nutrients boreal  forest  a coniferous forest that grows in high latitude regions, in which summers are too short to allow the production of a new set of leaves every year camoufl age  adaptations that make animals difficult for their predators or their prey to see carnivore  organism (usually an animal) that obtains food by eating animals chaparral  dry shrubland maintained by a fire cycle character displacement  process by which competition between two species causes lower fitness of individuals of at least one of the species that are most similar to the individuals of the other chordate  animal that has a notochord along its back, associated with the main nerve bundle, at least during its embryonic development cladistics  classification of species of organisms based on the pattern of evolutionary branches that produced them class  (taxonomic)  in traditional classification, the level into which phyla or divisions may be divided. each class consists of one or more orders. cloud forests  forests of short trees with abundant epiphytes that live in misty mountains

individual organism that enhance its survival and reproduction adaptation  a characteristic of organisms in a population that allows the organisms to have greater survival and reproduction, produced by natural selection acting upon that characteristic adaptive  radiation  evolution of diverse species from a common ancestor agriculture  deliberate cultivation of fungi or plants by animals allelopathy  production by plants of toxins that inhibit the growth of other plants allometry  differences between organisms due to their different sizes, which are necessary to allow structural support or the exchange of matter and energy with the physical environment amniotes  vertebrates that produce eggs with shells that potentially resist desiccation. Reptiles, birds, and mammals are amniotes. amphibian  a vertebrate that usually has an aquatic juvenile phase and a terrestrial adult phase angiosperm  a seed plant that produces flowers and fruits animal  a multicellular eukaryote that ingests chunks of food archaea  prokaryotes with unique cellular characteristics and that are usually extremophiles arthropod  an animal with an exoskeleton and jointed legs autecology  ecology of organisms responding to their physical environments avoidance  a method of acclimatization, plasticity, or adaptation that allows organisms to maintain their physiological processes by producing internal conditions that are more favorable to their function than are the external conditions bacteria  prokaryotes with unique cellular characteristics and that are usually not extremophiles benthic  dwelling at the bottom of a body of water biodiversity  the total genetic and species diversity of organisms biodiversity  hotspot  a small area with an unusually high number of species, many of them endemic 550

xviii+598_Biodiversity_F.indd 550

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Glossary 551 coevolution  evolution of two or more species in

disturbance, ecological  damage to or destruction

response to one another commensalism  a symbiotic relationship between two species in which the commensal species benefits and the host species is unaffected community, ecological  all of the species in a given location and all of their interactions competition, ecological  interactions among two or more species that depend on a single resource, which is not abundant enough for all of them conifer  a seed plant that produces pollen in male cones and seeds in female cones coniferous forest  a forest dominated by coniferous trees, such as boreal and subalpine forests, or the forests of the relatively dry mountain regions of western North America conservation  human activities intended to protect wild species and their habitats, while allowing human access and limited use consumers  organisms that obtain their food from other organisms, living or dead, in contrast with producers, which use photosynthesis to produce their food continental shelf  edge of a continent that is below sea level convergence  evolution of similar adaptations by different lineages of organisms coral bleaching  loss of symbiotic photosynthetic organisms from corals, as a result of adverse environmental conditions, which causes the corals to starve crustacean  an arthropod that usually has numerous legs and numerous visible body segments deciduous forest  a forest dominated by trees that lose their leaves every autumn and grow a new set of leaves every spring decomposition  consumption of dead organisms, or the organic molecules released by other decomposers, usually by microorganisms deserts  ecological communities with low rainfall and long rainless periods deuterostomes  animals with radial cleavage during embryonic development; includes chordates dicot  an angiosperm whose seeds have embryos with two leaves dinosaurs  reptiles that were the dominant vertebrates during much of the Mesozoic period and whose modern descendants are birds disjunct  a species geographically distant from closely related species, or a population separated from other populations of the same species by a distance that is sufficient to prevent interbreeding dispersal  (1) movement of offspring away from the parent; (2) movement of organisms that results in a new population in a distant location

of the dominant plants in an ecological community, which may allow resources to become available to surviving plants, or which may be severe enough to destroy an ecological community DNA  the molecule that stores genetic information in the cells of an organism. DNA can also be analyzed, allowing the identification of the species, and can mutate, producing genetic diversity upon which evolution can act. domain (taxonomic)  in traditional classification, the highest category, which contains one or more kingdoms. The eukaryotic domain contains protist, fungus, plant, and animal kingdoms. ecological footprint  the area of productive land that would be necessary to produce the resources that a person, or a nation, consumes ecology  interactions of organisms with their physical or biological environments ecotone  the zone in which one ecological community intergrades into another ecosystem  an ecological community, together with the matter and energy with which it interacts ecosystem services  ecological processes that happen to benefit the survival and prosperity of human societies ectotherm  an animal that absorbs most of its body heat from its environment edaphic factors  physical and chemical factors related to the surface (e.g., soil or rocks) upon which plants grow and animals live endemic species  a species that lives only in one limited area endotherm  an animal that generates most of its body heat by internal physiological processes energy pyramid  loss of stored energy as the energy is transferred from one trophic level to the next ephemeral organisms  organisms that are dormant most of the time and flourish during briefly favorable periods epigenetics  patterns of inheritance of characteristics from one generation to another that result from some genes being inactivated era  a duration of geological time that ends with a major extinction event. Each geological era consists of several geological periods. estuary  a marine brackish or salt marsh, often at the mouth of a river, in which many marine animal species breed eukaryote  an organism whose cells contain nuclei, usually contain mitochondria, and may contain chloroplasts eutrophication  an explosive growth of photosynthetic bacteria as a result of phosphate pollution evolution  genetic changes over time in populations

xviii+598_Biodiversity_F.indd 551

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552 Glossary 552 exaptation  a characteristic of organisms in a pop-

ulation that allows the organisms to have greater reproduction, produced by natural selection that acts upon a different characteristic exoskeleton  a hard outer covering of an animal, usually an arthropod, that provides the principal support for its body weight extinction  death of the last member of a species extremophile  an organism that lives in very hot, very salty, or very acidic conditions, or under conditions of high pressure or radiation. Most extremophiles are archaea. family (taxonomic)  in traditional classification, the level into which orders may be divided. Each family consists of one or more genera. feedback  the effect of one process upon another. Positive feedback occurs when one process makes another process occur more rapidly; negative feedback, when it makes it occur more slowly. fishes  aquatic vertebrates without legs fitness, evolutionary  the successful production of offspring food chain  a series of organisms, usually in which herbivores eat plants and carnivores eat herbivores, and all of the organisms, upon death, are metabolized by decomposers food web  a complex set of food chains, in which each organism eats and/or is eaten by organisms of more than one species fossilization  partial or complete transformation of an organism, or something produced by that organism (e.g., a footprint), into mineral form founder effect  a genetic pattern in a population that results from the genetic characteristics of the individuals that started the population fungi  multicellular eukaryotes that digest cells in their environment and absorb the digested molecules Gaia  an image for understanding the entire Earth as a living ecosystem whose physical characteristics are modified by its organisms genetically modified organisms (GMO)  organisms, primarily bacteria, crop plants, and livestock animals, whose genes have been modified by laboratory techniques genetic bottleneck  loss of genetic diversity in a population as a result of a reduction in population size genetic drift  genetic changes that occur by chance, rather than by selection, in small populations genetics  patterns of inheritance of characteristics from one generation to another that result from different alleles (versions) of genes genus (pl. genera)  in traditional classification, the level into which families may be divided. Each genus consists of one or more species.

xviii+598_Biodiversity_F.indd 552

first entry grassland  an ecological community in which

grasses make up most of the biomass, even if other kinds of plants constitute most of the species greenhouse effect  global warming that results from the accumulation of greenhouse gases (e.g., carbon dioxide) in the atmosphere gymnosperm  a seed plant that produces seeds that are not enclosed in a fruit habitat  a local ecological community in which an organism lives habitat fragmentation  division of a habitat into small portions by barriers (e.g., roads) that many organisms cannot readily cross Hardy-Weinberg equilibrium  the pattern of alleles (versions of genes) that occurs in populations when selection, genetic drift, nonrandom mating, mutation, immigration, and emigration are not occurring herbivore  an animal that subsists primarily by eating plant material homeotherm  an organism that maintains a relatively constant body temperature humus  organic matter in the soil that results primarily from the decomposition of dead plant parts hybridization  the process by which individuals of (usually) two different species produce offspring by sexual reproduction hydrostatic skeleton  structural support for an animal that results from sacs of fluid in which muscles can produce pressure hydrothermal vents  deep-ocean volcanic eruptions that release molecules such as hydrogen sulfide, which bacteria can metabolize and upon which a food web can be based ice age  a period of glaciation, in which the accumulation of snow produces glaciers that cover large areas. Glaciation alternates with glacial melting. inbreeding  production of offspring by sexual reproduction occurring between close genetic relatives. The offspring often reveal otherwise hidden genetic mutations. insect  an arthropod with six legs and three body parts; insects are the most diverse group of animals on Earth integrated pest management (IPM)  control of agricultural pests primarily by natural means, with a limited amount of pesticide invasive species  species that enter a new habitat and undergo explosive population growth invertebrate  an animal without an internal skeleton or backbone island biogeography  the pattern by which new species arrive at or evolve on a geographical or ecological island, and by which they become extinct, as a result of the size of the island and

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Glossary 553 its distance from the mainland or from larger populations isolating mechanism  a biological process that prevents two populations or two species from interbreeding, even if they are in close proximity keystone species  a species that significantly affects the survival of many other species in an ecological community and whose extinction would greatly alter the community lichen  an organism that is a symbiotic combination of single photosynthetic cells and strands of fungus life history  the pattern of growth, reproduction, and longevity of an organism mammal  a vertebrate with hair in which the females can produce milk marsh  a wetland dominated by herbaceous plants, primarily grasses and sedges marsupial mammal  a mammal in which very young embryos are born and which must crawl into a pouch to find a nipple meiosis  sexual cell division that separates pairs of chromosomes from one another and reduces the number of chromosomes by half mesophication  the process by which secondary succession, in the absence of fire, produces a forest that is dominated by species of trees that require wetter (more mesic) conditions metamorphosis  the development of an animal larva into a very different adult form, usually during a period of pupation microhabitat  a small area within a larger habitat, within which individuals of a species spend most of their time mimicry  characteristics of an organism that imitate some aspect of its environment (e.g., a different species of organism) in such a way that it is protected from danger or otherwise gains a reproductive advantage monocot  an angiosperm whose seeds have embryos with one leaf monoculture  an ecological community (usually an agricultural one) that consists almost entirely of a single dominant species or even a single dominant breed monophyletic  a cladistic category of organisms, all of which trace their ancestry to a single ancestral population monotreme mammal  a mammal whose females lay eggs but feed their young with milk mutualism  a symbiotic relationship between two species in which both species benefit mycorrhizae  fungi that live within plant roots and absorb minerals from the soil, thus supplementing the mineral supply available to the plant natural selection  the process by which some individuals in a population reproduce more than oth-

xviii+598_Biodiversity_F.indd 553

ers as a result of their genetic characteristics, in response to the physical environment or to other species natural systems agriculture  a system of agriculture that imitates natural ecosystems, particularly with respect to soil conservation, soil minerals, and pest control niche  the set of conditions in which an individual, population, or species survives and reproduces best nitrogen fixation  bacterial transformation of gaseous nitrogen into ammonia omnivore  an animal that eats food from both plant and animal sources order (taxonomic)  in traditional classification, the level into which classes may be divided. Each order consists of one or more families organic agriculture  agriculture that avoids the use of industrially produced chemicals paraphyletic  a cladistic category of organisms, some but not all of which trace their ancestry to a single ancestral population parasitism  a symbiotic relationship between two species in which the parasite species benefits but the host species is harmed pelagic  dwelling in deep ocean waters period  a duration of geological time that ends with a minor extinction event. Each geological era consists of several geological periods. permafrost  permanently frozen soil in the tundra persistent organic pollutants (POPs)  organic molecules, usually of industrial origin, that do not readily decompose but remain in the environment for long periods photosynthesis  the process by which some bacteria, or the chloroplasts of some eukaryotes, transfer sunlight energy into the production of sugar molecules; the basis of most food webs phylum (taxonomic)  in traditional classification, the level into which domains may be divided. Each phylum consists of one or more classes. This level is called “division” in plants, fungi, protists, and prokaryotes. placental mammal  a mammal in which the fetus remains inside the body of the mother for a prolonged period and is fed by the mother through a placenta plankton  floating (usually aquatic) organisms plasticity, phenotypic  development of different characteristics in response to different environmental conditions by organisms with the same types of genes poikilotherm  an animal whose body temperature fluctuates with environmental temperature pollination  transfer of pollen from the flower or cone of one seed plant to the flower or cone of another seed plant, usually of the same species

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554 Glossary 554 polyculture  an ecological community (usually an

agricultural one) that consists of more than one dominant species polymorphism  differences within a population of individual characteristics, resulting from differences in alleles (versions of genes) polyphyletic  a cladistic category of organisms that trace their ancestry to more than one ancestral population population  all the organisms of a species that are in close enough proximity to one another to customarily interbreed predator  an organism (usually an animal) that eats other organisms (such as seeds or prey) primates  an order of placental mammals with acute vision and opposable thumbs, which includes monkeys and apes (such as humans) producers  organisms that produce their food by photosynthesis productivity  the total amount of photosynthetic production of organic molecules in an ecological community (gross primary productivity), or the amount that remains after cellular respiration (net primary productivity), or the production of organic molecules at any trophic level prokaryotes  cells (usually very small) whose DNA is not contained within a nucleus protists  organisms that consist of a single eukaryotic cell or of eukaryotic cells that are not organized into tissues protostomes  animals with spiral cleavage during embryonic development rain forest  a forest that receives a great deal of rain, usually uniformly throughout the year rain shadow  interception of atmospheric moisture on the windward side of a mountain range, resulting in reduced rainfall on the leeward side reef  a large mineral deposit that results from secretion of minerals (mostly calcium carbonate) by aquatic organisms relictual population  a small isolated population that was once part of a larger, widespread population reptile  an amniote other than a bird or mammal respiration, cellular  the process by which cells (or mitochondria within cells) release metabolic energy from sugar resurgence  rapid growth of a pest population after the pesticide that was used to control it is no longer in active circulation within the ecosystem root nodules  root structures, primarily in leguminous plants and alders, within which bacteria carry out nitrogen fixation salinization  buildup of salt in soil, usually agricultural soil, as a result of evaporation of water (usually irrigation water) that contains salt

xviii+598_Biodiversity_F.indd 554

first entry savanna  a grassland with scattered trees seed  a reproductive structure in which a plant

embryo, with a stored food supply, is surrounded by a protective coat sexual selection  the process by which some individuals in a population reproduce more than others as a result of their genetic characteristics and of success in gaining access to members of the opposite gender speciation  evolution of two or more species from a single ancestral population species  a set of naturally interbreeding populations spider  an arthropod with eight legs and two body parts, which usually obtains its food by injecting digestive enzymes into a prey animal and consuming the resulting molecules spores  single reproductive cells produced by meiosis in protists, fungi, and plants, or the resting phase of a bacterium that can resist adverse environmental conditions subalpine forest  a coniferous forest that grows at high elevations, in which summers are too short to allow the production of a new set of leaves every year succession, ecological  changes in ecological communities that result after disturbance, with some species replacing others as the dominant species succulents  plants that store water in their tissues swamp  a wetland dominated by woody species (e.g., mangroves) symbiogenesis  the origin of a new evolutionary lineage as the result of the symbiotic merger of different species, usually on the cellular level symbiosis  the interaction of two species in which the interaction is of overwhelming importance to the fitness of at least one of the species symmetry  the balance of an organism’s structure around one or more axes synecology  ecology of organisms responding to other organisms taxonomy  the classification of organisms on the basis of their adaptations and/or evolutionary history tetrapods  vertebrates with four limbs (legs and arms) timberline  the ecotone between tundra and forest tolerance  a method of acclimatization, plasticity, or adaptation that allows organisms to maintain their physiological processes despite adverse internal conditions transpiration  evaporation of water from leaves trophic cascade  effects of populations of a keystone species on other trophic levels in the ecological community trophic levels  levels of a food chain, such as producers, herbivores, and predators

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Glossary 555 tundra  an ecological community with long winters

vertebrate  an animal with an internal skeleton,

and permafrost and which consists of small plants vascular plant  a plant that can transport water through pipelike cells such as xylem

vicariance  divergence of the species in an ecologi-

xviii+598_Biodiversity_F.indd 555

including a backbone cal community as a result of adaptive radiation

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Appendix III

Further Resources

BooKs

derness areas cannot be kept intact by merely keeping people out of them. collinge, Sharon K. Ecology of Fragmented Landscapes. Baltimore, Md.: Johns Hopkins, 2009. this book explains how habitat fragmentation disturbs the ecosystems and biodiversity of protected areas. comin, Francisco a., ed. Ecological Restoration: A Global Challenge. new york: Oxford University Press, 2010. this book explains how natural areas need to not only be preserved but restored throughout the world and the challenges associated with doing this. cox, c. Barry, and Peter D. Moore. Biogeography: An Ecological and Evolutionary Approach. Hoboken, n.J.: John Wiley, 2010. this textbook presents an up-to-date overview of the science of biogeography. Darwin, charles. On the Origin of Species by Means of Natural Selection, 1st ed. london: John Murray, 1859. available online. URl: http://darwinonline.org.uk/content/frameset?itemiD=F373& viewtype=side&pageseq=1. accessed august 2, 2010. this is perhaps the most important scientific book ever written. it lays the foundation for not just evolution but for ecology as well. Six editions were published during Darwin’s lifetime, each one addressing criticisms of previous editions, criticisms that are now considered to be inaccurate, and Darwin’s responses to them bogged down the initial insight of his first edition. Golley, Frank Benjamin. A History of the Ecosystem Concept in Ecology: More than the Sum of the Parts. new Haven, conn.: yale University Press, 1993. this book reviews the development of the ecosystem concept from before its formal proposal by tansley in 1935 to modern times when the emergent properties of ecosystems are recognized. Hagen, Joel B. An Entangled Bank: The Origins of Ecosystem Ecology. new Brunswick, n.J.: Rutgers University Press, 1992. this book is a history of important ecological concepts and the lives of the scientists who developed them. the name

Barrow, Mark V., Jr. Nature’s Ghosts: Confronting Extinction from the Age of Jefferson to the Age of Ecology. University of chicago Press, 2009. this book reviews the changing concept of extinction, from the enlightenment era, when many scholars believed extinction was impossible, to a modern understanding of the role of extinction in evolution and conservation. Bazzaz, Fakhri a. Plants in Changing Environments: Linking Physiological, Population, and Community Ecology. new york: cambridge University Press, 1996. this book explains how plants respond to one another within populations and within ecological communities, in conditions that change over ecological time and as a result of human activity. Begon, Michael, colin R. townsend, and John l. Harper. Ecology: From Individuals to Ecosystems, 4th ed. Oxford, U.K.: Blackwell, 2006. this textbook is a thorough overview of all aspects of ecology. carson, Rachel. Silent Spring. new york: Houghton Mifflin, 1962/2002. this book, more than any other, started the modern ecological movement. it thoroughly documented the effects of pesticides on entire ecosystems, including what we today call biomagnification, and the evolution of pesticide resistance, whereby humans were polluting their environments in order to ineffectively control pests. yet it is so delightfully written that millions of nonscientists read it. chivian, eric, and aaron Bernstein, eds. Sustaining Life: How Human Health Depends on Biodiversity. new york: Oxford University Press, 2008. this book, richly illustrated, shows nearly every possible way in which the protection of biodiversity is essential to human health and nutrition. the authors are at the Harvard Medical School. cole, David n. Beyond Naturalness: Rethinking Park and Wilderness Stewardship in an Era of Rapid Change. Washington, D.c.: island Press, 2010. this book explains that national parks and wil556

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Further Resources 557 refers to the metaphor used in Darwin’s Origin of Species. Hubbell, Stephen P. The Unified Neutral Theory of Biodiversity and Biogeography. Princeton, N.J.: Princeton University Press, 2001. This book explains what ecological communities would look like if the processes usually used to explain them were not operating. Jackson, Wes. New Roots for Agriculture. Lincoln, Neb.: University of Nebraska Press, 1980. Wes Jackson, considered one of the most important thinkers of modern times, proposes a whole new agriculture based on biodiversity and perennial crops. A great deal of contemporary research is emerging from his initial insights. Leopold, Aldo. A Sand County Almanac: With Essays on Conservation from Round River. New York: Sierra Club/Ballantine Books, 1974. Originally published in 1949, after Leopold’s death, this set of essays presented some of the foundational concepts of modern environmental ethics. Louv, Richard. Last Child in the Woods: Saving Our Children from Nature Deficit Disorder. Chapel Hill, N.C.: Algonquin Books, 2008. In this book, Louv explains the numerous personal and social problems that result from kids not having the chance to play outside in natural environments and the challenges that communities face in trying to solve this problem. Lovelock, James. The Vanishing Face of Gaia: A Final Warning. New York: Basic Books, 2009. Lovelock is the original proponent of the Gaia hypothesis, and in this book, written late in his life, he explains that human activities may have pushed Earth beyond the ability of its internal regulatory systems to maintain its stability. It is not an upbeat message of hope. Mann, Charles C. 1491: New Revelations of the Americas before Columbus. New York: Vintage, 2006. Mann explains how Native Americans had transformed the landscape before European contact and how much of what modern Americans consider to be “natural” resulted from the decline of Native American populations. ———. 1493: Uncovering the New World Columbus Created. New York: Knopf, 2011. Mann explains how the exchange of organisms, including disease parasites, between America and the rest of the world altered the entire Earth ecosystem. Marcus, Bernard. Tropical Forests. Sudbury, Mass.: Jones and Bartlett, 2008. This book is an overview of tropical forests, which contain more biodiversity than any other kind of ecological community, and each of which differs from the others. McCarthy, Dennis. Here Be Dragons: How the Study of Animal and Plant Distributions Revolution-

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ized Our Views of Life and Earth. New York: Oxford University Press, 2009. This book traces the historical development of human realization that every part of the Earth had different plants and animals. McGavin, George C. Endangered: Wildlife on the Brink of Extinction. Richmond Hill, Ont.: Firefly Books, 2006. This book introduces readers to some important endangered species. McKibben, Bill. The End of Nature. New York: Random House, 1990/2006. This book was the first popular science book about global warming. The author explains how, by enhancing the natural greenhouse effect, humans have changed the entire natural world, so that it is an extension of human activity rather than being “nature.” Menino, Holly. Darwin’s Fox and My Coyote: Why Science Alone Can’t Win the Race to Save Wild Animals. Charlottesville, Va.: University of Virginia Press, 2008. This book is an appeal to environmental and conservation ethics, without which scientific efforts cannot succeed. Merchant, Carolyn. American Environmental History: An Introduction. New York: Columbia University Press, 2007. This textbook is an overview of the development of conservation and environmentalism in the United States. Plotkin, Mark J. Tales of a Shaman’s Apprentice: An Ethnobotanist Searches for New Medicines in the Amazon Rain Forest. New York: Viking, 1993. The author relates his stories of finding medicinal plants in the rain forest by listening to the people who live there. Primack, Richard B. Essentials of Conservation Biology. Sunderland, Mass: Sinauer Associates, 2006. This textbook relates the basic scientific concepts of conservation. Quammen, David. Song of the Dodo: Island Biogeography in an Age of Extinctions. New York: Scribner, 1996. The author explains island biogeography and introduces the scientists who have studied it. Rice, Stanley A. Green Planet: How Plants Keep the Earth Alive. New Brunswick, N.J.: Rutgers University Press, 2009. This book presents the argument that plants keep the Earth alive by removing carbon dioxide from the air, regulating temperature and the water cycle, making all the food, creating soil, and determining and restoring habitats and why plant diversity is essential. ———. Life of Earth: Portrait of a Beautiful, Middle-Aged, Stressed-Out World. Amherst, N.Y.: Prometheus Books, 2010. This book presents the evolutionary saga from the viewpoint of humans, who are the most extreme example of many evolutionary processes from sex to altruism and who

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558 Further Resources 558 are also the biggest threat to the Gaia system of planetary interaction. Rosenzweig, Michael. Win-Win Ecology: How the Earth’s Species Can Survive in the Midst of Human Enterprise. New York: Oxford University Press, 2003. The author presents the argument that endangered species can be preserved along with human prosperity. Terborgh, John. Requiem for Nature. Covelo, Calif.: Island Press, 1999. This book explains that most of our efforts to protect the natural world will prove futile. Thomas, Peter, and Rob McAlpine. Fire in the Forest. New York: Oxford University Press, 2010. This book explains the many roles of fire in ecology. Todd, Kim. Tinkering with Eden: A Natural History of Exotic Species in America. New York: Norton, 2002. This book presents many examples of invasive species in North America and the ecological damage they have inflicted. Volk, Tyler. Gaia’s Body: Toward a Physiology of Earth. New York: Copernicus, 1998. The author presents the Gaia hypothesis as an imperfect system of negative feedbacks rather than as a perfectly integrated organism, but a system that nevertheless has a physiology. Whittaker, Robert J. Island Biogeography: Ecology, Evolution, and Conservation. New York: Oxford University Press, 1998. An overview of the science of island biogeography and the conservation challenges associated with endemic species on ecological and geographical islands. Wilson, Edward O. The Diversity of Life. Cambridge, Mass.: Harvard University Press, 1992. The founder of the modern concept of biodiversity presents an important overview of the exuberant diversity of life on Earth—and the continuing surprises that come from the discovery of yet more diversity—and how the human future is threatened by the extinction of wild species. ———. The Creation: An Appeal to Save Life on Earth. New York: Norton, 2006. The founder of the modern concept of biodiversity sends an open letter to an unspecified conservative Christian preacher about why Christians should care about the protection of endangered species and the ecosystems of Earth.

Internet Resources Agricultural Research Service, United States Department of Agriculture. “Phytoremediation: Using Plants to Clean Up Soils.” Available online. URL: http://www.ars.usda.gov/is/ar/archive/jun00/ soil0600.htm. Accessed August 8, 2011. This gov-

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first entry ernment Web site gives examples of how plants can clean up toxic wastes from soils. American Chestnut Foundation. “American Chestnut Foundation.” Available online. URL: http://www. acf.org. Accessed August 8, 2011. This foundation is attempting to restore the American chestnut to its former prominence in Appalachian forests. Amphibiaweb. “Amphibiaweb.” Available online. URL: http://www.amphibiaweb.org. Accessed August 8, 2011. This Web site is a resource for information about amphibians. Animal Welfare Institute. “Endangered Species Handbook.” Available online. URL: http://www. endangeredspecieshandbook.org. Accessed August 8, 2011. This Web site presents stories about endangered species and habitats that can be used by teachers. Blue Ocean Institute. “Guide to Ocean Friendly Seafood.” Available online. URL: http://www. blueocean.org/seafood/seafood-guide. Accessed August 8, 2011. This is an online guide to which seafood has been harvested in a manner that will not cause the collapse of ocean populations. Botanical Society of America. “Carnivorous Plants/ Insectivorous Plants.” Available online. URL: http://www.botany.org/Carnivorous_Plants. Accessed August 8, 2011. This Web site introduces viewers to every species of carnivorous plant. Bushmeat Crisis Task Force. “Bushmeat Crisis Task Force.” Available online. URL: http://www.bushmeat.org. Accessed August 8, 2011. This Web site provides information about and coordinates actions to reduce the destruction of African primates as a food source. California Oak Mortality Task Force. “California Oak Mortality Task Force.” Available online. URL: http://www.suddenoakdeath.org. Accessed August 8, 2011. This Web site monitors the spread of the Phytophthora infestations that are killing California oak forests. Charles Darwin Foundation. “Charles Darwin Foundation.” Available online. URL: http://www. darwinfoundation.org/english/pages/index.php. Accessed August 8, 2011. This is the Web site for scientific research and conservation on the Galápagos Islands. Chicago Wildnerness. “Leave No Child Inside.” Available online. URL: http://www.kidsoutside. info. Accessed August 8, 2011. This Web site coordinates activities to get kids to experience natural habitats. Children and Nature Network. “Children and Nature Network: Building a Movement to Reconnect Children and Nature.” Available online. URL: http:// www.childrenandnature.org. Accessed August 8, 2011. This Web site coordinates ­activities around

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Further Resources 559 the United States to get kids to experience natural habitats. Convention on International Trade in Endangered Species (CITES). “Convention on International Trade in Endangered Species of Wild Fauna and Flora.” Available online. URL: http://www.cites. org. Accessed August 8, 2011. This is the Web site for the international agreement that protects endangered species by prohibiting the transport and sale of endangered organisms, living or killed. Coral Reef Alliance. “Coral Reef Alliance.” Available online. URL: http://www.coral.org. Accessed August 8, 2011. This Web site documents the destruction of coral reefs and what can be done to stop it. Cornell Lab of Ornithology. “All about Birds.” Available online. URL: http://www.allaboutbirds.org. Accessed August 8, 2011. This Web site is the place to go to find out about all kinds of birds and their classification. Earth’s Endangered Creatures. “World Endangered Species List.” Available online. URL: http:// www.earthsendangered.com/full_list_html.asp. Accessed August 8, 2011. All in one place, here is a list (without links) to all endangered species in the world, by Latin and common names. Encyclopedia of Life. “Encyclopedia of Life.” Available online. URL: http://www.eol.org. Accessed August 8, 2011. The Encyclopedia of Life is an attempt to establish a Web page for every species on Earth. Environmental Protection Agency. “Integrated Pest Management (IPM) Principles.” Available online. URL: http://www.epa.gov/pesticides/factsheets/ ipm.htm. Accessed August 8, 2011. The federal government presents guidelines for how IPM can be effectively practiced. ———. “Persistent Organic Pollutants: A Global Issue, a Global Response.” Available online. URL: http://www.epa.gov/oia/toxics/pop.html. Accessed August 8, 2011. This is the definitive list of longlasting pollutants in the environment and what is being done to control them. Froese, R., and D. Pauly, eds. “FishBase.” Available online. URL: http://www.fishbase.org. Accessed August 8, 2011. This is the place to go to find out about all kinds of fishes. Galápagos Conservancy. “Galápagos Conservancy.” Available online. URL: http://www.galapagos. org/2008/index.php?id=68. Accessed August 8, 2011. This is the Web site for an organization that is working to restore the damaged habitats of the Galápagos Islands. Global Footprint Network. “National footprints.” Available online. URL: http://www.footprintnet work.org/gfn_sub.php?content=national_foot prints. Accessed August 1, 2010. This Web site compares the ecological footprints of all nations.

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Hooked on Nature. “Tools, Resources, and Workshops to Help People Deepen Their Relationship with the Natural World.” Available online. URL: http://www. hookedonnature.org. Accessed August 8, 2011. Ideas for education in schools and for the general public, to promote awareness of biodiversity. Integrated Taxonomic Information System. “Integrated Taxonomic Information System.” Available online. URL: http://www.itis.gov. Accessed August 8, 2011. The authoritative Web site for the classification of all American species. International Society for Phylogenetic Nomenclature. “International Society for Phylogenetic Nomenclature.” Available online. URL: http://phylonames.org. Accessed August 8, 2011. This Web site explains and defends the cladistic system of classification. International Society of Organic Agriculture Research. “International Society of Organic Agriculture Research.” Available online. URL: http:// www.isofar.org. Accessed August 8, 2011. This organization promotes improvements in organic agriculture. International Union for the Conservation of Nature. “IUCN.” Available online. URL: http://www.iucn. org. Accessed August 8, 2011. This Web site provides access to the “IUCN Red List,” which is information about endangered species all over the world, but also provides links to information about climate change and how to develop a “green” economy. Land Institute. “The Land Institute.” Available online. URL: http://www.landinstitute.org. Accessed August 8, 2011. The Land Institute is the world center for developing Natural Systems Agriculture. Leopold Center for Sustainable Agriculture, Iowa State University. “Welcome to the Leopold Center.” Available online. URL: http://www.leopold. iastate.edu. Accessed August 8, 2011. The Leopold Center promotes the benefits of biodiversity within agriculture. Local Harvest. “Local Harvest.” Available online. URL: http://www.localharvest.org. Accessed August 8, 2011. This Web site provides information about where consumers can buy food directly from local farmers. Martin, R. Aidan. “ReefQuest Center for Shark Research.” Available online. URL: http://www. elasmo-research.org. Accessed August 8, 2011. This is the place to go to find out about sharks. Millennium Ecosystem Assessment. “Millennium Ecosystem Assessment.” Available online. URL: http://www.maweb.org/en/index.aspx. Accessed August 8, 2011. This Web site presents reports of ongoing studies of how ecosystem changes are affecting human well-being. Missouri Botanical Garden. “MBGnet.” Available online. URL: http://www.mbgnet.net. Accessed

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560 Further Resources 560 August 8, 2011. This Web site introduces the diversity of plant species for children. Monterey Bay Aquarium. “Seafood Watch.” Available online. URL: http://www.montereybayaquar ium.org/cr/seafoodwatch.aspx. Accessed August 8, 2011. This is an online guide to which seafood has been harvested in a manner that will not cause the collapse of ocean populations. National Agricultural Library. “National Invasive Species Information Center.” Available online. URL: http://www.invasivespeciesinfo.gov. Accessed August 8, 2011. This government Web site provides comprehensive invasive species information for the United States. National Oceanic and Atmospheric Administration. “NOAA Coral Reef Conservation Program.” Available online. URL: http://coralreef.noaa.gov. Accessed August 8, 2011. This Web site describes the U.S. government’s plans for saving and restoring coral reefs. Natural Resource Conservation Service, United States Department of Agriculture. “Plants Database.” Available online. URL: http://www.plants. usda.gov. Accessed August 8, 2011. This Web site provides information about and photographs of nearly all American plant species. Ornithological Council, National Museum of Natural History, Smithsonian Institution. “Birdnet: The Ornithological Information Source.” Available online. URL: http://www.nmnh.si.edu/ BIRDNET. Accessed August 8, 2011. This Web site is the place to go for information about bird species. Pelagic Shark Research Foundation. “Pelagic Shark Research Foundation.” Available online. URL: http://www.pelagic.org. Accessed July 9, 2010. This Web site is the place to go for information about sharks. Population Reference Bureau. “2011 World Population Data Sheet.” Available online. URL: http:// prb.org/pdf11/2011population-data-sheet_eng. pdf. Accessed August 8, 2011. This Web site provides population and economic information for every country in the world. Ratnasingham, Sujeevan, and Paul D. N. Hebert. “Barcoding of Life Data System.” Available online. URL: http://www.barcodinglife.org. Accessed August 8, 2011. This Web site explains the protocols for using DNA to identify every species. RealClimate. “RealClimate: Climate Science from Climate Scientists.” Available online. URL: http:// www.realclimate.org. Accessed August 8, 2011. This is a scientific source of information about global warming. Rowe, Noel. “Primate Conservation, Inc.” Available online. URL: http://www.primate.org. Accessed

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first entry August 8, 2011. This organization promotes the protection of endangered primate species. Solomon, Susan, and the Intergovernmental Panel on Climate Change. “Climate Change 2007: The Physical Science Basis.” Available online. URL: http://www.ipcc.ch/publications_and_data/ar4/ wg1/en/contents.html. Accessed August 8, 2011. This organization is the recognized world authority on global warming. Tree of Life Web Project. “Explore the Tree of Life.” Available online. URL: http://www.tolweb.org. Accessed August 8, 2011. This Web site provides a constantly expanding cladistic classification of all species. United Nations. “Convention on Biological Diversity.” Available online. URL: http://www.cbd.int. Accessed July 11, 2010. This Web site explains the role of the United Nations in protecting biodiversity around the world. ———. “UN-REDD Programme: The United Nations Collaborative Programme on Reducing Emissions from Deforestation and Forest Degradation in Developing Countries.” Available online. URL: http://www.un-redd.org. Accessed August 8, 2011. This Web site explains the United Nations effort to reduce deforestation by paying countries for the ecosystem services provided by leaving their forests intact. United Nations Environment Programme. “Overfishing: A threat to marine biodiversity.” Available online. URL: http://www.grid.unep.ch/ product/publication/download/ew_overfishing. en.pdf. Accessed August 8, 2011. UNEP explains the crisis of overfishing in the oceans. United Nations Food and Agriculture Organization. “Biodiversity for a World Without Hunger.” Available online. URL: http://www.fao.org/biodiver sity/en/. Accessed August 8, 2011. This Web site explains the efforts of the Food and Agriculture Organization to protect the genetic diversity upon which agriculture depends. United States Census Bureau. “International Data Base.” Available online. URL: http://www.census. gov/population/international/data/idb/informationGateway.php Accessed August 8, 2011. This Web site provides access to information about the population characteristics of every country in the world, from 1950 onward, including projections into the future. United States Department of Agriculture. “Animal and Plant Health Inspection Service: Safeguarding American Agriculture.” Available online. URL: http://www.aphis.usda.gov. Accessed August 8, 2011. This Web site explains the work of APHIS, which protects the United States from the importation of invasive species.

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Further Resources 561 University of Illinois at Urbana-Champaign. “Landscapes and Human Health Laboratory.” Available online. URL: http://lhhl.illinois.edu. Accessed August 8, 2011. This Web site presents information about the importance of green landscapes in human mental health. University of Michigan at Dearborn. “Native American Ethnobotany.” Available online. URL: http:// herb.umd.umich.edu. Accessed August 8, 2011. This Web site provides access to a database about the Native American uses of medicinal plants. Weed Science Society of America. “International Survey of Herbicide Resistant Weeds.” Available online. URL: http://www.weedscience.org/in.asp. Accessed August 8, 2011. This Web site is the definitive list of weeds that are resistant to herbicides.

Periodicals American Forests Published by American Forests Box 2000 Washington, DC 20013 Telephone (202) 737-1944 www.americanforests.org American Journal of Botany Published by the Botanical Society of America P.O. Box 299 St. Louis, MO 63166-0299 Telephone (314) 577-9566 www.botany.org Annual Review of Ecology, Evolution, and Systematics Published by Annual Reviews, Inc. P.O. Box 10139 Palo Alto, CA 94303-0139 www.annualreviews.org Audubon Published by the National Audubon Society 225 Varick Street, 7th floor New York, NY 10014 Telephone (212) 979-3172 www.audubon.org

223 Spring Street New York, NY 10013 www.springer.com BioScience Published by American Institute of Biological Sciences 1900 Campus Commons Drive, Suite 200 Reston, VA 20191 Telephone (703) 674-2500 www.aibs.org Biotropica Published for Association for Tropical Biology and Conservation by John Wiley 111 River Street Hoboken, NJ 07030-5774 Telephone (201) 748-6000 www.wiley.com Conservation Biology Published by Society for Conservation Biology 1017 O Street NW Washington, DC 20001-4229 Telephone (202) 234-4133 www.conbio.org Ecological Applications Published by the Ecological Society of America 1990 M Street NW, Suite 700 Washington, DC 20036 Telephone (202) 833-8773 www.esa.org Ecology Published by the Ecological Society of America 1990 M Street NW, Suite 700 Washington, DC 20036 Telephone (202) 833-8773 www.esa.org Ecosphere Published by the Ecological Society of America 1990 M Street NW, Suite 700 Washington, DC 20036 Telephone (202) 833-8773 www.esa.org

The Auk Published by American Ornithological Union 5400 Bosque Boulevard, Suite 680 Waco, TX 76710 Telephone (254) 399-9636 www.aou.org

Endangered Species Research Published by Inter-Research Science Center Nordbünte 23 (+ 3, 5, 28, 30) 21385 Oldendorf/Luhe, Germany www.int-res.com/journals/esr/esr-home

Biodiversity and Conservation Published by Springer

Environmental Entomology Published by the Entomological Society of America

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562 Further Resources 562 10001 Derekwood Lane, Suite 100 Lanham, MD 20706-4876 Telephone (301) 731-4535 www.entsoc.org

first entry Landscape Ecology Published by Springer 223 Spring Street New York, NY 10013 www.springer.com

Frontiers in Ecology and the Environment Published by the Ecological Society of America 1990 M Street NW, Suite 700 Washington, DC 20036 Telephone (202) 833-8773 www.esa.org

Oecologia Published by Springer 223 Spring Street New York, NY 10013 www.springer.com

Functional Ecology Published by the British Ecological Society Charles Darwin House 12 Roger Street London, WC1N 2JU Telephone 0207 685 2500 www.britishecologicalsociety.org

Proceedings of the National Academy of Sciences USA Published by the National Academy of Sciences 500 Fifth Street NW Washington, DC 20001 Telephone (202) 334-2000 www.nas.edu

Journal of Applied Ecology Published by the British Ecological Society Charles Darwin House 12 Roger Street London, WC1N 2JU Telephone 0207 685 2500 www.britishecologicalsociety.org

Restoration Ecology Published for Society for Ecological Restoration International by John Wiley 111 River Street Hoboken, NJ 07030-5774 Telephone (201) 748-6000 www.wiley.com

Journal of Biogeography Published by the International Biogeography Society 133 Basswood Court Westlake Village, CA 91361-2003 www.biogeography.org Journal of Ecology Published by the British Ecological Society Charles Darwin House 12 Roger Street London, WC1N 2JU Telephone 0207 685 2500 www.britishecologicalsociety.org Journal of Integrated Pest Management Published by the Entomological Society of America 10001 Derekwood Lane, Suite 100 Lanham, MD 20706-4876 Telephone (301) 731-4535 www.entsoc.org Journal of Mammalogy Published by the American Society of Mammalogists P.O. Box 7060 Lawrence, KS 66044 Telephone (800) 627-0326 www.mammalsociety.org

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Science Published by the American Association for the Advancement of Science 1200 New York Avenue NW Washington, DC 20005 Telephone (202) 326-6417 www.sciencemag.org Scientific American 415 Madison Avenue New York, NY 10017 Telephone (212) 754-0550 www.sciam.com Trends in Ecology and Evolution Published by Cell Press 600 Technology Square Cambridge, MA 02139 Telephone (617) 661-7057

Societies and Organizations American Association for the Advancement of Science (www.aaas.org), 1200 New York Avenue NW, Washington, DC 20005. Telephone: (202) 326-6400

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Further Resources 563 American Forests (www.americanforests.org), Box 2000, Washington DC 20013. Telephone: (202) 737-1944 American Institute of Biological Sciences (www. aibs.org), 1900 Campus Commons Drive, Suite 200, Reston, VA 20191. Telephone: (703) 674-2500 American Ornithological Union (www.aou.org), 5400 Bosque Boulevard, Suite 680, Waco, TX 76710. Telephone: (254) 399-9636 American Society of Mammalogists (www.mammal society.org), P.O. Box 7060, Lawrence, KS 66044. Telephone: (800) 627-0326 Association for Tropical Biology and Conservation (www.tropicalbio.org) Botanical Society of America (www.botany.org), Box 299, St. Louis, MO 63166-0299. Telephone: (314) 577-9566 British Ecological Society (www.britishecologicalso ciety.org), Charles Darwin House, 12 Roger Street, London, WC1N 2JU United Kingdom. Telephone: 0207 685 2500 Ecological Society of America (www.esa.org), 1707 H Street NW, Suite 400, Washington, DC 200063915. Telephone: (202) 833-8775 Entomological Society of America (www.entsoc.org), 10001 Derekwood Lane, Suite 100, Lanham, MD 20706-4876. Telephone: (301) 731-4535 International Biogeography Society (www.biogeogra phy.org), 133 Basswood Court, Westlake Village, CA 91361-2003 International Society for Ecological Economics (www.ecoeco.org)

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Linnean Society of London (www.linnean.org), Burlington House, Picadilly, London, W1J 0BF United Kingdom. Telephone: +44 020 7434 4479 National Academy of Sciences (www.nas.edu), 500 Fifth Street NW, Washington, DC 20001. Telephone: (202) 334-2000 National Audubon Society (www.audubon.org), 225 Varick Street, 7th floor, New York, NY 10014. Telephone: (212) 979-3172 National Science Foundation (www.nsf.gov), 4201 Wilson Boulevard, Arlington, VA 22230. Telephone: (703) 292-5111 Nature Conservancy (www.nature.org), 4245 North Fairfax Drive, Suite 100, Arlington, VA 22203. Telephone: (703) 841-5300 Royal Entomological Society (www.royensoc.co.uk), The Mansion House, Chiswell Green Lane, St. Albans, AL2 3NS United Kingdom. Telephone: +44 (0) 1727 899387 Society for Conservation Biology (www.conbio.org), 1017 O Street NW, Washington, DC 20001-4229. Telephone: (202) 234-4133 Society for Ecological Restoration International (www.ser.org), 1017 O Street NW, Washington DC 20001. Telephone: (202) 299-9518 Society for the Study of Amphibians and Reptiles (www.ssarherps.org) World Wildlife Fund (www.worldwildlife.org), 1250 Twenty-Fourth Street NW, P.O. Box 97180, Washington, DC 20090-7180. Telephone: (202) 983-4800

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Appendix IV

Classification System Used in Encyclopedia of Biodiversity*

note: this system does not include all evolutionary lineages. Domain archaea Domain eubacteria thermophilic bacteria chemolithoautotrophic bacteria Proteobacteria (purple bacteria) Green sulfur bacteria cyanobacteria Obligate anaerobic bacteria aerobic bacteria Pathogenic bacteria Domain eucarya (eukaryotes) Kingdom Protista = Protoctista includes all eukaryotes. chromista = stramenopiles Oomycota (water molds) Bacillariophyta (diatoms) Xanthophytes and phaeophytes (golden and brown algae) chrysophyta alveolates Dinoflagellata ciliopoda (ciliates) apicomplexa chlorophyta includes all green plants (see below) Rhodophyta (red algae) Opisthokonts Fungi (see below) choanoflagellates and animals (see below) amoebas Foraminifers Radiolarians Diplomonada (archezoans) euglenas Myxomycota (plasmodial slime molds) acrasiomycota (cellular slime molds) Kingdom Fungi (see above) Basidiomycota (mushrooms) ascomycota (sac fungi) 564

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565

Glomeromycota (vesicular arbuscular mycorrhizae) Zygomycota (bread molds) Chytrids Kingdom Plantae (see above) Zygnematales (conjugating green algae) Charales Embryophytes Marchantiomorpha (liverworts) Anthocerotophyta (hornworts) Bryophyta (mosses and liverworts) Rhyniophytes (extinct) Lycophytes (extinct) Filicopsida (ferns) Spermatopsida (seed plants) Cycads Ginkgos Gnetales Conifers Family Pinaceae (pines, spruces) Family Taxaceae (yews) Family Taxodiaceae (sequoias, junipers) Angiosperms Primitive dicots Family Nymphaceae (water lilies) Family Magnoliaceae (magnolias) Family Ranunculaceae (buttercups) Monocots Liliales Family Liliaceae (lilies) Commelinanae Family Bromeliaceae (bromeliads) Family Cyperaceae (sedges) Family Typhaceae (cattails) Family Poaceae (grasses) Eudicots Rosids: Fagales Family Fagaceae (oaks and beeches) Family Betulaceae (alders and birches) Family Juglandaceae (hickories and   walnuts) Rosids: Rosales Family Rosaceae (roses) Family Ulmaceae (elms) Moraceae group (mulberries, nettles,   hackberries, and cannabis) Rosids: Fabales Family Fabaceae (leguminous plants) Malphigiales Family Salicaceae (willows) Family Euphorbiaceae (spurges) Myrtales Family Myrtaceae (myrtles, eucalyptus) Brassicales Family Brassicaceae (mustards)

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566 Classification System Used in Encyclopedia of Biodiversity 566

first entry

Malvales Family Malvaceae (mallows, hibiscus) Sapindales Family Sapindaceae (maples, soapberries) Rutaceae (citrus) Family Vitaceae (grapes) Caryophyllales Polygonales Family Polygonaceae (buckwheat) Family Cactaceae (cactus) Family Caryophyllaceae (carnations) Cornales Family Cornaceae (dogwoods) Ericales Family Ericaceae (heaths) Solanales Family Solanaceae (tomatoes, etc.) Lamiales Family Lamiaceae (mints) Gentianales Family Apocynaceae (milkweeds) Asterales Family Asteraceae (composites) Apiales Family Apiaceae (umbellifers) Kingdom Animalia (see above) Ctenophora (comb jellies) Porifera (sponges) Placozoans Cnidaria Bilateria Protostomes Rotifera (rotifers) Platyhelminthes (flatworms, tapeworms, flukes) Lophotrochozoans Annelida (segmented worms) Mollusca (mollusks) Ecdysozoans Nematoda (roundworms) Arthropoda (arthropods) Chelicerates (e.g., Arachnids) Spiders Ticks Scorpions Myriapods (e.g., centipedes and millipedes) Crustaceans (crabs, lobsters, shrimp,   barnacles) Hexapods (e.g., insects) Odonata (dragonflies) Hemipteroids (bugs and lice) Orthopterans (grasshoppers, roaches, crickets) Coleoptera (beetles) Diptera (flies) Siphonaptera (fleas)

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Classification System Used in Encyclopedia of Biodiversity

567

Lepidoptera (butterflies and moths) Hymenoptera (ants, bees, wasps) Deuterostomes Echinodermata (starfish) Chordates Hagfishes Vertebrates Lampreys Gnathostomata (jawed vertebrates) Chondrichthyes (sharks, rays) Ray-finned fishes (e.g., teleosts) Sturgeons Gars Eels Carps and catfishes Salmons and trouts Pikes Cods Seahorses Sticklebacks Flying fishes Puffers Flatfishes Anglerfishes Sarcopterygians Lungfishes Amphibians Frogs Salamanders Caecilians Amniotes Turtles Diapsids Lepidosaurs: Lizards, snakes Archosaurs Crocodiles Dinosaurs Long-necked Theropods Birds: Birds: Paleognaths (ostriches) Neognaths Galliformes (fowl) Anseriformes (ducks) Passeriformes (perching birds) Piciformes (woodpeckers) Columbiformes (doves) Apodiformes (hummingbirds) Caprimulgiformes (nighthawks, swifts) Strigiformes (owls) Ciconiiformes (storks, herons, pelicans) Falconiformes (birds of prey) Charadriiformes (shorebirds) Sphenisciformes (penguins)

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568 Classification System Used in Encyclopedia of Biodiversity 568

first entry

Synapsids Mammals Monotremes Marsupials Eutherians (placentals): Placental mammals: Edentates (anteaters, sloths, armadillos) Lagomorphs (rabbits) Rodents Muroids (mice, rats, etc.) Sciurids (squirrels) Insectivores Carnivores Feliformia (cats) Caniformia Canidae (dogs) Ursidae (bears) Procyonidae (raccoons) Mustelidae (weasels, skunks) Pinnepedia (seals) Cetartiodactyls Cetaceans (whales, dolphins) Artiodactyls Deer Hippos Camels Ruminants Bovids Cervids Giraffes Perissodactyls (horses, rhinos) Sirenians (manatees) Proboscideans (elephants) Primates and relatives Lemurs New World monkeys (platyrrhines) Old World monkeys and apes (catarrhines) Cercopithecids (Old World monkeys) Hylobatids (gibbons) Hominids Orangutans Gorillas Chimps Hominins *Based on: Tree of Life Web Project. “Explore the Tree of Life.” Available online. URL: http://www.tolweb.org/tree. Accessed February 1, 2011.

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INDEX

note: Boldface page numbers denote main articles on a topic. Italic page numbers indicate illustrations. Page numbers followed by c denote chronology entries; page numbers followed by t denote tables, charts, or graphs; page numbers followed by m denote maps.

a

aardvarks 367 Abies 92, 137 Abies bracteata 222 Abies concolor 502 Abies fraseri 94 Abies magnifi ca 92 abrahamson, Warren 389 Abutilon theophrasti 3, 4, 330, 356, 501 acacia coevolution 122 deserts, warm 175, 177 dicots 186 Janzen, Daniel H. 338 keystone species 343–344 mutualism 380 Acacia 9, 380, 537 Acacia fumosa 56 Acacia tortilis 278 Acanthaster planci 149, 381 acanthocephala 28, 31 Acanthodis curvidens 98 acanthopterygii 248 Acanthostega 17 Acanthostega gunnari 16 accipitriformes 89 acclimatization 3, 388 Acer 73 Acer negundo 505 Acerodon jubatus 366 Acer saccharinum 187 Acer saccharum 187, 504, 513, 513 Achatina fulica 331 achelates 157 acid Deposition act 2 acidification 150, 297 Acidithiobacillus ferooxidans 43 acid rain and fog 1–2, 18, 94, 152, 373, 409 acid Rain Peer Review Panel 2 acoelomate 20 acorns 185 acorn woodpeckers 90 acorn worms 29 Acrocephalus arundinaceus 405 Acromyrmex 8 Actias luna 325 actinobacteria 41, 42, 380 adapid primates 443 adaptation 2–6, 5 amphibians 17 animals 20–21 biodiversity, patterns of 47

biodiversity, resources for agriculture 58 biogeography 76 biomimicry 82–83 competition, ecological 132 convergence 144, 146–148 cultural diversity 158–160 deserts, warm 176–182 ecology 206 fi shes 249–250 herbivory 306 insects 323 life history, diversity of 353–354 mammals 362, 365, 366 natural selection 388–389 parasitism 404 pollination 418–419 predation 437 reptiles 455, 456 rivers, streams, ponds, and lakes 467 seed dispersal 470–471 sexual selection 482 adaptive radiation 6–8, 73, 169, 374 adder’s-tongue ferns 476 Adelges tsugae 2 adelgid bugs 2 adhesion 83 Adiantum 475 adipose fi ns 248 adnate fusion 254 advanced cell technologies 220 Aedes aegypti 404 Aedes albopictus 330 Aegilops speltoides 310 Aegilops squarrosa 310 Aequorea victoria 69 aerobic bacteria 32, 509 aerobic respiration 42 Aetiocetus cotylaveus 399 afghan snakes 456 afl atoxins 262 africa adaptive radiation 6 agriculture 8–9 biodiversity, resources for agriculture 62 biogeography 73, 74 biomagnification 81 birds 87 camoufl age and mimicry 98 carson, Rachel louise 109 coevolution 122 cretaceous period, biodiversity in 154 deep oceans, biodiversity in 172 deserts, warm 175, 177, 180, 181 dicots 187 environmental ethics 223 extinction 235 grasslands and savannas 277t, 278–279 greenhouse effect 286 Humboldt, alexander von 307

ice ages 318 Maathai, Wangari 358–359 Pleistocene extinction 415 primates 443 Quaternary period, biodiversity in 452 reptiles 457 tropical rain forests and deforestation 533 tropical seasonal forests 537 african cherry 66 african honeybees 332 african land snail 331 african meerkats 159 agassiz, lake 316, 317 agassiz, louis 195, 315 Agathis australis 136 agaves 375, 376 Agelaius phoeniceus 370 age of Dinosaurs 153–156, 339–341 Agkistrodon contortrix 457 Agkistrodon piscivorus 457 Aglaophyton major 263 agnathan fi shes 246 agriculture x, 8–15, 10t, 11, 14 biodiversity, resources for agriculture 62–63 biomagnification 81 biomimicry 83 coevolution 122 convergence 148 greenhouse effect 290 herbivory 304 insects 326 invasive species 333 mutualism 380, 381 natural systems agriculture 390–392 pollination 420–421 population biology 429–430 resistance, evolution of 460 restoration ecology 462, 463 temperate deciduous forests 516 tropical rain forests and deforestation 531–533 agriculture, U.S. Department of (USDa) 59, 238, 239, 242, 548c Ailanthus altissima 350 Ailuropoda melanoleuca 363 air pollution 1–2, 289 alaska 94, 537 alaska’s north Slope 540 albedo 205, 211, 286, 311, 315, 316 Albumares 217 Alcanivorax borkumensis 84 alders boreal and subalpine forests 92 conservation biology 139 convergence 145 dicots 186 herbivory 304 hybridization 308 speciation 490, 492

569

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570 Index 570 tundra  alewives 345 algae animals 23 competition, ecological 134 coral reefs 149 eukaryotes 232 fungi 264 mutualism 381 protists 447, 448 seedless plants 472 alkaloids 67, 303 Allee, Warder C. 132, 429 Allee effect 132, 429 alleles 258, 430, 432–434 allelochemicals 133 allelopathy 132, 267–268, 487 alligator(s) 370, 456, 462 Alligator mississippiensis 370, 456 alligator snapping turtle 99 Allium cepa 144 allometry 5 allopatric speciation 490 allozymes 432 Alnus 92, 186, 490, 492 Alnus maritima 186, 194–195, 308 Alnus maritima ssp. georgiensis 221 Alnus maritima ssp. maritima 221 Alnus maritima ssp. oklahomensis 139, 221 Alnus serrulata 194, 308 Alosa pseudoharengus 345 alpha diversity 125–126 Alphadon 156 Alpheus lottini 381 alpine tundra 76, 194, 296, 537, 538, 538 Alps 76, 154 Alteromonas 380 altruism 389 Alvarez, Luis 152 Alvarez, Walter 152 alveolates 447 Amanita muscaria 262 amaranth 62 Amazon 548c amphibians 17 Bates, Henry Walter 45 biodiversity, patterns of 49 fishes 248 Humboldt, Alexander von 307 hydrological cycle 313 restoration ecology 461 tropical rain forests and deforestation 527, 531, 532, 534 tropical seasonal forests 537 Wallace, Alfred Russel 542 Amazonian tribes 461 amber 256 Ambolucetus natans 399 Amborella 254 Amborella trichopoda 75, 80, 221, 254, 356 Ambystoma mexicanum 18 amebozoan protists 448 American beeches 513, 515 American chestnuts 186, 234, 344–345 American gray squirrels 333 ammonia 18, 42, 394 ammonites 182, 399 ammonoids 151 amniotic egg 454 amoebae 447–448, 509–510 Amoeba proteus 509 Ampheristocystus 488 amphibians 15–19, 17t biodiversity, resources for medicine 66, 67 Carboniferous period, biodiversity in 105–106 Jurassic period, biodiversity in 341 Neogene period, biodiversity in 393 Permian period, biodiversity in 412 predation 436 Quaternary period, biodiversity in 452

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first entry amphipods 158 amphisbaeneans 458 Amsterdam Declaration (2001) 266 Amyciaea 497 Amytornis goyderi 181 Anacardiaceae 187 anadromous fishes 248, 251, 467 anaerobic archaea 32 anaerobic bacteria 41, 379 anaerobic fungi 261 anal fin 246 anapsids 454 Anatolian peninsula 313 ancestral traits 110 anchovies 248 Andersson, Malte 480 Andrias 17 Andropogon 278 Angier, Natalie 354 angiosperms. See also flowering plants angler fishes 99, 171, 248, 437 animal adaptations 180–182 Animal and Plant Health Inspection Service (APHIS) 334 animals 19–31, 20, 21t, 22–24, 26, 30. See also specific animals Anisocelis flavolineata 98 Ankylosaurus 155 Annelida 26–27, 172 Anniella 458 annuals 499 anole lizards 389 Anomalocaris 96, 97, 257–258 Anopheles 324 Anoplura 38, 322 anoxic deep oceans 373 anoxic deposits 407 Anseriformes 89 ant(s) 380, 404 agriculture 8–9 arthropods 38 coevolution 122 convergence 145, 148 Cretaceous period, biodiversity in 155 fungi 264 insects 323, 325–326 Janzen, Daniel H. 338 mutualism 380 seed dispersal 471 spiders 497–498 Wilson, Edward O. 545, 546 Antarctica arthropods 36–37 birds 89 deep oceans, biodiversity in 172 deserts, polar 174 greenhouse effect and biodiversity 296 ice ages 315, 316 monocots 377 Antarctic ice 282, 283, 285 Antarctic Ocean 171 anteaters 361, 367 antennae 34, 37, 320 antheridia 447, 473, 474 Anthill (Wilson) 545 anthrax 114 anthropic principle 544 anthropoids 441–442 antibiotic resistance 43, 66–68, 390, 423 antibiotics 64, 66–68, 173 anticoagulants 66 anticonvulsants 66 antienvironmentalists 270 antifreeze proteins 147 antifungals 59 anti-inflammatory compound 67 Antilocapra americana 173 antimicrobials 67, 459–460 antlers 480 ant-mimic spiders 497–498 Ants, The (Wilson and Hölldobler) 545

anxiety 230 Anza-Borrego Desert 179 Apalachicola River area 222 Apatosaurus 341 apes 366, 442, 444 Apex chert 33, 42, 256 aphids 35, 38, 52, 323, 380 APHIS. See Animal and Plant Health Inspection Service Apiaceae 188 apicomplexans 447 apicoplasts 509 Apis mellifera 215, 326, 421 apocalyptic Christianity 225 Apocynaceae 188 Apodiformes 89 apomixis 309, 491 Apotosaurus 191 Appalachian Mountains 2, 72, 234, 312, 516 appendages 35, 37, 320 appetite suppressant 66 apples 117–118, 186 Apterygota 321 aquaculture 172–173 aquatic arthropods 156 aquatic environment 17, 18 aquatic habitats 49, 90–91 aquatic invertebrates 257 aquatic plants 472 Aquifex 32 Arabian Peninsula 175 Arabidopsis thaliana 186 Araceae 376 arachnids 35, 496–499 arachnophobia 498 Aral Sea 463–464, 464 Araucaria araucana 136 Araucariaceae 136, 221 Araucaria heterophylla 136 Araucarioxylon trees 341 Arbor Day 548c arboreal adaptations 366 arbuscular mycorrhizae 263 Arcata, California 61 archaea 32–34, 549c bacteria 41, 42, 44 biodiversity, concept of 47 biological classification 79 decomposers 170 deep oceans, biodiversity in 171 eukaryotes 230–232 Archaean era 33, 42 archaebacteria 79, 509 Archaeopteris 183 Archaeopteryx 84, 85, 193, 193, 257, 341 Archaeosperma 477 Archaeothyris 106 archegonia 447, 473–476 Architeuthis dux 171 archosaurs 87, 454, 524 Arctic ice cap 284, 286 Arctic National Wildlife Refuge 540 Arctic Ocean 171, 174, 316, 537 arctic tern 89 arctic tundra 76, 194, 195, 537 Arctostaphylos bush 487 Ardea herodius 370 Ardipithecus ramidus 258 Arecaceae 376 arerectores pilorum muscles 360 Arfia 400 Argentina 13, 53, 173 Argyroneta 497 Aristotle 548c Arizona 76, 173, 175, 341, 344 Arizona bark scorpion 36 Arizona pines 511 Arkarua 217 Armadillidium 158 armadillos 297, 367, 450

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tundra  Index 571 arm bones 15, 17 armies 10, 11 Armillaria 262 Armillaria ostoyae 262–263 armored jawless fishes 183 army ants 145 Army Corps of Engineers 242 Army Survival Manual, U.S. 60 arrow worms 28 arroyos 177, 179 arsenic 84 Artemia 158 Artemia salina 305–306 Artemisia annua 67 artemisinin 67 Arthrobotrys oligospora 438 Arthropleura 105 arthropods 34–39, 34t, 36, 79 animals 27 biodiversity, concept of 46 Cambrian period, biodiversity in 96 Carboniferous period, biodiversity in 105 crustaceans 156 decomposers 170 deep oceans, biodiversity in 172 insects 318–327 island biogeography 336 Ordovician period 396 Silurian period, biodiversity in 488 spiders 496–499 articular bone 361 artificial evolution 58 artificial selection 11–12, 165, 384 Artiodactyla 365 arums 376 Asclepias 117 Asclepias viridis 133–134 Ascomycota 261–262 ascus (asci) 261, 262 asexual reproduction 35, 261–263 asexual sporangia 260 Ashe juniper 200, 331 Ashfall Beds State Historic Park 258 Asia biogeography 73 dicots 186 grasslands and savannas 276–278 temperate coniferous forests 511 temperate deciduous forests 513, 516 temperate rain forests 519 tundra 537 Asian carp 330–331, 333–334 Asian elephants 537 Asian tiger mosquitoes 330 Asiatic salamanders 17 Asimina triloba 119 Asipenser baerri baicalensis 222 aspens 73, 92, 186, 502 Aspergillus 264 Aspergillus flavus 262 Aspergillus oryzae 262 aspirin 66, 67 Asplenium septentrionale 476 Asteraceae 74, 75, 180, 188, 188, 272 asterids 188 asteroid collisions 373, 374, 409, 416 Astragalus 84, 186, 303 Astrapsis 397 Aswan Dam 30 asymmetry 22–23 Atacama Desert 175, 176 athlete’s foot 262 Atlantic cod 172 Atlantic horseshoe crabs 37, 46, 67 Atlantic Ocean 141, 154, 172 Atlantic rain forest 527 atmosphere 103, 269–270, 393, 394, 407 atmospheric carbon dioxide. See carbon dioxide, atmospheric Atrax robustus 498

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atrazine 18, 423 Atriplex hymenelytra 177 Atta 8, 380 auracarians 136 Australia biogeography 75 birds 87 boreal and subalpine forests 92 continental shelves, biodiversity on 141 deserts, warm 175, 177, 180, 181 disjunct species 196 Ediacaran organisms 217 grasslands and savannas 276, 278 greenhouse effect 286 hydrological cycle 313 invasive species 330, 331 mammals 361, 363, 367 Pleistocene extinction 415 shrublands 486, 487 spiders 498 symbiogenesis 510 temperate dry forests 517, 518 temperate rain forests 519 tropical rain forests and deforestation 527 Australian aborigines 461 Australian rats 360 Australopithecus 443–444 Australopithecus afarensis 258 autapomorphy 110 autecology 205–206 Avena barbata 12 Avena fatua 12 Avena sativa 12 Aventa fatua 278 avermectins 59 avocados 118 avoidance 177, 180, 304, 305 axolotl salamander 18 Axores 313 Ayrean grasswren 181 Azadirachta indica 59 azaelea 174 Azolla 476 Azores 196

B

bacilli 40 Bacillus 43 Bacillus thuringiensis 59 backswimmers 467 bacteria 40–45, 41t, 44t adaptation 5 archaea 32–33 biodiversity, concept of 47 biodiversity, resources for agriculture 59 biodiversity, resources for medicine 64–68 biological classification 78, 79 bioremediation 84 coevolution 121–122 commensalism 123, 124 competition, ecological 133, 134 convergence 143, 145, 148 decomposers 170 deep oceans, biodiversity in 171 ecosystems 212 eukaryotes 230–232 insects 323 Margulis, Lynn 368 mutualism 378–381 natural selection 385, 389, 390 nitrogen cycle 394 parasitism 402, 404, 405 pollution 423 population biology 424–426 symbiogenesis 508–510 bacterial chemosynthesis 549c bacteria-like organisms 32–33

Bacteriodes thetaiotaomicron 378 Bactrian camel 173 Bagherra kiplingi 496 Baikal, Lake 222, 469 Baikal seal 469 Baja, California 52–53 baker’s yeast 262 Balaenoptera musculus 365 balanced pathogenicity 121, 405 balanced polymorphism 434 balance of nature 130 Balanus 133 Bald and Golden Eagle Protection Act 243 Baldauf, Sandie 445 bald cypresses 137, 369, 371, 512, 513 bald eagle 108, 109, 219, 243 Ballard, Robert 549c Balsamorhiza sagittata 188 Baltica 396 Bambi syndrome 198 banana 62 bandicoots 363 Banks, Joseph 54, 56 Barbary macaque 518 barbs 83, 85, 86, 470 barcode of life 203 bark 254 bark scorpion 36 barley 10 barnacles 35, 124, 133, 147, 158, 165 Barnosky, Anthony 416 barrier reefs 149 Barro Colorado Island 52, 56, 129 Bartman, William 501 Barton, Andrew 52 Barton, Joe 281 Bartow County, Georgia 194, 221 Bartram, John 233, 356 Bartram, William 233, 439, 461, 462, 522 basal angiosperms 255, 478 Basidiomycota 261, 262 basil 59 Basilosaurus cetoides 399 bastard toadflax 403 Bates, Henry Walter 45–46, 50, 99, 542, 548c Batesian mimicry 45, 99 Batrachochytrium 19 Batrachochytrium dendrobatidis 18 batrachotoxin 17 bats 147, 418 biodiversity, patterns of 48 convergence 146 mammals 365–366 parasitism 403 pollination 418 sexual selection 481 Bayer 68 Bazzaz, Fakhri 298 bdelloid rotifers 28 Beagle, H.M.S. 162–163, 167, 271–273, 548c beaks 86, 168, 169, 455 beans 74 bears 66, 67, 249, 311, 516, 518 beavers 344, 370, 467 bee(s) arthropods 38 camouflage and mimicry 98–99 coevolution 120, 121 convergence 145 insects 325–326 pollination 418, 419, 421 beeches 73, 78, 185, 504, 513, 515 beef tapeworm 30–31 Beelzebufo 155 beer 262 beetles 418 arthropods 37 biodiversity, patterns of 51 biomimicry 83 camouflage and mimicry 99

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572 Index 572 tundra  convergence 145 decomposers 170 deserts, warm 181 greenhouse effect and biodiversity 297 insects 324–325 invasive species 331 IPM 328 Permian period, biodiversity in 412 rivers, streams, ponds, and lakes 467 Belarus 516 Benepe, Adrian 217 Bengal tiger 365 Bennett, Hugh Hammond 242, 549c Bennettitales 253 benthic waters 171–172 Benton, Michael 52, 408, 409 Beringia 74 Bering land bridge 74 Berry, Wendell 13, 14, 226, 375 beta diversity 126–128 Betula 73, 92 Betulaceae 186 Betula glandulosa 91 Betula occidentalis 91 Betula pendula 264 between-habitat diversity 48 bewnnettitalean plants 477–478 Bible 224–226 bichirs 247 bilateral symmetry 20, 20, 24–29 bile 66 binary code 83 binary fission 41 binocular vision 363, 366 binomial nomenclature 77 bioaccumulation 80–82 biodiversity, concept of 46–47, 47t biodiversity, patterns of 47–54, 47t, 129 biodiversity, quantification of 54–57, 56t biodiversity, resources for agriculture 57–64, 61, 63, 83, 215 biodiversity, resources for medicine 64–69, 65t, 83, 215 biodiversity hot spots 7, 52–53, 56, 75, 221, 234 biofilms 41 biogeochemical cycles 69–72, 71, 170, 212 biogeography 72–77, 74t deserts, warm 179–180 Humboldt, Alexander von 307 Wallace, Alfred Russel 543 Wilson, Edward O. 546 bioluminescence 41, 148, 171, 248 biomagnification 80–82, 81t, 82t, 212, 372 biomass 81, 209 biomimicry 82–83 bionomial nomenclature 548c biophilia 228 Biophilia (Wilson) 546 bioprospecting 42 bioremediation 42, 83–84 biotechnology 58–59, 69 bioterrorism 114 bipedalism 442 birches 73, 92, 186, 264, 304 bird eggs 21 bird-hipped dinosaurs 191 birds 84–90, 85, 86, 88t, 147, 379 biomagnification 80–81 camouflage and mimicry 99–100 Carson, Rachel Louise 108, 109 cladistics 112 coevolution 118–119, 122 commensalism 124 communities, ecological 126, 128 competition, ecological 134 convergence 146, 147 Cretaceous extinction 151 Cretaceous period, biodiversity in 155 cultural diversity 159 Darwin’s finches 167–169

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first entry deserts, cool 173 deserts, warm 181 dinosaurs 193 disjunct species 196 extinction 235 fossils and fossilization 257 greenhouse effect and biodiversity 297, 298 herbivory 305 Jurassic period, biodiversity in 341 keystone species 344 life history, diversity of 350 mammals 360, 363 marshes and swamps 370 mutualism 379 natural selection 386, 389 Neogene period, biodiversity in 393 parasitism 404 predation 436–438 reptiles 454 seed dispersal 470–471 sexual selection 480, 481 tropical seasonal forests 537 bishop pines 128, 136, 196, 199–200, 200, 308, 428 bison x, 198, 439 disturbances, ecological 198 extinction 234 federal government role in conservation (U.S.) 239 grasslands and savannas 279 predation 439 restoration ecology 461 temperate deciduous forests 516 Bison bison 461 bivalves 25, 26, 396, 467, 523 Bjork, Adam 479 black bears 518 black-bellied seedcrackers 389 blackberries 186 blackbirds 370 black cherry trees 186, 516 Black Death 323 Black Forest 2 Black Hills, South Dakota 91, 127, 196, 303, 511 black honey-eater 134 black ironwood 196 blackjack oaks 515 black locust 186 black mamba 457 black market 235 black oaks 185, 308.309 black pines 511 black poplar 186 black soil 531 black sunbird 134 black-tailed prairie dogs 366 black vulture 124 black walnut tree 113, 425 black widows 498 bladderworts 106–107 blas spiders 497 Blastocladiomycota 261 blending inheritance 386 blindness 31 blister beetles 98–99 blood 21, 250 blood cells 320, 353, 360 blood fluke 30 blood vessels 257 blueberries 91 blue crabs 297 bluefin tuna 172, 250 bluegills 308 blue heron 370 blue jays 471 blue oaks 6, 128, 278 blue orchard bees 421 blue poison dart frogs 18 blue whale 365

Blyth, Edward 384 boas 456 body shape 23 bog birch 91 bog people 91 bogs, life in 90–91 boreal and subalpine forests 92 ecosystems 208, 209, 212 rivers, streams, ponds, and lakes 469 seedless plants 474 succession, ecological 505 tundra 540 Boidae 456 Boiga irregularis 333 bois d’arc 118, 119, 186, 527 bolas spider 99 Bolivia 537 Bomakellia 217 bones 15, 16, 86, 193, 257, 258, 360–361, 454, 456 bonobo 443 Bonpland, Aimé 307 bony armor 246 bony fishes Carboniferous period, biodiversity in 105 Cretaceous period, biodiversity in 154 fishes 247–250 Jurassic period, biodiversity in 341 Neogene period, biodiversity in 392 Paleogene period, biodiversity in 399 Permian period, biodiversity in 412 Quaternary period, biodiversity in 452 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523– 524 book lungs 497 boreal and subalpine forests 91–94, 92, 93t biogeography 76 communities, ecological 125 disjunct species 196 greenhouse effect 292 greenhouse effect and biodiversity 297 temperate coniferous forests 511 tundra 540 Borneo 116, 526–527, 533, 534 Borrelia burgdorferi 40, 404 Bossert, William H. 545 Bos taurus 12 Botswana 175 botulism 43 Boulding, Kenneth 226–227, 427, 429 Bouteloua 278 Bouteloua curtipendula 198 Bouteloua gracilis 198 Bowers, Karen 420 bowfins 247, 250 bow-legged bug 98 Bowler, Peter 165 boxelder 505 Boyd, Christin 389 BP (British Petroleum) Deepwater Horizon oil spill (Gulf of Mexico, 2010) 549c continental shelves, biodiversity on 142–143 ecology 206 ecosystem services 214, 215, 217 federal government role in conservation (U.S.) 243, 244 brachiation 442 brachiopods animals 27 Carboniferous period, biodiversity in 105 Devonian period, biodiversity in 182 mass extinctions 374 Permian extinction 407, 408, 410 Permian period, biodiversity in 411 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523

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tundra  Index 573 Brachiosaurus 341 Brachycera 323 bracken ferns 476 bracts 135, 377 Bradshaw, Toby 492, 494 brain 351–352, 365, 366 brakefern 84 branchiopods 158 Branta sandiviensis 258 Brassica campestris 12 Brassicaceae 74, 186 Brassica napus 12 Brassica oleracea 186, 310 Brazil 498, 531, 532–534, 537 Brazilian rubber tree 188 breaching whales 365 bread 262 bread mold 261 breast cancer 354 brewer’s yeast 262 brine shrimp 305–306 bristlecone pines 92, 137, 138, 281, 281, 354 British Columbia 494 British Petroleum. See BP Deepwater Horizon oil spill broadleaf trees 513, 518 broad-sense heritability 432 broad-spectrum antibiotics 68 brome 278 bromeliad plants 52, 526 Bromus japonicus 278 Bromus tectorum 278 Brontosaurus 191, 341 brooding frogs 68–69 brown algae 232, 446, 447 brown bears 516 Brownlee, David 374 brown plant hopper 327 brown recluse spiders 498 brown tree snake 333 bryophytes 472–474 Bryozoa 27 Bt toxin 59 bubonic plague 38, 323 Bubulcus ibis 124 Buchloë dactyloides 274, 276 Buchnera 323 Buchnera aphidicola 510 bucket orchid 419 budding 262 buffalo. See bison buffalo gourds 61 buffalo grass 274, 276 Buffon, Georges-Louis Leclerc, comte de 77, 548c Bufo alvarius 17 Bufo marinus 331 Bufo periglenes 18, 116, 235 bugs 467 bulblets 538 bull nettle 133–134 bumblebees 418, 419 bundleflower 61 buoyancy 250 Buphagus africanus 122 Bureau of Reclamation 242 Burgess Shale 257 Buri, Peter 258 Burley, Nancy 483 bur oaks 6, 303, 309, 511 bursage bushes 175 Bursera simaruba 369, 515 burying beetles 170, 325 bush(es) 66, 91, 168, 175, 206, 233 Bush, George H. W. 2, 219–220 Bush, George W. 220, 225 bushmeat 235 buttercups 185 butterflies arthropods 37–38 Bates, Henry Walter 45

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coevolution 120, 121 DNA studies of biodiversity 202–203 herbivory 305 insects 324 life history, diversity of 349 predation 437 butterfly effect 270 butternuts 113 butterworts 106

C

C 4 grasses 393 C 4 photosynthesis 393 caatinga 537 cabbage 310 Cactaceae 179–180, 188–189 cacti 180, 189, 418 biodiversity, resources for agriculture 61 coevolution 119 communities, ecological 127 deserts, warm 175, 177, 179–180 dicots 188–189 Galápagos Islands 272 herbivory 303 Neogene period, biodiversity in 393 tropical seasonal forests 537 cactus finch 169 caddisflies 466 caecilians 17 caecum 365 Caenorhabditis elegans 27, 68, 353 Calamitales 473 Calamites 105, 475 calanolide A 68 calcium 70, 72, 212 calcium carbonate 101–102 calcium carbonate shells 256 calcium silicate 102 Caleidocrinus 397 California x adaptive radiation 6 agriculture 12 biodiversity, patterns of 52–53 biodiversity, resources for agriculture 61, 62 biogeochemical cycles 72 biogeography 73, 75, 76 birds 90 boreal and subalpine forests 92 communities, ecological 127–129 conifers 136, 137 deserts, cool 173 deserts, warm 175, 176, 179, 181 disjunct species 196 disturbances, ecological 199, 200 endemic species 221, 222 fossils and fossilization 258 greenhouse effect and biodiversity 296 marshes and swamps 369 restoration ecology 463 shrublands 486–487 temperate dry forests 517, 518 tundra 537 California black oak 309 California poppy 487 Callinectes sapidus 297 Calluna 487 Calment, Jeanne 354 Calocedrus decurrens 137 Calochortus 144 Calophyllum lanigerum 68 caltrop 180. See also puncture vine Calyptra minuticornis 324 Camarhynchus pallidus 169 Cambrian explosion 95–96 Cambrian period, biodiversity in 96–97, 97, 97t, 245, 257 camels 112, 173, 181 Camelus bactrianus 173

Camelus dromedarius 181 camouflage and mimicry 17, 98–101, 99, 100t, 248–249, 436–438, 455, 457 Campsis radicans 120 Canada 92, 196, 257, 537 Canada lynx 438 Canary Islands 313 cancer 66, 353, 354 Candida 262 Candida albicans 262, 379 cane toads 331, 332 Canfield, Donald 373 Canfield ocean 373 canines 308 Canis familiaris 12, 78, 308 Canis latrans 78 Canis lupus 46, 78, 308 canola 12 canopy 526, 531 canopy trees 528t–529t cap and trade 2 Cape Verde 313 Capra aegagrus 12 capsule 40 carapace 37, 157, 455 Carassius auratus 248 carbon 70, 212 carbon cycle 71, 101–103, 102t carbon dioxide amphibians 17 animals 23 communities, ecological 126 coral reefs 149 decomposers 170 fungi 262 hybridization 310 rivers, streams, ponds, and lakes 467 carbon dioxide, atmospheric 102t, 284t, 288t agriculture 14 biogeochemical cycles 70, 71 Cambrian period, biodiversity in 96, 97t carbon cycle 101–103 Carboniferous period, biodiversity in 104 coevolution 117 coral reefs 150 Cretaceous period, biodiversity in 153 decomposers 170 desert(s), warm 177 Devonian period, biodiversity in 182, 183 ecology 205, 206 ecosystems 211, 212 ecosystem services 214–216 federal government role in conservation (U.S.) 243, 244 fossils and fossilization 258 Gaia 267–270 greenhouse effect 279, 284t, 287–293 herbivory 305 Jurassic period, biodiversity in 339, 340t mass extinctions 375 Neogene period, biodiversity in 392, 393 Ordovician period 396, 397 Paleogene period, biodiversity in 399 Permian extinction 408–411 Quaternary period, biodiversity in 450, 451 Silurian period, biodiversity in 488, 489t succession, ecological 501 Triassic period, biodiversity in 523 tropical rain forests and deforestation 533, 534 tundra 540 carbon emissions 293t, 549c. See also carbon dioxide, atmospheric

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574 Index 574 tundra  carbon footprint 293 Carboniferous period, biodiversity in 103– 106, 104t, 105 amphibians 16 insects 320 mammals 361 seedless plants 473 seed plants 477 carbon isotope ratios 258, 408 carbon sequestration 290 carbon sinks 102, 102t carbon sources 102 Carcarhinus obscurus 344 Carcharodon megalodon 247, 392 Carcinoscorpus rotundicaudatus 46 Cardiocaryon 113 Carex aquatilis 540 caribou 76, 538 carnassial teeth 363 Carnegeia gigantea 180 Carnivora 78, 363–365 carnivores 365 adaptation 5 biological classification 78 competition, ecological 132 dinosaurs 191 ecology 206 ecosystems 208, 209 mammals 360, 361, 363–365 Triassic period, biodiversity in 524 carnivorous diets 210 carnivorous plants 91, 106, 106–107, 107t, 438 carp 248, 330–331, 333–334 carpels 252, 252, 254 Carpinus putoensis 235 carrion feeders 151 Carroll, Scott 389 carrots 188 carrying capacity 429 Carson, Rachel Louise 107–109, 108, 549c biomagnification 82 federal government role in conservation (U.S.) 242 IPM 328 natural selection 390 resistance, evolution of 459 Carsonella ruddii 510 cartilaginous fishes 246–247, 250 Carya 186 Carya illinoensis 515 Cascade Mountains 76 cassowaries 87 Castanea 73 Castanea americana 186, 516 Castanea dentata 234, 344–345 castor bean 187–188, 303 Castor canadensis 370 Castorocauda 341 Casuarina equisetifolia 333 casuarina trees 333 cat(s) 12, 112 Catalogue of Life (Internet database) 57 catarrhines 442 caterpillars 37, 98, 117, 305, 324, 500 catfish 248 Catharanthus roseus 66, 67, 527 Cathartes aura 124 catkins 185, 186 cattails 61, 78, 377 cattle 13, 210 cattle egrets 124, 427 caudal fin 246 Cavendish banana 62 CBD. See Convention on Biological Diversity CBOL. See Consortium for the Barcode of Life CCD. See colony collapse disorder Ceanothus bush 487 Cedar Lake Bog, Minnesota 208, 208t, 209

xviii+598_Biodiversity_F.indd 574

first entry cedars 137, 200, 313, 331, 333 Ceiba 527 Ceiba pentandra 527 cell fossils 42 cell membranes 32, 40, 230 cellulose 303 cell vacuoles 304 cell walls 32, 40, 230, 260 Cenchrus 144 Cenchrus spinifex 145 Cenozoic era 6, 8, 365, 392–394, 398–401, 450–452, 478 centipedes 27, 35 Central America 9, 189, 296, 527, 532, 537 Central Asian deserts 173 Central Mexico 486 Central Valley, California 369 Centris tarsata 421 Centruroides exilicauda 36 Cephalocarida 158 cephalopods animals 25, 26 Carboniferous period, biodiversity in 105 Cretaceous period, biodiversity in 154 deep oceans, biodiversity in 171 Devonian period, biodiversity in 182 Ordovician period 396–397 Permian period, biodiversity in 411 Cephalotes aratus 404 cephalothorax 35, 37, 157, 496, 497 Ceratiocaris 488 Ceratopealum 519 Ceratopsians 192 Ceratosaurus 341 cercopithecine 442 cercozoans 447–448 cereals 263 Cerris 73 Cervus canadensis 221 cetaceans 365, 365 cetartiodactyls 365 Cetorhinidae 171 Chaco Canyon, New Mexico 461, 461 Chaetognatha 28 Chagnon, Napoleon 546 Challenger Deep 171 Challenger expedition 548c Chamaesaura 457 Chamaesyce 168 Chambers, Robert 165 Chameleonidae 457 Channel Islands 12, 75 chaparral 129, 199, 486–487, 517 character displacement 169 Charadriiformes 89 charcoal 416 charismatic megafauna 363 Charniodiscus 217, 218 Charophyceae 448 cheatgrass 278 cheese 262 cheetahs 119 chelicerae 34–35, 496–499 chelonians 455–456 chemical defenses 117, 144, 147, 436 chemosynthetic bacteria 41 Chernobyl 82 Cherokee Nation 196, 238 cherry trees 66, 186 chert gap 407 Chesapeake Bay 462–463 chestnut(s) 73, 234, 344–345, 516 chestnut blight 262, 428, 516 Chicago 229 chickadees 69 chickens 89, 210, 404 Chicxulub crater 374 chiggers 36 Chihuahuan Desert 175, 180 childbirth 354–355

child care 352 Chile 486, 517 Chiloglottis trapeziformis 99 Chilopoda 35 chimaeras (ghost sharks) 247 chimeras (cells) 232 chimpanzees 235, 305, 351, 354, 443 China agriculture 9 cloud forests 115 conifers 137 continental shelves, biodiversity on 141 endemic species 222 extinction 233, 235 fishes 245 living fossils 356 Permian extinction 408 reptiles 456 temperate deciduous forests 516 Chine 49 Chinook 467–468 Chiroptera 365–366 chitin 260 chlorophyll 22, 448 Chlorophyta 448 chloroplasts bacteria 42 biomimicry 83 coevolution 122 eukaryotes 230–232 Margulis, Lynn 368, 369 protists 445–446, 448 symbiogenesis 508–510 chloroquine 68 choanocytes 22, 449 choanoflagellates 20, 448–449 chocolate 60 chocolate mint 59 chokecherry 303, 511 cholla 180 Chondrichthyes 246 Chordata 29, 78, 79 chordates 29, 244–251 Christian environmentalism 225 Christianity 163, 164, 224, 225 Christmas Island 156 chromists 447 chromosome(s) 90, 230, 232 chromosome doubling 309–310, 491–492 chrysalis 37, 324 Chrysemys picta 455 Chrysler Corporation 84 Chthamalus 133 chum 467 Chytridiomycota 261 chytrid protists 18 Cicada 323 cichlid fish 6–7 Ciconiiformes 89 cilia 26, 29, 509 ciliates 447 Cinara cedri 510 Cinclus mexicanus 466 Cingulata 367 circulation 360, 455 circulatory system 20–21, 26, 34, 147, 320, 496–497 CITES. See Convention on the International Trade in Endangered Species clades 80, 112–113 Cladina 348 cladistics 109–114, 111t, 113t, 114t cladograms 109–110, 111t, 112, 114 Cladonia rangiferina 381 clams 25, 171, 172 Clark, William A. 414 Clarkia, Idaho 256 Clark’s nutcrackers 137 class (taxonomic) 78 Claviceps 262 Claviceps purpurea 264

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tundra  Index 575 claws 363 Clean Air Act (1970) 243, 549c Clean Air Act Amendments (1990) 2 Clean Water Act 243, 549c Clements, Frederic 79, 124 Clethropsis 492 Cleveland, Grover 239 click beetles 99 climate biodiversity, patterns of 48–49 boreal and subalpine forests 92 Cambrian period, biodiversity in 96 Carboniferous period, biodiversity in 103 Cretaceous period, biodiversity in 154 Devonian period, biodiversity in 182 fossils and fossilization 258 ice ages 316–317 Jurassic period, biodiversity in 339 Neogene period, biodiversity in 392 Ordovician period 396 Paleogene period, biodiversity in 398 Permian period, biodiversity in 411 Pleistocene extinction 416 Quaternary period, biodiversity in 450 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523 climate change 416. See also global warming climatic shifts 295, 534 climax forest 500 climbing fern 476 Clinton, Bill 219–220 clitellum 27 cloaca 18, 86, 87, 250, 361–363, 455 clonal organisms 431 clones 262 cloning 159, 220 closed circulatory systems 21 closed-cone pine forests 199–200 Clostridium 43 Clostridium botulinum 43 Clostridium dificile 68 cloud forests 115–116, 115t, 222, 520 cloud formation 313 clouds 211, 311 Clovis people 343, 416, 417 club mosses 105, 472–474, 475 Cnidaria 23, 24, 149, 162, 218 Cnidoscolus texanus 133–134 coal acid rain and fog 1 biogeochemical cycles 72 biomagnification 82 carbon cycle 102 Carboniferous period, biodiversity in 103 environmental ethics 227 fossils and fossilization 256 greenhouse effect 289 greenhouse effect and biodiversity 295 insects 320 Permian extinction 408 seedless plants 473 coal balls 256, 473 coal gap 408 Coast Guard, U.S. 142 coatimundis 331 cobra 457 cobra lilies 106 Coburn, Tom 109 cocci 40, 41 cockleburs 83, 470 cockroaches 105, 322, 356, 412, 426, 459 cocoa 60 coconuts 470 cocoon 37, 324 Cocos Island 335 Cocos Island finch 169 codling moths 328 coelacanths 249

xviii+598_Biodiversity_F.indd 575

coelenterates 23, 24 coelom 20 Coelophysis 524 coelourosaurians 192 Coenobita clypeatus 156 coevolution 116–123, 116t coffee trees 60 coho fish 467 cold seeps 171–172 Cold War 263 Coleoptera 37, 324–325 collembolans 321 Colobanthus quitensis 174 colobines 442 Colombia 527 colonies 38 colony collapse disorder (CCD) 421 Colorado 258, 344 Colorado Desert 126, 175, 179 Colorado potato beetle 325 Colorado River basin 465 Colorado River toad 17 coloration 17, 98, 436, 437 color blindness 258 color vision 441 colugos 366 Columba livia 89, 386 Columbia River basin 465 Columbiformes 89 Columbus, Christopher 313 Comandra 403 comb jelly 23–24, 332 Comephorus baikalensis 222 Comephorus dybowskii 222 comets 373 Comita, Liza 52 commensalism 121, 123–124, 207, 401, 402, 404–405 commensals 378 communication 365 communities, ecological x, 124–130, 126m, 127m, 129, 130, 549c biodiversity, patterns of 51 biodiversity, quantification of 54 biological classification 79 competition, ecological 134–135 deserts, cool 173 disturbances, ecological 198–200 ecology 207 ecosystems 207 herbivory 305 Leopold, Aldo 347 life history, diversity of 355 Comoro Islands 249 compass plant 276 compensatory regrowth 305 competition 5, 481–483 competition, ecological 49, 129, 131–135, 531 competition, species 75, 169, 367–368, 384–390 Competitive Enterprise Institute 291 composite family 74, 188 composting 461, 531 compound eyes 320 computers 83 Conartium ribicola 297 condensation 177, 311 Condylostylus 321 cones 135, 417 cone snails 26, 66 Confusciusornis 156 Congress, U.S. 548c, 549c adaptation 2 Carson, Rachel 109 environmental psychology 229 federal government role in conservation (U.S.) 238, 239, 242, 243 greenhouse effect 281, 290, 292 Pinchot, Gifford 413, 414 coniferous forests 92, 296

conifers 92, 135–138, 136–138 acid rain and fog 1 biogeography 75 Carboniferous period, biodiversity in 105 endemic species 222 Jurassic period, biodiversity in 341 pollination 417, 420 seed plants 477, 478 temperate coniferous forests 511 temperate deciduous forests 513 temperate rain forests 518 connate fusion 254 Connell, Joseph 133 conodonts 97, 245–246, 258 Conraua goliath 17 conservation deep oceans, biodiversity in 172–173 deserts, warm 181 disturbances, ecological 200–201 federal government role in conservation (U.S.) 238–244 fishes 250–251 fungi 264 Gaia 269 habitat fragmentation 302 island biogeography 336 Janzen, Daniel H. 338–339 Maathai, Wangari 358–359 Muir, John 378 mutualism 381 Pinchot, Gifford 413–414 pollination 421 reptiles 456 tropical rain forests and deforestation 532 conservation biology 138–141, 439–440 conservation tillage 391 Consilience (Wilson) 546 Consortium for the Barcode of Life (CBOL) 203 consumers 208 continental drift 72 continental shelves, biodiversity on 49, 141–143, 142, 316, 409 contour feathers 85–86 contour plowing 391 Conus 66 Convention on Biological Diversity (CBD) 140, 235 Convention on the International Trade in Endangered Species (CITES) 218, 235, 244 convergence 73, 88, 110, 143–149, 145, 146t, 147, 366 Conway, Erik 280 Conway Morris, Simon 148–149 Cook, James 54 cookie-cutter shark 247 Cooksonia 472, 488 Cooper, Ellwood 333 Cope, Edward Drinker 190 Copenhagen Conference 549c copepods 158 copper 71 copperhead snake 457 coprolites 257 Copsychus sechellarum 234 Coragyps atratus 124 coral bleaching 23, 149, 150, 463 Corallorhiza 144, 170, 403 coral reef(s) 149–151, 150 animals 29 biodiversity, patterns of 49, 52 continental shelves, biodiversity on 141–142 greenhouse effect and biodiversity 297 mutualism 381 succession, ecological 501–502 coral reef fish 380 coral reef shrimp 145

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576 Index 576 tundra  coral-root orchid 170 corals 67, 344 coral snakes 457 Cordaites 477 cordgrass 297, 370 Cordia alliadora 144 core eudicots 185 Corema album 196 Corema conradii 196 Corixidae 467 cork oak 6, 73, 518 Corkscrew Swamp Sanctuary, Florida 370 cormorant 76 corn. See maize corn borer larvae 490–491 Correns, Carl 369 Coryanthes panamensis 419 Costanza, Robert 217 Costa Rica 339, 526 cottonmouth snake 457 cotton sedge 91 cottonwoods 73, 186, 187, 483, 516 cottony cushion scale 328 cotyledons 184, 185, 375 Courtenay-Latimer, Marjorie 249 cowbirds 99–100 Coweeta watershed 312 Cowles, Henry Chandler 504 cows 11–12, 30–31, 111–112, 122, 304– 305, 378 coxa 320 coyote 78 crabs arthropods 37 biodiversity, concept of 46 biodiversity, resources for medicine 67 crustaceans 156 deep oceans, biodiversity in 172 Jurassic period, biodiversity in 341 living fossils 356 mutualism 381 crab spiders 497, 497 Crafoord Prize 339 cranberries 91 craneflies 323 Crassostrea virginica 463 Crassula erecta 128 Crataegus 119 crayfish 157 creationism 166, 225–226, 356 creeks 465, 466 Crematogaster 380 Crenarcheota 33 creosote bushes 175 Cretaceous extinction 151–153 carbon cycle 102, 103 Gaia 268–269 mammals 362 mass extinctions 372, 374 succession, ecological 506 Cretaceous period, biodiversity in 153–156, 153t–154t, 155 birds 85, 87 deep oceans, biodiversity in 171 dinosaurs 193 flowering plants 252–253 insects 320–321 mammals 361, 362 crickets 321 crime 229 crinoids 397 crocodiles 221, 341, 454–456, 524 Crocodylus mindorensis 221 Crocodylus porosus 456 Croll, James 315 crop plants 10t, 12, 381, 501 crop production 13, 304 crop rotation 13, 63, 327, 394 crossopterygians 247, 249 cross-pollination 310, 460 Cross Timbers forest 515

xviii+598_Biodiversity_F.indd 576

first entry Crotalinae 181 Crotalus cerastes 457 crowberries 75, 196 crown-of-thorns starfish 149 crows 118 crucifers 186 crustaceans 31, 35, 154, 156–158, 157, 341 crustose lichens 348 Cryphonectria parasitica 234, 262, 344–345 Cryptocerus 356 Cryptococcus 262 cryptodires 455–456 cryptograms 77 Cryptomeria japonica 137 cryptomonads 447 Cryptostylis 420 Cryptotethya crypta 67 Ctenizidae 497 ctenophores 23–24 cuckoos 99–100, 405 cucumbers 470 cud 365 Culex pipiens 404, 491 Culex tarsalis 404 cultivated mustards 12 cultivated oats 12 cultural diversity 158–160, 159 Cunoniaceae 519 Cupressaceae 137 Cupressus macrocarpa 318 Curatella americana 278 Curculionidae 325 Curcurbita foetidissima 61 curly-nosed primates 366 Currie, Cameron 380 Curtis, John T. 54, 55 Cuscuta 110, 403 cushion plants 538 Cuyahoga River, Ohio, fire (1969) 242 cyanobacteria agriculture 13 animals 22–23 bacteria 41–44 deep oceans, biodiversity in 170 eukaryotes 232 fossils and fossilization 256 fungi 264 Gaia 267 lichens 348 nitrogen cycle 394 rivers, streams, ponds, and lakes 466 symbiogenesis 509 cycads 341, 477, 478 cyclic AMP 448 Cycliophora 21, 28, 549c cyclones 286 Cycloprosopon 341 Cyclorana platycephalus 180 cyclosporine 66, 262 Cydia pomonella 328 cynodonts 361 Cynomys 344 Cynomys ludovicianus 366 Cyperaceae 377 Cyperus alternifolius 222 cypresses 137, 369–371 Cyprinodon diabolis 301 Cyprinodon nevadensis nevadensis 301 Cyprinodon salinus 180 Cyprinus carpio 248 Cyrtocara eucinostomus 481 cystic fibrosis 434 cysts 29–30 cytoplasm 40, 230, 231 cytoplasmic inheritance 369

daddy longlegs 35 daffodils 375 Daily, Gretchen 344

D

dairy products 42 daisies 177 daisy trees 272 Daktulosphaira vitifoliae 60 dams 251, 469, 533 damselflies 321, 466, 481 Danaus plexippus 117 dandelions 330, 491 Daphne Major 273 Daphnia 158 Darlingtonia californica 106 Darwin, Charles 161–167, 163, 548c Bates, Henry Walter 45 biodiversity, patterns of 50 biodiversity, quantification of 54 biogeography 72 biological classification 78 carnivorous plants 107 cladistics 113–114 communities, ecological 130 competition, ecological 131 Darwin’s finches 167–169 disjunct species 195 flowering plants 253 Galápagos Islands 271–273 Humboldt, Alexander von 307 island biogeography 335 life history, diversity of 351 natural selection 384–390 population biology 424, 427, 429 sexual selection 479, 480 speciation 489, 490 symbiogenesis 507–508 Thoreau, Henry David 522 Wallace, Alfred Russel 542–545 Darwin, Robert 161, 162 Darwin, Susannah Wedgewood 161 Darwin’s finches 8, 134, 167–170, 168t, 432–433, 491, 493, 494 Dasypus novemcintus 367 date palms 62, 63, 179 Davis, Marc 373 Dawkins, Richard 390 dawn redwoods 51, 136–137, 222, 356 DDT 81t, 549c biomagnification 80–82 Carson, Rachel Louise 108, 109 federal government role in conservation (U.S.) 242, 243 IPM 328 resistance, evolution of 460 Dean, Rebecca 481 death 353–355 Death Valley, California 176, 176, 180, 301, 330 debridement 38 decapods 35, 157 Deccan Traps 374 deception 352 deciduous forests 513, 515 adaptive radiation 6 biodiversity, patterns of 49, 52 communities, ecological 126 greenhouse effect and biodiversity 296 keystone species 344–345 Paleogene period, biodiversity in 398 temperate coniferous forests 511 temperate deciduous forests 512–516 tropical seasonal forests 537 deciduous oaks 185 deciduous white oaks 6, 7 decomposers 71, 170 animals 27 bacteria 42 carbon cycle 101 commensalism 124 ecology 205, 206 ecosystems 208 fungi 261–263 Gaia 267, 268 Janzen, Daniel H. 339

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tundra  Index 577 decomposition agriculture 14 bogs, life in 91 fossils and fossilization 256, 257 Gaia 269 greenhouse effect 286–287, 290 nitrogen cycle 394 tropical rain forests and deforestation 530 Deep Ecology 226 deep oceans, biodiversity in 170–173 deep ocean vents 32, 41, 43 Deepwater Horizon oil spill (2010). See BP Deepwater Horizon oil spill deer 12, 56, 111, 338, 344, 345, 518 deer ticks 36, 404 Defense, Department of 239, 241–242 defense mechanisms 76, 146 defoliant chemicals 533 deforestation 312, 312, 313, 461, 525–526, 531, 533, 534 Deinococcus radiodurans 43 Delaware 194, 195 Delmarva Peninsula 194, 196, 221 demes 423 Demodex folliculorum 36 Dendroaspis polylepis 457 Dendrobates azureus 18 dendrobatid frogs 67 Dendroctonus ponderosae 297 Dendroctonus rufipennis 297 dengue fever 324 denitrification 42, 394 dentary bone 361 depth perception 441 derived traits 110–112 Dermochelys coriacea 455 Dermoptera 366 Descent of Man, The (Darwin) 166, 479, 544 Deschampsia antarctica 174, 296 desert(s) 130 adaptation 6 arthropods 36 biodiversity, resources for agriculture 61 biogeography 73 convergence 144 ecology 206 life history, diversity of 351 tropical seasonal forests 537 desert(s), cool 174–175, 174t desert(s), polar 175 desert(s), warm 175–182, 176, 177, 178t–179t, 180 desert frogs 6, 180 desert rhubarb 179 desert shrubs 129 Desmanthus illinoensis 61 detergents 466 detritivores 126 Deuteromycota 261 deuterostomes 28–29 Devil’s Hole 301 devil’s rider walking stick 436 devil’s thorn 180 Devonian mass extinction 372–373 Devonian period, biodiversity in 15, 182– 184, 183t, 184, 320, 473, 477 DeVries, Hugo 369 DeWaal, Frans 443 Diamond, Jared 11, 134 diapsids 87, 412, 454 diatomaceous earth 128, 258 diatoms 381, 446 dibamid lizards 458 Dicamba 460 dicots 113t, 114, 114t, 144, 184–190, 185, 187–189, 254, 255 Dictyoptera 322, 356 Dictyostelium discoideum 448

xviii+598_Biodiversity_F.indd 577

Didelphus virginiana 354, 362, 437 digestion 86, 260, 378–379 digestive bacteria 43 digestive systems 5, 23, 24, 27, 29 digital code 83 dikaryotic cells 260 Dimetrodon 361, 412, 412 dingos 367 dinoflagellates 46, 232, 447 Dinosaur National Monument 258 dinosaurs 190–194, 191–193 adaptive radiation 8 birds 84–87 cladistics 112–113 Cretaceous extinction 151 Cretaceous period, biodiversity in 153–156 fossils and fossilization 257, 258 Jurassic period, biodiversity in 339– 341 mammals 361, 362 mass extinctions 374 reptiles 454 Triassic period, biodiversity in 524 Dionaea muscipula 106 Dioscaryon 113 Diospyros kaki 60 Diospyros virginiana 60, 504, 527 diplococci 41 Diplodocus 341 diploid cells 260 diploid phase 472, 477 diplomacy 140 Diplopoda 35 Dipodomys 181 dipper ouzel 466 Diprotodon 393 Diptera 323 dipterans 38 Dipterocarpaceae 527, 537 Dipylidium caninum 31 directional selection 387, 388t, 389 discicristates 445–446 disease x agriculture 11 animals 29–31 arthropods 38 bacteria 42 biodiversity, resources for agriculture 58, 62 coevolution 121 ecosystems 210 fungi 263 greenhouse effect and biodiversity 298 insects 323, 324 parasitism 404 pollination 421 population biology 428 restoration ecology 461 succession, ecological 501 temperate deciduous forests 516 disjunct species 194–197, 195 disk florets 188 dispersal 73–75, 194, 196, 348, 388, 403 “Dispersion of Seeds, The” (Thoreau) 228–229, 521 Distichlis palmeri 60 distraction mimicry 98 distribution 47–48, 55 disturbances, ecological 197–202, 198– 200, 201t biodiversity, patterns of 51 biodiversity, quantification of 56 biogeography 77 ecology 207 extinction 233 marshes and swamps 370 succession, ecological 499–502, 505–506 Diversity of Life, The (Wilson) 545, 546 diversity selection 387, 388t, 389

diving beetles 467 divisions 78 DNA animals 27 archaea 32–33 bacteria 40, 43, 44 biomimicry 83 eukaryotes 230–232 fossils and fossilization 256 fungi 262 mammals 365 DNA sequencing 110–114 DNA studies of biodiversity 202–204 biodiversity, resources for agriculture 58–59 biodiversity, resources for medicine 69 deep oceans, biodiversity in 171 population genetics 432–433 speciation 492 symbiogenesis 508 dobsonflies 466 Dobzhansky, Theodosius 119, 430, 490 dodder 403 dodos 234, 462 dogs 12, 75, 78, 112, 308 dog tapeworm 31 Dolomedes 467 dolphins 365 domains (taxonomic) 79 domesticated grapes 187 dominance-diversity curves 55 dominant alleles 434 donkeys 12, 173, 308, 330 dorsal fins 248 dorsal nerve cord 29 dorsal surface 20 double fertilization 252 Douglas firs 137, 511, 518 dove(s) 89, 350 Dover, England 258 down feathers 86 dragonfishes 248 dragonflies 105, 105, 320, 321, 412, 466, 481 drainage basins 465 Dreissena polymorpha 26, 330 Drina River Valley 222 dromedary camels 181 Dromiciops gliroides 363 Drosera capensis 106 Drosera rotundifolia 91, 106 Drosophila 430, 493, 494 Drosophila bifurca 479 Drosophila melanogaster 68, 353 Drosophila sechellia 493 Drosophila simulans 493 drought 168, 169, 286, 297 drought adaptations 176–180 drought resistance 234 dry-nosed primates 366 dry soils 61 dry summers 312 duck-billed platypus 362, 363 ducks 89 duckweeds 467 dung beetle 325 Dunkleosteus 183 DuPont 68 Dürer, Albrecht xi dusky shark 344 dust bowl 223, 223, 239, 241, 242 Dutch elm disease 262 dwarf azaelea 174 dwarf lantern shark 246 Dytiscidae 467

E

ear bones 16, 361 early birds 87 early-successional habitats 499, 500

11/17/11 1:13 PM

578 Index 578 tundra  Earth Day 549c earthquake (Japan, 2011) 549c Earth’s Endangered Creatures 219 Earth Summit 549c earthworms 26–27, 166, 170 Easter Island 66, 313 eastern red cedar 200, 331 Ebenaceae 527 ebola virus 121 ebony 527 Ecballium elaterium 470 ecdysis 27–28 echidnas 363 echinoderms 28–29, 149, 154, 397, 411, 488 Echiura 28 echolocation 146 Ecklonia 141 ecological degradation 461 ecological footprint 292–293, 292t, 521 ecological islands 221 ecological rules 381 ecological succession. See succession, ecological ecology xi, 205–207, 548c. See also restoration ecology economy of nature 351 ecosystems x, 207–213, 208t, 209t, 210m, 211t agriculture 12 bacteria 42, 43 biogeochemical cycles 69–72 biomimicry 83 fungi 262–264 hydrological cycle 311–314 invasive species 333 keystone species 343–345 mammals 363 natural selection 385 restoration ecology 460–464 ecosystem services 213–217, 216t ecotones 125 ectomycorrhizae 263 Ectopistes migratorius 234 Ectoprocta 27 ectotherms 17, 249, 455 Ecuador 12, 52, 68, 167–169, 527, 533, 538 Ecuadorean Amazon 525 edaphic factors 128 edentates 367 edge effect 139, 301 Ediacara Hills 217 Ediacaran organisms 95–97, 217–218, 372 Edmondstone, John 162 eels 172, 247–238 effluent 466 egg(s) amphibians 18 animals 20, 21, 25, 29–31 arthropods 38 birds 87 dinosaurs 190 reptiles 454, 455 egg capsule 246 egg cells 473, 474, 479 Egypt 30 Ehrlich, Paul 344 Eichhornia crassipes 84, 372, 467 Eiseley, Loren 165 Elapidae 456–457 elapids 456–457 Elateridae 99 electric eels 248, 307 electrolocation 146 electrophoresis 432 Electrophorus electricus 248 electroreception 246 elephant(s) 276 coevolution 119 keystone species 343–344 life history, diversity of 350, 351 mammals 366–367

xviii+598_Biodiversity_F.indd 578

first entry natural selection 385 tropical seasonal forests 537 elephant birds 87 elephantiasis 31, 402 Eleutherodactylus coqui 18 elevation 176 eliasomes 471 elk 221 Elkinsia 477 Ellesmere Island 16, 174 Ellstrand, Norm 12 elms 73, 262 El Niño 168, 271 El Niño Southern Oscillation (ENSO) 171, 284 Elodea canadensis 467 embryo(s) 28, 362, 477 embryonic development 479 Emerson, Ralph Waldo 378, 521, 522 emperor scorpion 36 Empetraceae 75, 196 Empetrum 196 Empusa muscae 261 emus 87 encephalitis 324 Encyclopedia of Life (Internet database) 47, 57 endangered species 218–221, 219t, 220t, 235, 242, 244 Endangered Species Act (ESA) 219, 220, 243, 549c endemic species 221–222, 526 Endoceras 397 endomycorrhizae 263 endopterygotes 323 endosperm 484 endospores 43 endosymbiotic bacteria 510 endotherms 86, 249, 361 energy balance 205–206, 211 energy efficiency 210, 292 energy flow 48, 207–211 energy pyramid 209 energy storage 209 England. See Great Britain English oak 6, 303 Ensatina 494 ENSO. See El Niño Southern Oscillation Entoprocta 27 environmental degradation 463, 464 environmental ethics 215, 223, 223–228, 347 environmental impact 220 environmentalism 520–522 Environmental Protection Agency (EPA) 243, 327, 549c environmental psychology 228–230 environmental terrorism 226 enzymes 32, 231 Eomaia 156 Eoraptor 191 EPA. See Environmental Protection Agency ephemeral plants 177, 513 Ephemeroptera 321 epibatidine 17, 67, 68 epidermal scales 367 epigenetics 3 Epipedobates tricolor 17, 67 epiphytes 52, 376, 513, 518, 526, 526, 531 Epischura baikalensis 222 Equador 116 equilibrium 433–434 Equisetophyta 474–475 equitability 56 Equus 452 Equus asinus 12 Equus caballus 12 Equus hemionus 173 ergot 262, 264 Erica 196, 487 Ericaceae 91

Eriophorum vaginatum 91, 195, 540 Eristalis tenax 467 erosion 13 Eruasian walnuts 113 Erwin, Douglas 148, 374, 407, 408 Eryops 412 ESA. See Endangered Species Act Escherichia coli 43, 143, 379 Eschscholzia californica 487 Eschscholzia mexicana 497 Española 169 Essay on the Principle of Population (Malthus) 164, 548c Estopistes migratorius 461 estuaries 370 ethical systems 223 Ethiopia 56, 60 ethnobotanists 66 Etmopterus perryi 246 Etterson, Julie 3 eubacteria 79 eucalyptus 92, 333, 463, 487, 517, 518 Eucalyptus globulus 518 Eucalyptus pauciflora 92 Eucryphya 519 eudicots 185–189, 255, 478 eugenics 544 Euglandina rosea 331 Euglena 445–446 eukaryotes 47t, 230–233, 232t animals 19–31 bacteria 42, 44 coevolution 122 population genetics 430 protists 445–449 species diversity 47t symbiogenesis 508–509 eukaryotic flagella 232 Euphorbia 187 Euphorbiaceae 187 Euphorbia marginata 133–134 Eupithecia 324 Eurasia 11–12, 73–76, 174, 415 Eurasian watermilfoil 330 Europe acid rain and fog 2 adaptive radiation 6 agriculture 9 biodiversity, patterns of 49 biogeography 73, 76 boreal and subalpine forests 92 Devonian period, biodiversity in 182 dicots 186 greenhouse effect 285 ice ages 318 invasive species 331, 333 Paleogene period, biodiversity in 398 temperate coniferous forests 511 temperate deciduous forests 513, 515, 516 temperate dry forests 517 tundra 537 European blackcap 297, 298 European grapevines 60 European honeybees 326, 332 European rock dove 89 Eurotamandua 401 Euryarcheota 33 Eurypterids 396 Eusthenopteron 249 Eusthenopteron foordi 15 eutrophication 13, 150, 394, 466 eutrophic water 466 Evangeline (Longfellow) 201 evaporation 206, 311 evapotranspiration 313 evening primrose 345, 418 Everglades 369, 372 evergreen(s) 92, 513, 515, 525 evergreen broadleaf trees 537 evergreen oaks 185

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tundra  Index 579 evergreen palm trees 537 evergreen white oak 6 evolution 548c adaptation 2–6 adaptive radiation 6–14 agriculture 8–12 amphibians 15–17 bacteria 43–44 biodiversity, concept of 46 biodiversity, patterns of 49 biodiversity, resources for agriculture 58 biogeography 72, 75 biological classification 78 birds 85 cladistics 113–114 convergence 148 crustaceans 157 Darwin, Charles 161–166 Darwin’s finches 167–169 disjunct species 195 ecology 206 environmental ethics 226 eukaryotes 231 fishes 246, 249 flowering plants 254 fossils and fossilization 258 Galápagos Islands 271–273 Grant, Peter and Rosemary 273–274 herbivory 306 ice ages 318 life history, diversity of 351–355 mammals 362–363 Margulis, Lynn 368–369 mass extinctions 374 natural selection 384–390 parasitism 402 pollination 420 population biology 426 population genetics 430, 434 protists 445 resistance, evolution of 459–460 sexual selection 478–484 speciation 494 symbiogenesis 507–508 tropical rain forests and deforestation 526 Wallace, Alfred Russel 542–545 evolutionary diversity 261–262 evolutionary medicine 58 exaptation 4–5 excavates (protists) 445 Exopterygota 321 exoskeleton 34, 96, 156, 318, 496 exponential population growth 425, 427, 429 Expression of Emotions in Men and Animals, The (Darwin) 166 Extatosoma tiaratum 322 external digestion 260 external fertilization 18, 21, 26, 249 external parasites 379 external skeletons 28 extinction x, 233–237, 236t agriculture 13 amphibians 18–19 biodiversity, resources for agriculture 59–62 biogeography 75 birds 87 Cambrian period, biodiversity in 97 coevolution 118–119 conservation biology 139 Cretaceous extinction 151–152 Cretaceous period, biodiversity in 156 Devonian period, biodiversity in 184 dinosaurs 193 disjunct species 196 ecology 207 grasslands and savannas 278–279 greenhouse effect and biodiversity 296, 297

xviii+598_Biodiversity_F.indd 579

ice ages 318 mass extinctions 372–375 Ordovician period 397 Permian extinction 407–410 Permian period, biodiversity in 412 Pleistocene extinction 414–417 Quaternary period, biodiversity in 452 restoration ecology 462 Silurian period, biodiversity in 489 succession, ecological 501, 506 Triassic period, biodiversity in 524 extractive preserves 533, 534 extraterrestrial impact 152 extremophiles 32, 33, 43, 134 eyes animals 26 arthropods 35 biomimicry 83 convergence 145, 148 fishes 246, 249 insects 320, 324 mammals 366 reptiles 457, 458 spiders 497 eyespots 24

F

Fabaceae 145, 186, 394 Fagaceae 73, 74, 185 Fagus 73 Fagus crenata 516 Fagus grandifolia 185–186, 504, 513 Falconiformes 89 falcons 89 Falkowski, Paul 42 family (taxonomic) 78 Famitsyn, Andrey S. 508 fan palms 179, 195 FAO. See United Nations Food and Agriculture Organization farming 10–11 fat accumulation 482 feathers 5, 84–86, 85, 86, 193, 480 federal government role in conservation (United States) 238–244, 240t–241t federal wildlife refuges 548c feedlot runoff 422, 423 Feeny, Paul 303 feet 16 Felis catus 12 fen 91 feral animals 12, 501 feral livestock 330 feral pigs 12, 333 Fergusobia curriei 27 fermentation 262 ferns 475, 476 Carboniferous period, biodiversity in 105 deserts, warm 177 Permian period, biodiversity in 412 seedless plants 472, 473, 475–476 succession, ecological 505 Triassic period, biodiversity in 524 fertile hybrids 310 fertility rates 425–427 fertilization agriculture 13 amphibians 18 animals 21, 26, 27 arthropods 35 birds 87 fishes 246, 249 flowering plants 252, 253 reptiles 455 seedless plants 472–476 sexual selection 479, 484 speciation 491, 494 fertilizer runoff 466 Ficus 186

fiddleheads 475 Field, Christopher 291 figs 52, 186 filaments 41 filarial worms 31 filmy ferns 476 filter feeders 22, 28, 171 finches 8, 167–169, 271–274, 335 Fincke, Ola 481 Finland 304 fins 15, 16, 246–249 fir(s) 2, 92, 94, 137, 511, 518 fire ants 325, 328, 331, 332, 545 fire cycle 128, 201t firefly beetle 99 fire poppy 487 fires grasslands and savannas 274, 276 greenhouse effect 286, 287 restoration ecology 461 shrublands 486, 487 succession, ecological 500–502 temperate deciduous forests 516 fire suppression 200, 201, 462 firewood 289 Fischbach, Michael 67, 68 fish(es) 244–251, 245t, 246, 248–250 adaptive radiation 6–7 amphibians 15, 16, 18 animals 30 biomagnification 81 Cambrian period, biodiversity in 96–97 camouflage and mimicry 99 Carboniferous period, biodiversity in 105 cladistics 113 coevolution 122 convergence 146, 147 Cretaceous period, biodiversity in 154 deep oceans, biodiversity in 170, 171 Devonian period, biodiversity in 182–184 disjunct species 196 endemic species 222 greenhouse effect and biodiversity 297 hybridization 308 invasive species 331 Jurassic period, biodiversity in 341 keystone species 345 life history, diversity of 350, 353 living fossils 356 mutualism 380, 381 Neogene period, biodiversity in 393 Ordovician period 397 Paleogene period, biodiversity in 399 Permian extinction 408 Permian period, biodiversity in 412 restoration ecology 462 rivers, streams, ponds, and lakes 467 sexual selection 481 Silurian period, biodiversity in 488 succession, ecological 501 Fish and Wildlife Service, U.S. (FWS) 219, 220, 241 fish breeding grounds 372 Fisher, R. A. 430, 431, 434, 479 fishing 150 fishing spiders 467, 497 fishopod 16, 16 fitness indicators 479–480, 482–483 FitzRoy, Robert 54, 162, 163 flagella 22, 32, 40, 261, 448, 509 flatfishes 249 flatworms 24, 29, 467 fleas 38, 323, 403, 404 fleshy-finned fishes 15, 247, 249 flies 321 arthropods 38 Cretaceous period, biodiversity in 155 insects 323, 324

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580 Index 580 tundra  Permian period, biodiversity in 412 pollination 420 sexual selection 481 speciation 492 flight 85, 146–147, 193, 320 flight feathers 86, 86t flightless birds 87, 173 flight muscles 86 Flint’s Pond 521 flippers 365 flood control 242 floodplain habitats 200 flood prevention 215, 216 floods 465, 466 flora 57 Flores Island people 75, 387 florets 188 Florida 75, 137, 222, 369, 389, 493 Florida Keys 546 flounder 249 flower(s) 188, 252, 252, 418, 419, 538 flowering plants (angiosperms) 252, 252– 256, 253, 255 adaptation 6 biodiversity, patterns of 51, 52 biodiversity, quantification of 56 biogeography 74t, 75 biological classification 80 camouflage and mimicry 99 carnivorous plants 106–107 cladistics 109, 110, 113t, 114 coevolution 119–121 convergence 144 Cretaceous period, biodiversity in 154 deserts, polar 174 deserts, warm 177 dicots 184–189 dinosaurs 193 endemic species 221 greenhouse effect and biodiversity 298 living fossils 356 marshes and swamps 371 monocots 375–377 parasitism 402–403 pollination 417–420 seed plants 478 speciation 494 flukes 24–25, 29–30 Flustra 162 flying fishes 248 flying foxes 366 flying mammals 365–366 fog 177, 518 fogslimbs 457–458 foliose lichens 348 follicle mite 36 food chain 71, 208t bacteria 42 biodiversity, patterns of 48, 50 biogeochemical cycles 72 biomagnification 80–82 Cretaceous extinction 151, 152 deep oceans, biodiversity in 171–172 ecology 205, 206 ecosystems 212 invasive species 333 keystone species 343 predation 439 food chain disruption 298 food energy 210 food processing 42 food production x, 10, 14, 381, 390–392 food resource specialization 493–494 food web 101, 170, 205, 209, 466 foraging 51 foraminiferans 448 Forbes, Andrew 49, 50 forbs 127–128, 199, 274, 275t, 276 Ford, Henry 389 forest(s) 504. See also specific forests, e.g.: temperate coniferous forests

xviii+598_Biodiversity_F.indd 580

first entry acid rain and fog 1–2 biogeography 73, 76 boreal and subalpine forests 91–94 carbon cycle 103 Cretaceous period, biodiversity in 154–155 ecosystem services 213 greenhouse effect 292 Permian extinction 408 succession, ecological 500 forest destruction 289–290 Forest Reserve 548c Forestry, Division of 548c Forest Service, U.S. 239, 347, 413, 414 forest succession 522 fossa 527 fossil fuels 14, 103, 210, 225, 227, 280, 289, 291, 293t, 501. See also coal; petroleum fossil record 148, 408 fossils and fossilization 42, 163, 190, 191, 217–218, 256–259, 257 founder effect 4, 75 founder effect and genetic drift 259–260 foxes 330 foxfire 370 foxtail pines 137 Fraenkel, Gottfried 116 Fragaria 186 France 60 Frankia 394 Frankia bacteria 42 Franklinia alatamaha 233 Franz Josef Land 174 Fraser firs 94 frequency-dependent selection 387 freshwater fish 196, 341, 452 freshwater marshes 369 freshwater mussels 467 freshwater pools 437 freshwater swamps 369–370 fringing reefs 149 Frizte, Jessica 229 frogs x, 18 adaptation 6 amphibians 15, 17, 18 biodiversity, resources for medicine 66–69 Cretaceous period, biodiversity in 155 deserts, warm 180 predation 436 sexual selection 481 Triassic period, biodiversity in 524 fronds 475, 475, 476 frugivorous animals 133 fruit biodiversity, resources for agriculture 61 coevolution 118–119 competition, ecological 133 dicots 186, 187 flowering plants 252 herbivory 305 seed dispersal 470–471 fruit flies biodiversity, resources for medicine 68 founder effect and genetic drift 258 insects 324 life history, diversity of 353 population genetics 430 sexual selection 479 speciation 490, 493, 494 fruit toxins 117–118 Frutafossor 341 fruticose lichens 348 Fucus 447 Fuegian people 163 Fugitive Slave Act 521 Fukashi, Tadami 134 Fulton, George 369

fungi 259t, 260–265, 260t, 261, 262, 262t, 263t agriculture 8–9 biodiversity, resources for agriculture 62 biodiversity, resources for medicine 64–67 biological classification 78, 79 camouflage and mimicry 98 coevolution 122 competition, ecological 133 decomposers 170 DNA studies of biodiversity 202 eukaryotes 232 extinction 234 greenhouse effect and biodiversity 297 keystone species 344–345 lichens 347–349 mutualism 379–381 parasitism 402 predation 438 temperate deciduous forests 516 fungus beetle 324 funnel-web spiders 498 Fusarium fungus 297 Fusarium oxysporum 62 Future of Life, The (Wilson) 545, 546 FWS. See Fish and Wildlife Service, U.S. fynbos 486

G

Gadsden Purchase 238 Gadus morhua 172 Gaia 223, 266–271 galagos 441 Galápagos Islands 271–273, 272t adaptive radiation 8 agriculture 12 biogeography 76 competition, ecological 134 Darwin, Charles 163 Darwin’s finches 167–169 endemic species 221 Grant, Peter and Rosemary 273–274 island biogeography 335 speciation 490, 491, 493 Galápagos tortoise 379, 455, 456 gall bladder 66 Galliformes 89 Gallornis 156 Galloway, Laura 3 galls 403 Gallus gallus 89 gall wasps 389 Galton, Francis 544 Gambusia 331 gametes 20 gametophytes 447, 472–477 gamma diversity 126, 128–129 Gandhi, Mohandas 521 Garden of Eden 224 garrigue 486 gars 247, 250 garter snakes 438 Gasterosteus aculeatus 481 gastric brooding frogs 68–69 gastroliths 86, 190, 257, 455 gastropods 25, 26 Gastrotricha 28 Gaviiformes 89 gazelles 173 Gecarcoidea natalis 156, 157 geckos 83, 457 geese 89 gene(s) 17, 69, 231, 353–354 gene flow 489–490 generalists 208 General Land Office 238, 239 General Sherman Tree 136 Generelle Morphologie der Organismen (Haeckel) 548c

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tundra  Index 581 genetically modified organisms (GMO) 12–14 genetic bottleneck 4, 234, 258–259 genetic diversity 233, 258 genetic drift 4, 75. See also founder effect and genetic drift genetic engineering 59 genetic extinction 59–60 genetic pollution 12 genetics 430–435 genetic variability 3–5, 301, 353, 388, 430–435 gene transfer 310–311 gene variation 203 genotypes 430 Genovesa 169, 273 genus (pl. genera) 78 geographical isolation 301, 489, 490 geological deposits 407 geometric series 55 Georgia 137, 194, 195, 221, 222, 233 Geospiza conirostris 169 Geospiza fortis 168, 169 Geospiza magnirostris 169 Geranium viscosissiumum 418 Germany 2, 257 germ cells 353 germline cells 384 Gerridae 467 gestation period 351–352 GFP (green fluorescent protein) gene 69 gharials 456 GHGs. See greenhouse gases ghost shark 247 giant armadillo 367 giant-flowered phacelia 487 giant golden-crowned flying fox 366 giant moray eel 248 giant redwood 222 giant sequoia 136, 354, 502, 511 giant tortoises 221, 455, 456 Giardia lamblia 445 giardiasis 445 Gibberella zeae 263 gibbons 537 Gibson, J. Phil 194 gila monsters 457 Gill, Jacquelyn 416 gills 16, 17, 34–35, 467 gill slits 29, 245, 247, 250 Ginkgo biloba 222, 233, 478 ginkgoes 222, 233, 341, 356, 478 giraffes 5, 5 gizzards 86 glacial retreat 316 glaciations 49, 95–96, 411 glaciers 76, 201, 282–286, 289, 315–316, 450, 452 glands 5 glass snakes 457 glaucoma 67 Gleason, Henry 125 Gleditsia aquatica 119 Gleditsia triacanthos 118, 119, 186 global climate change. See global warming global conveyor current 284 global temperature 279–284, 280t, 282t, 311, 398 global warming x amphibians 18, 19 boreal and subalpine forests 94 coral reefs 150 deserts, polar 174 ecosystems 211 ecosystem services 216 environmental ethics 224 extinction 234, 235 Gaia 269, 270 greenhouse effect 279–280, 282, 285–287, 290

xviii+598_Biodiversity_F.indd 581

greenhouse effect and biodiversity 296–298 herbivory 305 mass extinctions 373–375 Permian extinction 408–410 Permian period, biodiversity in 411 restoration ecology 462, 464 tropical rain forests and deforestation 534 tundra 540 Glomeromycota 263 Glossopteris 412, 524 glue 66 glutin 310 glyphosate 460 glyptodonts 450 GMO. See genetically modified organisms Gnathostomulida 28 Gnetales 253, 478 goats 12, 273 goatsbeard 492 Gobi Desert 173 gobies 249 goblet worms 27 God 224, 225 golden eagle 219 golden rain tree 389 goldenrod 431 golden toad 18, 116, 235, 297 gold extraction 533 goldfish 248 Goliath birdeater 498 goliath frog 17 Gondwana/Gondwanaland Carboniferous period, biodiversity in 105 Cretaceous period, biodiversity in 154 Devonian period, biodiversity in 182 ice ages 315 Jurassic period, biodiversity in 339 Ordovician period 397 Triassic period, biodiversity in 523 Goodall, Jane 443 Goosen, Hendrick 249 Gore, Al 358 gorillas 223, 235, 443, 444, 481 Gould, John 167 Gould, Stephen Jay 33, 42, 148, 546 Graham, Linda 488 grains 10, 60–62, 209 grama grasses 198 gram-negative bacteria 40 gram-positive bacteria 40 Gram’s stain 40 Grand Canyon 344 grandmother hypothesis 354 Grant, Peter and Rosemary 168–169, 271, 273–274, 432, 493, 494 Grant, Robert 161 grapes 60, 187 grasses 129 agriculture 12 biodiversity, resources for agriculture 61 biogeography 74 coevolution 117, 122 communities, ecological 127–128 convergence 144 deserts, cool 173 deserts, warm 180 disturbances, ecological 198 grasslands and savannas 277t greenhouse effect and biodiversity 296 hybridization 310 invasive species 332–333 monocots 376–377 Neogene period, biodiversity in 393 succession, ecological 504 grasshoppers 13, 38, 181, 321 grasslands and savannas 199, 274, 274– 279, 275t, 276, 277t–278t, 504 biodiversity, patterns of 49

biogeography 76 carbon cycle 103 deserts, cool 173 dicots 186 disturbances, ecological 198–199 greenhouse effect 292 keystone species 343 monocots 377 restoration ecology 461 temperate dry forests 517 grass lizards 457 grass stems 303 Gray, Asa 166 grazing animals 276, 278–279, 343, 360, 363, 377, 538 great ages 442–443 Great Basin Desert 173, 511 Great Basin system 465 Great Britain 76, 171, 217, 258, 296, 298, 486, 487 Great Chain of Being 78, 356 Great Lakes 316, 331 Great Lakes system 465 Great Outback 175 Great Oxidation Event 95 Great Pacific Garbage Patch. See Pacific Trash Vortex Great Plains 76, 241, 279 Great Smoky Mountains 55, 56t, 313 great white sharks 247, 249 green algae 109, 110, 348, 448, 472 Green Belt Movement 358–359 greenhouse effect 279–295, 280t, 281, 282t, 283, 284t, 288t, 292t, 293t, 549c greenhouse effect and biodiversity 295– 300 biogeography 76 carbon cycle 102, 103 cloud forests 116 ecology 205 environmental psychology 229 Gaia 268–270 ice ages 318 restoration ecology 462 succession, ecological 501 tropical rain forests and deforestation 534 greenhouse gases (GHGs) 14, 205, 286– 290, 311, 395, 409–410. See also carbon dioxide, atmospheric; methane Greenland 174 Greenland ice sheet 283–285 green landscaping 228, 229 green protists 448 green spider orchid 99 green sulfur bacteria 43, 44 Grime, Philip 350 grizzly bear 311 grolar bear 311 Grosberg, Rick 52 Gros Michel banana 62 gross primary production 210m ground finches 168, 169 ground pink (wildflower) 487 groundwater 312–313 groundwater recharge 215 growth patterns 354 grubs 389 guanacos 173 guars 220 guevedoche 435 Gulf Coastal system 214, 465 Gulf of Mexico 142–143, 172 Gulf of Mexico oil spill (2010). See BP Deepwater Horizon oil spill Gulf Stream 171, 284, 285, 311, 316 gulls 89 gumbo limbo tree 369, 515 guppies 389–390, 437 Gymnocladus dioicus 516 Gymnophthalmidae 458

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582 Index 582 tundra 

first entry

gymnosperms 135, 154–155, 180, 253, 341, 477–478 Gymnothorax javanicus 248 gypsy moth 324 Gyrinidae 467

H

habitat animals 20 biodiversity, patterns of 52 bogs, life in 90–91 disturbances, ecological 200, 201 endemic species 222 population biology 426 rivers, streams, ponds, and lakes 466 succession, ecological 499 habitat conservation 139, 251, 372 habitat creation 344 habitat destruction x, 12–13, 60, 103, 234, 374, 463 habitat disruption 139 habitat expansion 297 habitat fragmentation 12–13, 301–302 Habronestes bradleyi 498 Habropoda pallida 98–99 Hackett, Shannon J. 87 Hadley cells 176 Hadronyche formidabilis 498 hadrosaurs 155 Haeckel, Ernst 548c hagfish 69, 246 Haikouichthys 97, 245 hair(s) 303, 359–360 hairgrass 174 Haldane, J. B. S. 324, 434 halibut 249 Hallucigenia 97 hallucinogens 264 halophiles 33 halteres 147, 323 Hamilton, William 480 hammerhead sharks 246 handicap principle 480 hands 16 Hansen, James V. 220, 285, 549c haplodiploidy 325 haploid cells 252, 260, 325, 472, 477 Haplorrhini primates 366 haptophytes 447 Hardin, Garrett 429 hard skeletons 95, 96 Hardy, G. H. 433 Hardy-Weinberg equilibrium 433–435, 433t Harmonia axyridis 331 Hartnett, David 264 harvestmen 35 Hasselquist, Frederik 355 hatchetfishes 248 Hautier, Yann 49 Hawaiian goose 234, 258 Hawaiian Islands adaptive radiation 7–8 agriculture 12 biogeography 76 continental shelves, biodiversity on 142 endemic species 221 invasive species 332–333 speciation 490, 492, 493 succession, ecological 505 Hawkes, Kristin 354 Hawkins, Bradford 48 hawkmoth 324 hawthorns 119 Hay, Mark 381 Hayden, Ferdinand V. 239 hazel alder 194, 308 hazelnuts 78 heading 11–12 heads 24, 37, 456, 457 health 11, 58, 229, 378–379, 460, 482

xviii+598_Biodiversity_F.indd 582

heartbeat 86 hearts 360, 455 heath bushes 91 heather 487 heather shrub 196 heath plants 110 Heavenly City 225 heavy metals 72, 84, 224, 502 hedgerows 13 heirloom varieties 59 Helianthus 492 Helianthus annuus 310 Helianthus anomalus 310 Helianthus deserticola 310 Helianthus maximiliani 61 Helianthus paradoxa 494 Helianthus petiolaris 310 heliconid butterflies 45 Heliconius 117 Helicoprion 412 Heloderma suspectum 457 Hemachatus haemachatus 457 Hemiaulus haukii 381 hemichordates 29 hemimetabolous development 321 hemiparasitic figs 52 Hemiptera 322–323 hemlocks 128, 137, 504, 511, 516 Hemochordata 29 hemocyanin 26 hemoglobin 15 hemolymph 320 Hemphillian extinction 374 Hennig, Willi 109 Henslow, John Stevens 162 herbaceous plants 254–255, 296, 375–376, 403 herbicides 13–14, 18, 423, 459–460 herbivory 302–307, 304t adaptation 5 agriculture 12 coevolution 117, 122 communities, ecological 126, 130 competition, ecological 132 dinosaurs 191 ecology 205 ecosystems 208–209 Janzen, Daniel H. 338 Jurassic period, biodiversity in 341 keystone species 343, 344 mammals 365 marshes and swamps 370 Triassic period, biodiversity in 524 herbs 187 herds 436–437 heritability 431 heritable diversity 424 hermaphroditism 18, 252 hermit crabs 156 Herrerasaurus 191 herrings 248 Hesperornis 156 Hetch Hetchy reservoir 378 heterocysts 394 heterokonts 446–447 heterotherms 17, 250, 455 heterozygous organisms 258, 430, 432, 434 Hevea brasiliensis 188 Heyburn, Weldon 414 hibernation 206 Hibiscus liliflorus 235 Hibiscus moscheutos 484 hickories 186, 515 high-elevation tropical forests 115–116 high-input system 13 Hill, Julia Butterfly 520 Hillis, Daniel 114 Himalayas 89, 398 Hines, Bob 108 Hipparion 393 Hippocampus 249

Hippocampus bargibanti 250 hirudin 66 Histoire Naturelle (Leclerc) 548c histones 32, 230, 231 Historia Naturalis (Pliny the Elder) 548c Historia Plantarum (Theophrastus) 548c histrionicotoxin 17 HIV/AIDS 67, 68, 114, 262 Hogberg, Peter 264 Hohokam culture 461 Hölldobler, Bert 545 holometabolous development 321 homeotherms 86, 147, 250, 360, 367 Homestead Act 238 Hominidae 443 hominins 443–444 Homo 318, 444 Homo caudatus 356 Homo erectus 75 Homo ergaster 438 Homo ferus 356 Homo floresiensis 75, 387 Homo habilis 114, 438 Homo neanderthalensis 318 homoplasy 110, 111 Homoptera 38, 323 Homo sapiens 58, 227, 318, 351–352, 444 homozygous organisms 430, 432, 434–435 honeybees 38, 215, 326, 332, 421 honeydew 323 honey locusts 118, 119, 186 hooded tickspiders 36 Hoodia gordonii 182 Hooker, Sir Joseph 165 Hoplostethus atlanticus 172 hopping-mouse 181 horizontal gene transfer 40, 231 hormonal conflict 352 hormones 231 horns 470 hornworms 324 hornworts 474 horse(s) 12, 56, 308, 393, 400, 452 horse apples 119 horsehair worms 28 horseshoe crabs 37, 46, 67, 356, 356 horseshoe worms 27 horsetails 105, 472–475 horticultural therapy 228 host density 327 hosts 403 hot spots. See biodiversity hot spots Hottonia inflata 125 house fly 324 hox genes 17 Hubbard Brook, New Hampshire 197, 312 Hubbell, Steven 52, 129 human activities x biogeochemical cycles 72 biogeography 76–77 boreal and subalpine forests 94 carbon cycle 101, 103 ecosystems 211, 212 environmental psychology 228 extinction 235 Gaia 269 greenhouse effect 289–290 habitat fragmentation 301 mass extinctions 374–375 Permian extinction 410, 417 succession, ecological 501–502, 506 human body 42–43 human brain 110, 483, 545 human civilization 298 human evolution 166, 482–483 human flea 38 human population 425–426 Humboldt, Alexander von 47, 50, 307, 548c Humboldt Current 307 humidity 280 hummingbirds 86, 89, 120, 418

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tundra  Index 583 hunter-gatherers 9, 10, 57–58 hunting 220, 234, 414, 415, 417, 438–439, 483 hurricanes 286 Hut, Piet 373 Hutchinson, G. Evelyn 50–51, 132, 549c Huxley, Julian 18 Huxley, Thomas Henry 165, 166 Hyalymenus tarsatus 98 hybridization 12, 61–62, 169, 307–311, 308t–309t, 391, 491 hybrid vigor 307 hydrogenosome 509 hydrogen sulfide 42, 269 hydroid cells 474 hydrological cycle 212, 311–314, 312, 313t hydrostatic skeleton 147 hydrothermal vents 172, 549c hyenas 132–133 Hylonomus 106 Hymenophyllaceae 476 Hymenoptera 38, 325–326, 524 hyomandibular bone 16 hypertonic 250 hyphae 260–264 hypotonic 250 hypsithermal 317 hyraxes 367 Hyrocotherium 400

I

ice 96, 175, 218, 282, 285, 312 ice ages 315–318, 317m biodiversity, patterns of 49 biogeography 76–77 boreal and subalpine forests 92 disjunct species 195, 196 disturbances, ecological 197, 201 Ediacaran organisms 218 fossils and fossilization 258 Gaia 270 grasslands and savannas 274, 278 greenhouse effect 282, 289 Quaternary period, biodiversity in 450, 452 tundra 537 ice cores 152, 282–284, 283, 284t Icerya purchasi 328 ice sheets 268 ice shelf 283 Ichthyornis 156 ichthyosaurs 154, 524 Ichthyostega 17 Ichthyostega stensioei 16 Idaho 256 iguanas 272 Iguanodon 341 Illinois 128 illness 164 Iltis, Hugh 234 immune system 69, 362, 405 Impatiens 470 inbreeding 164, 434–435 incense cedar 137 incipient speciation 169 incus 361 India biogeography 73 Cretaceous period, biodiversity in 154 deserts, warm 175 IPM 328 Paleogene period, biodiversity in 398 reptiles 456 tropical rain forests and deforestation 527 tropical seasonal forests 537 Indiana Dunes National Lakeshore 504 Indian cobra 457 Indian Ocean 249 Indian pipe 403

xviii+598_Biodiversity_F.indd 583

indigobirds 491 Indochina 537 Indonesia biodiversity, patterns of 52 biogeography 75 fishes 249 IPM 327 reptiles 457 tropical rain forests and deforestation 527, 534 Wallace, Alfred Russel 542, 543 Industrial Revolution 280 indy gene 353 infant mortality 426, 427 infections 68, 262 infectious disease 428 infrared photons 205, 206 infrared radiation 211, 287 inheritance 369, 386, 548c Inhofe, James 226 In Memoriam (Tennyson) 386 Inouye, Isao 510 insect eggs 21 insecticides 59 insectivores 366, 367 insects 318–327, 319t, 321, 322, 325 adaptation 6 agriculture 13 animals 27 arthropods 35, 37–38 Bates, Henry Walter 45–46 biodiversity, patterns of 52 biodiversity, quantification of 54 camouflage and mimicry 98, 100 Carboniferous period, biodiversity in 105 coevolution 116, 117, 120–121 convergence 145–147 Cretaceous period, biodiversity in 155 DNA studies of biodiversity 203 flowering plants 253 fossils and fossilization 256 herbivory 302–303 Jurassic period, biodiversity in 341 marshes and swamps 370 natural selection 389 parasitism 403 Permian extinction 407 pollination 419 population biology 427 predation 436 resistance, evolution of 459, 460 rivers, streams, ponds, and lakes 466, 467 sexual selection 480 succession, ecological 500 Triassic period, biodiversity in 524 Wilson, Edward O. 545, 546 Insect Societies, The (Wilson) 546 insect vectors 405 instars 37, 321 insurance companies 214 integrated pest management (IPM) 327– 329 Integrated Taxonomic Information System 57 interference competition 132, 133 Intergovernmental Panel on Climate Change (IPCC) 281, 282, 287, 290 Interior, Department of the 238, 239, 241, 242, 244 internal fertilization amphibians 18 animals 21, 26, 27 arthropods 35 birds 87 fishes 246 reptiles 455 internal membranes 230 International Society for Phylogenetic Nomenclature 80

International Union for the Conservation of Nature (IUCN) 218, 235 interspecific competition 132 intertidal zones 133, 142 intestinal bacteria 378–379 intestines 5, 32, 43 intraspecific competition 132, 428 introgression 311 invasive species 329–335, 330, 331t–332t, 333 agriculture 12 amphibians 18 herbivory 305 IPM 328 marshes and swamps 372 restoration ecology 462, 463 temperate dry forests 518 invertebrates animals 20, 29–31 Carboniferous period, biodiversity in 105 continental shelves, biodiversity on 142 convergence 147 Cretaceous period, biodiversity in 154, 155 deep oceans, biodiversity in 170 Devonian period, biodiversity in 182 Ediacaran organisms 217 fossils and fossilization 256, 257 Jurassic period, biodiversity in 341 Neogene period, biodiversity in 392, 393 Ordovician period 396–397 Paleogene period, biodiversity in 398–399 Permian period, biodiversity in 411, 412 population genetics 431 Quaternary period, biodiversity in 450, 452 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523, 524 iodine 71 IPCC. See Intergovernmental Panel on Climate Change IPM. See integrated pest management Ireland 446 Iridaceae 376 iridium anomaly 152, 374 Iridomyrmex purpureus 498 irises 376 Irish Potato Famine 501 iron 71, 212 irrigation 463, 464 Irwin, Terry 54 Islam 224, 225 island biogeography 75–76, 221, 335–337, 471, 490, 546 isolating mechanisms 489–490, 492–494 isopods 158 isoprene compounds 101 Isoptera 38, 322 isotonic balance 250 isotope ratios 258, 407–408 iteroparous species 350 IUCN. See International Union for the Conservation of Nature Ixodes damminnii 36 Ixodes pacificus 404 Ixodes spinipalpis 404

J

Jablonski, David 148 jack-in-the-pulpit 376 jack pine 92 jackrabbits 181 Jackson, Andrew 238 Jackson, Wes 62, 83, 226, 338, 391

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584 Index 584 tundra 

first entry

Jackson, William Henry 239 Jadera haematoloma 389 Janzen, Daniel H. 52, 338–339 Japan 52, 81–82, 137, 141, 263, 516 Japanese beech 516 Japanese black pines 511 Japanese brome 278 Japanese persimmons 60 Java Man 75 jawless fishes 96–97, 154, 183, 245–246, 397 jaw worms 28 jays 118–119 Jefferson, Thomas 307 Jeffrey pines 511 jellyfish 23, 23, 24 Jenkin, Fleeming 165 Jeon, Kwang 509 Jesus Christ 225 jet propulsion 26 jewel weeds 470 jock itch 262 Johnson grass 12, 61 jojoba 61 Jomon Sugi tree 137 Joshua tree 175 Judaism 224, 225 Judson, Olivia 166 Juglandaceae 186 Juglans 113, 186 Juglans nigra 425 jumping spider 496, 497 Juncaceae 377 juniper shrubs 137 Juniperus 137 Juniperus ashei 200, 331 Juniperus virginiana 200, 313, 331 Jurassic period, biodiversity in 84, 85, 87, 193, 339–342, 340t, 341, 361–362, 454, 477 Justice Department, U.S. 142

K

Kaibab Plateau 344 Kalahari Desert 175 Kalm, Peter 355 kangaroo 362, 363 kangaroo mice 6 kangaroo rats 181 Kansas 61 kapok tree 527 Karoo Basin deposits 408–409 Karpechenko, Georgi 310 katydids 98, 99 Kauai 7 Keeling, Charles 288 Keiferia lycopersicella 328 kelp forests 141, 142, 447 Kennedy, Edward 358 Kentucky coffee trees 516 Kenya 358–359 Kepenomamus robustus 361 Kessler, Danny 420 Kettlewell, H. B. D. 168 keystone species 343–346 biodiversity, concept of 46 continental shelves, biodiversity on 141 marshes and swamps 370 Pleistocene extinction 417 rivers, streams, ponds, and lakes 467 temperate rain forests 520 Kimura, Mot[o] 434 kinetic energy 206 King, Martin Luther, Jr. 521 kingdom (taxonomic) 78–79 kingpin principle 389 king snakes 457 King Tut’s Curse 264 Kinorhynchia 28 Kirschenmann, Fred 13

xviii+598_Biodiversity_F.indd 584

kiwis 87–89 knockout mice 68 Knoll, Andrew 95 knotweed 133 knowledge 354 Knowlton, Nancy 150 koalas 304–305, 363, 518 Kok-Aral Dam 464 Komodo dragons 457 Korarcheota 33 Kosmos (Humboldt) 307 Kozo-Polyansky, Boris M. 508 krill 157–158, 170 krummholz trees 92, 540 Küchler, A. W. 461 kudzu 333, 333 Kump, Lee 373 Kuo, Frances E. 229 kwolu-aatmwol 435 Kyoto Protocol 549c

L

labellum 376 laboratory animals 27 Labrador 171 Labroides dimidiatus 380 Lack, David 167, 271 Lacks, Henrietta 353 lactation 360 Lactobacillus 43, 379 lactose digestion 148 Lactrodectus hasseltii 498 Lactrodectus mactans 498 ladybird beetle 331 ladybug beetles 325 Lagenidium callinectes 380 Lagerstätten 257 lakes. See rivers, streams, ponds, and lakes lake sturgeon 356 Lama guanicoe 173 Lamarck, Jean-Baptiste de 161, 548c Lamarckia aurea 128 Lamarckian evolution 161, 162, 386 Lamellibrachia luymesi 172 Lamiaceae 188, 487 Laminaria 141 lampreys 69, 246, 246, 250 Lamprocyphus augustus 83 lampshells 27, 374 Lampsilis perovalis 467 Lampyridae 325 Lanai 7 lancelets 29, 245 land crab 156 land degradation 461 land ethic 226, 347 land iguanas 272 Land Institute, The 61, 62, 226, 338 Land Management, Bureau of 241 land nationalization 544 land rights 533, 534 landscaping 228 La Niña 171, 280, 284 larches 91, 137, 195 Larix 137 Larix decidua 91 Larsen B ice shelf 283 Larus 494 Lassen Peak, California 540 Late Precambrian 95–96 Lates niloticus 332 late-successional habitats 499, 500 latex 144 Laticauda colubrine 98 Latimeria chalumnae 249 Latimeria menadoensis 249 Latin America 62, 548c Laurasia 103, 105, 339, 523 Laurentia 396 lava 505

lava lizards 272 LD50 (lethal dose, 50%) 306 leaching 530 lead 84 leaf area 177 leaf-cutter ants 8–9, 122, 264, 380 leaf-cutter bee 421 leaf insects 321–322 leaf litter frog 98 leaf structure 371 Leakey, Mary 258 learning 158–159 least tern 196 leatherback sea turtle 455 leaves adaptation 3 biodiversity, resources for medicine 66 boreal and subalpine forests 92 conifers 135–136 convergence 144, 145 deserts, warm 177 dicots 185–187 ecology 206 flowering plants 254 fossils and fossilization 256, 258 herbivory 303, 304 marshes and swamps 371 monocots 376–377 rivers, streams, ponds, and lakes 467 temperate deciduous forests 513 tropical seasonal forests 537 Leclerc, Georges-Louis. See Buffon, Georges-Louis, comte de leeches 66 leg bones 15, 17 legumes 13, 42, 61–63, 145, 186, 394 leks 480 Lemnaceae 467 lemurs 441 Leonardo da Vinci 256 Leopold, Aldo 224, 226, 344, 347, 549c Lepidodendron 105, 473, 474 Lepidoptera 37–38, 324, 341. See also butterflies; moths lepidosaurs 87, 454 lepirudin 66 Lepomis cyanellis 308 Lepomis macrochirus 308 Leptinotarsa decemlineata 325 Leptotyphlops 457 Lepus americanus 438 Lepus californicus 181 lesser apes 442 lethal recessive allele 434, 435 Leucaena leucocephala 63 leucaena tree 63 Leucochrysum fitzgibbonii 177 leukemia 66, 353 Lewis, Martin 227 Lewontin, Richard 546 lianas 513, 526 lice 38, 322, 403 lichens 84, 262, 264, 347–349, 348, 381 life history, diversity of 349–355, 350t, 352t Life magazine 338 Likens, Gene 2, 312 lilacs 296 Liliaceae 375–376 lilies 375, 420 limber pine 92, 196 lime sediments 448 limestone 1, 102, 257 limnetic zone 468 limonene 144, 148 Limulus polyphemus 37, 46, 67 Linanthus dianthiflorus 487 Linanthus montanus 253 Lindeman, Ray 208, 212 linden 506 Lingula 27, 407, 408 Linnaea borealis 356

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tundra  Index 585 Linnaean system of classification 77–80, 113–114, 232 Linnaeus, Carolus 77, 355–356, 548c lions 112, 132, 133, 308 Lithops 98 Little Ice Age 281 littoral zone 468 live birth 147, 246, 359, 455 live oak 6, 185, 309, 369, 513 liver 80, 81, 250 liver flukes 29–30 liverworts 473 Lives of a Cell (Thomas) 266 livestock 12, 13, 63, 210, 381, 501 livestock feed 13, 209, 210 living fossils 356, 356–357, 357t lizard-hipped dinosaurs 191 lizards 83, 106, 272, 341, 389, 454–458 Lobatae 73 lobe-finned fishes 105, 183–184 Lobocraspis griseifusa 324 lobsters 157, 341 locoweeds 84, 186, 303 locus 430 locusts (insect) 13, 38 locust trees 118, 119, 186 lodgepole pines 200, 511 Löfling, Pehr 355 logging 94, 239, 520, 533 log-normal distribution 55 Loiseleuria procumbens 174 Lompoc, California 258 Longfellow, Henry Wadsworth 201 long-horned beetle 324 long-term carbon cycle 101–103 long-term mineral cycle 70, 71, 212 Lontra canadensis 370 loosestrife 333 Lophelia pertusa 149 lophophores 27 Loricifera 21, 28 lorises 441 Losos, Jonathan 389 Louisiana Purchase 238 Lovelock, James 223, 266 lower jaw 361 Loxosceles reclusa 498 LSD (lysergic acid diethylamide) 264 Lubchenco, Jane 72 luna moths 325 lungfishes 105, 183–184, 247, 249, 341, 412 lungs 16, 17, 86, 250, 455, 456 Lycopersicon esculentum 188 Lycopodiophyta 474 Lycosidae 498 Lyell, Sir Charles 163, 165, 542–543 Lygodium 476 Lymantria dispar 324 Lyme disease 40, 404 lynx 438 Lynx canadensis 438 lysates 67 Lyssopimpla excelsa 420 Lystrosaurus 409, 524, 524 Lythrum salicaria 330

M

Maathai, Wangari 358–359, 359 Macaca sylvanus 518 macaque 518 Macaranga 380 MacArthur, Robert H. 51, 335, 546 MacArthur distribution 55 MacDonald, Julie 220 Maclura pomifera 118, 186, 527 Macrochelys temminckii 370 Macrocystis 141, 447 Macropus rufus 363 Madagascar 66, 87, 221, 222, 457, 527 mad cow disease 210

xviii+598_Biodiversity_F.indd 585

Madeira 313 maggots 38, 170 Magnaporthe grisea 263 magnesium 70, 72 Magnolia grandiflora 515 magpie robin 234 maidenhair ferns 475 maidenhair tree 478 maize 9, 11, 12, 58, 60, 234, 381, 484 Malaclemys terrapon 455 Malacostraca 157–158 Malagasy people 457 malaria 67, 305, 324 Malawi, Lake 6 Malay Archipelago, The (Wallace) 542 Malaysia 456, 527 mallee 486 malleus 361 Mallophaga 322 Malthus, Thomas 164, 165, 351, 425, 548c Malus 186 mammals 79, 359–368, 362, 364t, 365– 367, 393, 401. See also specific mammals, e.g.: bison adaptation 3 adaptive radiation 8 biodiversity, patterns of 48, 49 biogeography 74–76 biological classification 78 boreal and subalpine forests 93t cladistics 110 convergence 145, 146t, 147 Cretaceous extinction 151 Cretaceous period, biodiversity in 156 deserts, warm 181 flowering plants 253 grasslands and savannas 276, 278–279 greenhouse effect and biodiversity 297 Jurassic period, biodiversity in 341 keystone species 343 life history, diversity of 350, 353 mass extinctions 374 Neogene period, biodiversity in 393 Paleogene period, biodiversity in 400 Pleistocene extinction 414–417, 415t, 416t pond species 468t Quaternary period, biodiversity in 452 reptiles 454 rivers, streams, ponds, and lakes 466 seed dispersal 470–471 sexual selection 480 temperate deciduous forests 516 Triassic period, biodiversity in 524 tropical rain forests and deforestation 529t–530t tropical seasonal forests 537 mammary glands 5 mammoths 75, 76, 343, 417 managed ecosystems 463 managed forest 463 Man and Nature (Marsh) 548c manatees 365 mandibles 34, 320, 322–323 Manduca sexta 306, 324 mangrove islands 336 mangrove swamps 370 mangrove trees 371 manifest destiny 238 Manihot esculentum 188 manioc 188 maniraptorians 193 Mann, Michael 281, 282 Mantgem, Phillip van 296 mantids 98, 322 Mantis religiosa 481 mantis shrimp 158 manzanitas bush 487 maples 73, 187, 462, 499–500, 504, 513, 515, 516 maquia 486

Marchantiophyta 473 Margulis, Lynn 123, 231, 232, 266, 270, 368–369, 507–510 Marianas Trench 171 marine ecosystems 209 marine habitats 49 marine life animals 29 Cambrian period, biodiversity in 96–97 Carboniferous period, biodiversity in 105 Cretaceous period, biodiversity in 154 Devonian period, biodiversity in 182 Ediacaran organisms 217–218 Jurassic period, biodiversity in 341 Neogene period, biodiversity in 392 Ordovician period 396 Paleogene period, biodiversity in 398 Permian period, biodiversity in 411 Quaternary period, biodiversity in 450, 452 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523– 524 marine preserves 142 marine reptiles 151 Marsh, George Perkins 548c Marsh, Othniel Charles 190 Marshall, Diane 484 Marshall, John 238 marshes and swamps 274, 369–372, 370, 371t Marsilea drummondii 177 marsupials 393 biogeography 74–75 convergence 146, 146t, 147 life history, diversity of 352–353 mammals 359, 360, 362, 363, 367–368 temperate dry forests 518 tropical rain forests and deforestation 527 Martin, Paul 119 Martin, Robert A. 16 Mason, John 217 Massachusetts 520–522 mass extinctions 372–375, 373t Cretaceous extinction 151–152 Devonian period, biodiversity in 184 extinction 233, 235 Ordovician period 397 Permian extinction 407–410 Pleistocene extinction 414–417 Wilson, Edward O. 546 Mastigias papua 23 mastodons 76, 343, 417 mast seeding 118 Mathew, Patrick 384 mating dances 493 mating disruption 328 matorral shrublands 486, 517 matrix 256 matter, cycling of 207, 211–213 Maui 7 Mauritius 234 Mawsonites 217 maxillopods 158 Maximilian sunflower 61 May, Robert M. 52 Mayan culture 461, 501 mayflies 321 Mayr, Ernst 384–385 McKenney, Daniel W. 296 McKinley, William 239 McMenamin, Mark 217–218 McMurdo dry valleys 174 McNair, M. 484 meadows 130 meat 210 Medawar, Peter 353 Medea Hypothesis 223, 268

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586 Index 586 tundra  medical research 68, 444 medicine x, 38, 58, 114, 215, 326. See also biodiversity, resources for medicine; pharmaceuticals Medieval Warm Period 281 Mediterranean Basin 313, 486–487, 517, 518 Mediterranean Sea 76, 196 medusa stage 22 meerkats 159, 159 Megachile rotundata 421 Meganeura 105, 105 Meganeura monyi 320 meiosis 20, 260, 261, 472, 477 Melaleuca quinquenervia 330, 372 melaleuca trees 330, 333, 372 Melanerpes formicivorus 90 Meloe fransiscanus 98–99 Mendel, Gregor 386, 548c menopause 354 mental health 230 mercury 72, 80–82, 206, 423, 533 Mereschkovsky, Konstantin S. 508 Mesoamerican Biological Corridor 302 Mesohippus 400 mesophication 201 Mesopotamia 9, 11 Mesozoic era adaptive radiation 6, 8 Cretaceous period, biodiversity in 153–156 dinosaurs 190–193 ice ages 316 Jurassic period, biodiversity in 339–341 mammals 361, 362, 367 mass extinctions 372 reptiles 454 seed plants 477–478 mesquite 175 Mestral, George de 83 metagenomics 203 metamorphic rocks 256 metamorphosis 15, 37, 321, 324 Metasequoia glyptostroboides 51, 136–137, 222 methane 14, 101–103, 205, 287, 370, 409–410 Methanobrevibacter smithii 32 Methanococcus janaschii 33 methanogens 33 Methodus Plantarum Novae (Ray) 548c methyl mercury 72 Metrosideros polymorpha 505, 507 Mexican piñon 518 Mexican poppies 177, 497 Mexico agriculture 12 biodiversity, resources for agriculture 60, 62 cloud forests 115 deserts, cool 173 deserts, warm 175 endemic species 222 pollution 422 shrublands 487 temperate coniferous forests 511 temperate dry forests 517, 518 tropical seasonal forests 537 mice 6, 68, 350 Michigan 262 Michigan, Lake 128, 504 microaerophiles 379 microclimates 52, 90–91 Micrognathozoa 21, 28 microhabitats biodiversity, patterns of 51 communities, ecological 127, 128 rivers, streams, ponds, and lakes 466 temperate coniferous forests 511 temperate deciduous forests 513 tropical rain forests and deforestation 526

xviii+598_Biodiversity_F.indd 586

first entry micronutrients 71–72 microorganisms 47, 64–66, 171 Microsporidia 261 microwhip scorpions 36 Middle East 9–10, 12, 36, 60, 175, 179, 180, 517 mid-domain effect 48 migration birds 89 boreal and subalpine forests 92 fishes 248 greenhouse effect and biodiversity 295–297 habitat fragmentation 301–302 herbivory 305 predation 437 Migratory Bird Treaty 243 Milankovic, ´ Milutin 315 Milankovic´ cycles 270, 316, 450 mildew 262 military bases 241–242 milk 360, 362 milkweeds 117, 133–134, 180, 188, 303 Miller, Geoffrey 483 Miller-Rushing, A. J. 296, 522 millipedes 27, 35, 105, 436 Mimetica viridifolia 98 mimicry 45, 98, 321–322, 420, 437–438 Mimulus 490, 492, 494 Mimulus bigelovii 177, 177 Mimulus cardinalis 492 Mimulus dudleyi 128 Mimulus guttatus 484 Mimulus lewisii 492 Mimus longicaudatus 272 mineral cycle 71 mineral deposits 41–42, 256 mineralization 256 minerals 70–72, 206, 212 Minerals Management Service (Department of the Interior) 225, 244 mining 422 Minnesota 208, 209 minnows 248 mint 59, 188, 487 mirex 328 Miriophyllum aquaticum 467 missing-link fish-amphibians 15 missing links 361 Mississippian culture 461 Mississippi River basin 465 Missouri River 316 mistletoe 403 Mitchell, Mount 2 mites 35, 36, 123–124, 126–127, 184, 460 mitigation banking 139 mitochondria 42, 122, 230, 231, 368, 508–510 mitosis 261 Mivart, St. George Jackson 165 mixed-grass prairies 276 Mnemiopsis leidyi 332 moas 87, 119 Mobulidae 171 mockingbirds 272 Moi, Daniel arap 358, 359 Mojave Desert 175, 181, 301 Mola mola 247 molds 446, 448, 449 mole(s) 363, 367 molecules 69–72 mole rats 145–146 mollusks 25 animals 25–26 Cretaceous period, biodiversity in 154 Devonian period, biodiversity in 182 Linnaeus, Carolus 355 mass extinctions 374 Ordovician period 396–397 Paleogene period, biodiversity in 399

Permian extinction 410 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523 Molokai 7 molts 37, 321 monarch butterfly 117, 305, 500 moncots 255 Mongolian steppe 173 mongoose 527 monkeyflowers 177, 484, 490, 492 monkey puzzle tree 136 monkeys 112, 441–442, 537 monocots 113t, 114, 254, 375–377, 376, 467, 478 monoculture 13, 62, 391 monotreme mammal 110, 361–363, 527 Monotropa 144, 403 Monterey Canyon 172 Monterey cypress 318 Monterey pine 138, 308, 330, 518 Montin, Lars 355 moorlands 486 Moraceae 186 moraines 316 Moran, Thomas 239 moray eels 149, 248 Morgan, Thomas Hunt 430 Morganucodon 361 morning glories 110 morphology 40 mortality 426 Morus 186 Morus alba 60 mosquitoes arthropods 38 biomagnification 81 greenhouse effect and biodiversity 298 insects 323–324 invasive species 330, 331 IPM 328 parasitism 403, 404 resistance, evolution of 460 rivers, streams, ponds, and lakes 466 speciation 491 tundra 538 mosquito fish 331 moss animals 27 mosses 91, 381, 473–474, 474, 540 moth caterpillars 324 moths 325 arthropods 37–38 biodiversity, resources for agriculture 62 biomimicry 83 coevolution 120, 121 Darwin’s finches 168 DNA studies of biodiversity 203 pollination 418 Mound Builders 461 mountain birch 91 mountains 128–129, 176 Mount Rainier National Park 239 mourning doves 350 mouth-brooding 481 mudpuppies 18 Muir, John 239, 377–378, 413, 548c mulberries 60, 118, 186, 527 mule deer 345 Müller, Fritz 99 Muller, Robert 373 Mullerian mimicry 45, 99 Mundy, N. I. 148 Munson, T. V. 60 Muraenidae 149 Muricella 250 Musca domestica 324 muscles 86, 362 mushrooms 261, 262 muskeg 92 musk oxen 538 muskrats 370

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tundra  Index 587 mussels 26, 99, 467 mustard plants 12, 74, 84, 186, 310, 460 mutations biodiversity, patterns of 49 biodiversity, resources for medicine 68 disjunct species 194 DNA studies of biodiversity 202 extinction 233–234 founder effect and genetic drift 258 hybridization 309 insects 320 life history, diversity of 353 natural selection 384, 388–389 population genetics 431, 434–435 mutualism 378–383, 379, 380 agriculture 8 bacteria 41, 43 coevolution 121–122 communities, ecological 126 convergence 144–145 ecology 207 fungi 263–264 Gaia 267 insects 323 Janzen, Daniel H. 338 lichens 347–349 mycelium 260 mycobionts 264, 347–349 Mycoplasma 32 mycoplasmas 67 mycorrhizae 122, 263, 264, 381 Myllokunmingia 97, 245 myna bird 332 Myotis lucifugus 481 myriapods 35 Myrica cerifera 333 Myriophyllum spicatum 330 Myxococcus xanthus 41 Myxotricha paradoxa 381 Myzomela pammelaena 134

N

Nabhan, Gary 58 Nagoya Protocol 549c Naja naja 456–457 naked mole rat 145–146 nalidixic acid 68 Namibia 175, 217 Nanoarcheota 33 Nanosella fungi 324 nardoo fern 177 narrow-sense heritability 432 Nasua nasua 331 Nasutitermes triodiae 322 National Academy of Sciences xi, 2 National Environmental Policy Act (NEPA) 243, 549c national forests 238, 239, 241, 548c National Marine Fisheries Service Office of Protected Resources 219 National Oceanic and Atmospheric Administration (NOAA) 280 national parks 239, 240t–241t, 548c National Park Service (NPS) 2, 220, 239, 548c national wildlife refuges 241 Native American lands 238 Native Americans agriculture 11 biodiversity, resources for agriculture 62 disjunct species 196 disturbances, ecological 201 grasslands and savannas 279 Pleistocene extinction 416 predation 439 restoration ecology 461 succession, ecological 501 temperate deciduous forests 516 natural gas 102

xviii+598_Biodiversity_F.indd 587

Natural History of Selborne (White) 162 natural hybrids 309, 310 Naturalist on the River Amazons, The (Bates) 46 naturalists 542–545 natural pesticides 327 natural resource destruction 239 Natural Resources Conservation Service 242 natural selection 384–390, 388t, 548c adaptation 3, 5 agriculture 11–12 Bates, Henry Walter 45 biodiversity, concept of 46 biodiversity, patterns of 50 biogeography 72 biomimicry 82–83 Cambrian explosion 96 competition, ecological 131 cultural diversity 158 Darwin, Charles 164, 165 Darwin’s finches 167–169 environmental ethics 226 environmental psychology 228 Gaia 267, 268 herbivory 305 life history, diversity of 351–355 parasitism 405 pollination 418 population biology 426 population genetics 433–434 predation 437–438 resistance, evolution of 459–460 sexual selection 478–480, 482 speciation 489–490, 492, 494 Wallace, Alfred Russel 542–545 natural systems agriculture (NSA) 61, 62, 83, 338, 390–392 Natural Theology (Paley) 162 The Nature Conservancy 549c nature preserves 298 nautilus 25 n-dimensional hyperspace 132 Neanderthals 318 Nebraska 258 neck 16, 191 Necroscia sparaxes 480 nectar 169, 419, 420 nectar guides 418 Nectarinia sericea 134 nectar thieves 120, 419 Necturus maculosus 18 needle-leaved evergreen trees 92 neem tree 59 negative feedback 267 Nematocera 323 nematocysts 23 nematodes 27, 68, 124 Nematomorpha 28 Nemertea 28 Nemesis star 373 nene 234, 258 Neocallimastigomycota 261 Neogene period, biodiversity in 392–394, 392t–393t, 393 neognaths 89 Neopterygii 247 neoteny 18, 483 neotropics 527 Neozeleboria cyroptoides 99 NEPA. See National Environmental Policy Act Nepa cinerea 467 Nepenthes lowii 107 Nerine (fishing trawler) 249 nerpa seal 469 nervous system 24 Nesochen sandiviensis 234 net production 55 nettles 75, 76, 490 neurogenesis 69

neutral theory of evolution 434 Nevada 173 New Caledonia 75, 221, 254 Newfoundland 53, 217 New Guinea 9, 527, 542 New Hampshire 197, 312 New Mexico 175, 461, 461 New Roots for Agriculture (Jackson) 226 Newton, Sir Isaac 166 newts 438 New World monkeys 366, 442, 527 New World Tropics 49 New World vultures 89 New Zealand 87, 89, 119, 136, 138, 141, 458, 518 NGOs. See nongovernmental organization niche 132 Nicophorus 325 Nicotiana attenuata 419, 420 Nicotiana digluta 310 Nicotiana glutinosa 310 Nicotiana tabacum 310 Nicrophorus americanus 170 nightshade family 188 Niihau 7 Nilaparvata lugens 327 Nile perch 332 nine-banded armadillo 367 nipples 360 nitrates 42, 394–395 nitric acid 1 nitrites 42 Nitrobacter 394 nitrogen 42, 70, 206, 212 nitrogenase 394 nitrogen cycle 71, 267, 394–395 nitrogen fixation 42, 394 nitrogen-fixing bacteria 13, 63, 122, 186, 212, 380 nitrogen gas 394 Nitrosomonas 394 Nitrospira moscoviensis 43 nitrous oxide 287, 395 Nixon, Richard 243–244 NOAA. See National Oceanic and Atmospheric Administration Noah 224 Nobel Peace Prize 358, 359 No Child Left Inside 229 nodules 394 nonavian dinosaurs 113, 190 noncoding DNA 111 nongovernmental organization (NGOs) 59 nonrenewable resources 212 Norfolk Island pine 136, 477 North Africa 36, 175, 517, 518 North America adaptive radiation 6 biodiversity, patterns of 49, 52 biodiversity, resources for agriculture 61 biogeography 73–76 boreal and subalpine forests 91, 92 communities, ecological 128 conifers 137 deserts, cool 173 deserts, polar 174 deserts, warm 175–177, 179–180 Devonian period, biodiversity in 182 dicots 185–187, 189 disjunct species 194–196 grasslands and savannas 274–279 habitat fragmentation 301 ice ages 316–318 invasive species 330 keystone species 344–345 mammals 367 Paleogene period, biodiversity in 398 Pleistocene extinction 414–416 reptiles 457 temperate coniferous forests 511

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588 Index 588 tundra 

first entry

temperate deciduous forests 513, 515, 516 temperate rain forests 519 tundra 537 North Atlantic Ocean 285 Northern Hemisphere biodiversity, patterns of 48 biogeography 73–74 Carboniferous period, biodiversity in 103 communities, ecological 128–129 competition, ecological 133 greenhouse effect 282 ice ages 315 Quaternary period, biodiversity in 452 shrublands 487 Northern river otters 370 Norway 59 Norway spruce 511 Nostoc 348 Notaden bennetti 66 Nothofagaceae 73 Nothofagus 73 notochord 29, 245 Notomys alexis 181 Notonectidae 467 Novotny, Vojtek 50 NPS. See National Park Service NSA. See natural systems agriculture Nucifraga columbiana 137 nuclear membrane 231 nuclear plants 549c nuclei 447 nucleic acid sequences 32–33 nucleus 230–232 null models 48 nunataks 316 Nunavat people 16 nurse logs 518 nurse plants 463 nutrient cycling 381 nutrients 170, 171, 263–264, 348, 466, 469, 530–531 nutrition 11, 212 nuts 185, 186 nymphs 321

O

Oahu 7 oaks x, 7, 129, 403, 506 adaptive radiation 6 biogeography 73 biological classification 77–79 communities, ecological 128, 129 dicots 185 disturbances, ecological 200 endemic species 222 grasslands and savannas 278 greenhouse effect and biodiversity 296 herbivory 303 hybridization 308.309, 309 ice ages 318 keystone species 345 mammals 363 protists 446 shrublands 487 succession, ecological 504 temperate deciduous forests 515 temperate dry forests 517–518 temperate rain forests 518 oases 179 oats 12 Obama, Barack 220, 292 obligate mutualism 380 ocean acidification 297 ocean currents deep oceans, biodiversity in 171 deserts, warm 176 greenhouse effect 284–285 Humboldt, Alexander von 307

xviii+598_Biodiversity_F.indd 588

hydrological cycle 311 Neogene period, biodiversity in 392 Quaternary period, biodiversity in 450 ocean floor 172 ocean mutualisms 380–381 oceans 101–102, 170–173, 292, 311, 381, 396 ocean sunfish 247 ocean temperature 286 ocean vents 32, 41, 43 ocelli 35 Ochotona curzoniae 344 ocote blanco 518 ocotillo bush 177 octopus 25, 26, 154, 171 Oculina varicosa 149 odd-toed ungulates 365 Odocoileus virginianus 518 Odonata 321 Odysseus 223 Oecophylla ants 497 Oenothera caespitosa 128, 199 Oenothera hookeri 345 Oenothera rhombipetala 418, 419 Office of Science and Technology Policy 2 offshore oil drilling 215. See also BP Deepwater Horizon oil spill ohia trees 505, 507 oil. See petroleum oil fish 222 oil palm plantations 13 oilseeds 61, 62 oil spills 42, 242. See also BP Deepwater Horizon oil spill Okamoto, Noriko 510 okapis 56 Oklahoma 191, 194, 196, 221, 242, 303, 304, 515 Old Testament 224 Old World monkeys 366, 442, 527 Old World vultures 89 Olea europaea 196 Olea laurifolia 196 Oligocene epoch 367 oligotrophic water 466 olive trees 196 Olympic rain forest (Washington) 518 ombrotrophic bogs 91 ommatidia 320 omnivores 151, 208, 365 onagers 173 “On Civil Disobedience” (Thoreau) 521 Oncorhynchus gorbuscha 467 Oncorhynchus keta 467 Oncorhynchus kisutsh 467 Oncorhynchus tshawytscha 467 Ondatra zibethicus 370 On Human Nature (Wilson) 545, 546 onions 144, 375, 431 onomyid primates 443 On the Origin of Species (Darwin) 479, 489, 508, 544, 548c Bates, Henry Walter 45 biogeography 72 cladistics 113–114 communities, ecological 130 Darwin, Charles 165 natural selection 385, 386 population biology 424 Thoreau, Henry David 522 Onychophora 28 oomycetes 446–447 Opabinia 97 open circulatory systems 21 Ophioglossophyta 476 Ophiostoma 262 Ophisaurus 457 Ophiusa tirhaca 324 opisthokont protists 448–449 Opisthorchis sinensis 29–30 opossums 354, 362, 437

opportunistic infections 68 opposable thumbs 366, 441 Opuntia basilaris 189 Opuntia ficus-indica 61 Opuntia megasperma 273 oracle oaks 309 orange roughy 172 oranges 62, 63, 262 orangutans 443 orbit of Earth 315 Orchidaceae 376 orchids 376 biodiversity, patterns of 52 coevolution 120 decomposers 170 hybridization 310 monocots 376 parasitism 403 pollination 419, 420 tropical rain forests and deforestation 526 order (taxonomic) 78 Ordovician extinction 372 Ordovician period, biodiversity in 246, 396, 396–397, 397t, 472, 488 Oregon 136, 263 Oreskes, Naomi 280 organelles 230, 231 organic agriculture 13 Organization for Tropical Studies 339 organ pipe (cactus) 180 organ transplants 66, 262 “Origin of Human Races and the Antiquity of Man, The” (Wallace) 544 Origin of Species. See On the Origin of Species ornamentation 480 ornithischians 191, 192 Ornithopods 192 Ornithosuchus 524 Orrorin 443 Orthoptera 38, 321 Orycteropus afer 367 Osage oranges 118 adaptation 6 biodiversity, patterns of 50–52 camouflage and mimicry 98 conifers 136 convergence 148 Cretaceous period, biodiversity in 155 Darwin, Charles 166 ecology 207 flowering plants (angiosperms) 253 flowering plants and pollinators 119–121 herbivory 305 monocots 375, 377 mutualism 121–123 parasitism 402 parasitism to commensalism 121 plants and herbivores 116–117 predation 436–438 predators and prey 117–119 seed dispersal 471 seed plants 478 symbiogenesis 510 temperate deciduous forests 513 tropical rain forests and deforestation 526 Osbeck, Peter 355 Osmia lignaria 421 Osmia ribifloris 421 ospreys 80–81, 437, 466 ostariophysians 248 Osteichthyes 246 ostracods 158 ostriches 87, 88 otters 370 ovaries 87 overfishing 141, 172, 250 overhunting 234, 343, 416, 417, 439, 461

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tundra  Index 589 overkill hypothesis 416, 501 overpopulation 164, 165 Oviraptor 155, 193 Ovis aries 12 Owen, Sir Richard 166, 190 Owens Valley Desert 173 owls 89, 520 Oxalis pes-caprae 491 oxazolidinones 68 Oxyaena 400 oxygen animals 26 biogeochemical cycles 69–71 Cambrian explosion 95 Carboniferous period, biodiversity in 103 deep oceans, biodiversity in 171 ecology 205 ecosystems 212 ecosystem services 214 Gaia 267–269 mass extinctions 373 Ordovician period 396 Permian extinction 407–408 rivers, streams, ponds, and lakes 465, 466 oxygen depletion 13 oxygen isotope ratios 407–408 Oxytropis 84, 303 oysters 25, 463

P

Pachycephalosaurs 192 Pacific Northwest 296, 519, 520 Pacific Ocean 141, 172 Pacific Rim 141 Pacific Trash Vortex 172, 250–251 Pacific yew 66 Paedocypris progenetica 247 Paine, Robert 343 painkillers 66, 67 painted turtles 455 Pakicetus inachus 399 Pakistan 175, 460 Palaemon macrocadtylus 380 palate 456 Palau 23 Paleocene-Eocene Thermal Maximum 102–103, 374–375, 398 Paleogene period, biodiversity in 362–363, 398–401, 399t–400t, 401 paleognaths 87–89 paleotropics 527 Paleozoic era amphibians 15 birds 87 Cambrian period, biodiversity in 96–97 Carboniferous period, biodiversity in 103–106 Devonian period, biodiversity in 182–184 fishes 245–246, 249 fossils and fossilization 258 Gaia 269–270 mass extinctions 372, 374 seedless plants 474, 475 seed plants 477 Silurian period, biodiversity in 488–489 Paley, William 162 Palin, Sarah 68 palms 255 biodiversity, patterns of 52 biodiversity, resources for agriculture 62, 63 deserts, warm 179 endemic species 222 flowering plants 254–255 marshes and swamps 369 monocots 376 palolo worms 26

xviii+598_Biodiversity_F.indd 589

pampas 276–278 Panama 52, 284 Panama, Isthmus of 73, 74, 171, 284, 316, 450 Panama Canal region 56, 129 Panama disease 62 Panama land bridge 367 pandas 5, 363 Panderichthys rhombolepis 15 Pandion haliaetus 437, 466 Pangaea 73, 154, 409, 411, 523 pangenesis 386 Pan paniscus 443 Panthalassic Ocean 105 Pan troglodytes 443 Panulirus argus 157 Papaveraceae 185 Papaver californicum 487 papaya 62–63 paper daisy 177 paper parks 244 Papua New Guinea 87, 538, 540 papyrus sedge 377 Paracanthopterygii 248 Paraceratherium 400 Parameciuim 447 páramo region, Ecuador 538, 540 parapatric speciation 490 paraphyletic cladistic group 112–114, 185, 245 parasite resistance 480 parasitism 401–407, 402–405 amphibians 18, 19 animals 24–25, 27–31 arthropods 38 camouflage and mimicry 99–100 coevolution 121, 122 commensalism 124 communities, ecological 126 convergence 144, 148 ecology 207 fungi 261 herbivory 305 insects 322 mutualism 379 protists 447 Parasuchus 524 Parmesan, Camille 296, 297 parrot feathers 467 parrots 471 Parthenociccus quinquefolia 187 Parus atricapillus 69 passenger pigeons 234, 235, 461, 516, 548c Passeriformes 90 passerines 90 Passiflora 117 passionflower 117, 305 pastures 532 Patagonian Desert 173 pathogenic bacteria 43, 390 pathogenic fungi 263, 263t, 380 pathogens 263, 446–447 Patriofelis 400 Paulownia tomentosa 425–427 Pauropoda 35 Pavo crisatus 85 pawpaws 119 pax gene 148 peaches 186 peacock 85 peanut worms 28 pearlwort 174 pears 186 peas 548c peatmoss 474 pecan trees 515 pectoral fins 246, 247, 249 pedipalps 35, 36, 496 Pelagia panopyra 23 pelagic waters 170–171 Pelecaniformes 89

Pelican Island, Florida 241, 548c pelvic fins 246, 249 pelvis 192 pelycosaurs 454 penguins 89 penicillin 67–68, 262 Penicillium 262 Penicillium chrysogenum 262 Penicillium italicum 262 penis 35, 87, 481, 482 penis worms 28 Pentastomes 157 peppered moths 168 pepper tree 372 perches 249 perciform fishes 249 peregrine falcons 89 perennials 61–62, 426, 499, 502, 513, 538 peripatric speciation 490 perismmons 504 Perissodactyla 365 periwinkle (flower). See rosy periwinkle periwinkle snails 297 permafrost 538 Permian extinction 407–411 carbon cycle 102, 103 environmental ethics 223–224 Gaia 268–269 insects 320 mass extinctions 372, 374 Permian period, biodiversity in 361, 411– 413, 411t, 412, 454, 477 permineralization 256 Permo-Triassic boundary 407–409 Persea americana 118 persimmon 60, 471, 504, 527 persistent organic pollutants (POPs) 80, 81t, 82t, 212, 422, 502 Peru 175 pesticides agriculture 13 arthropods 38 biomagnification 80–82 Carson, Rachel Louise 107–109 ecology 207 federal government role in conservation (U.S.) 242 IPM 327, 328 pollination 421 pollution 422 resistance, evolution of 459–460 pest management 62, 215, 326–328 pests 36, 38 petals 184, 186, 188, 252, 252, 254, 375, 376, 376, 418 Petraitis, Peter 135 Petrified Forest Nation Park 341 petrified wood 257 petroleum. See also BP Deepwater Horizon oil spill agriculture 14 bacteria 42 bioremediation 84 carbon cycle 102 Carboniferous period, biodiversity in 103 continental shelves, biodiversity on 142–143 ecology 206 ecosystems 209, 212 ecosystems services 217 federal government role in conservation (U.S.) 242–243 greenhouse effect 289 tropical rain forests and deforestation 533 tundra 540 pets 382 phacelia 487 Phacelia campanularia 177 Phacelia cicutaria 128

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590 Index 590 tundra  Phacelia grandiflora 487 phaeophytes 446 Phalaropus lobatus 481 Phanerozoic eon 96–97, 372 pharmaceuticals bacteria 42 biodiversity, resources for medicine 66 deserts, warm 181–182 ecosystem services 215 herbivory 304 pollution 423 tropical rain forests and deforestation 526 Phasianus colchicus 330 Phasmida 321–322 Phasolarctos cinereus 518 pheasants 330 phenology 522 phenotypes 424, 430, 434 phenotypic plasticity. See plasticity, phenotypic phenotypic traits 431–432 pheromones 328, 498 Philippine Islands 62, 221 Philippine tarsier 443 Phillips, John 407 phloem 254, 255, 472, 477 Phoca sibirica 222, 469 Phoenix dactylifera 179 Pholidota 367 Pholistoma auritum 133 Pholistoma membranaceum 128 Phoneutria nigriventer 498 Phoronida 27 phosphate 263 phospholipids 32 phosphorus 70, 72, 264, 381, 466 photonic crystals 83 photons 205, 206 photosynthesis bacteria 42 biogeochemical cycles 70 carbon cycle 101 convergence 144 deep oceans, biodiversity in 170 deserts, warm 180 ecology 205 ecosystem services 214 eukaryotes 231 fossils and fossilization 258 Gaia 267–270 greenhouse effect 291 Neogene period, biodiversity in 393 photosynthetic bacteria 41, 381 photosynthetic symbionts 23, 347–349 phycobiont 264, 347–349 phyletic constraints 387–388 Phyllium giganteum 98 Phylloscopus trochiloides 494 phylloxera bug 60 PhyloCode 80, 113 phylogenetic analysis. See cladistics phylogenetic species concept 490 phylum (taxonomic) 78 Phymatotrichum omnivorum 263 Physalia physalis 23 physiological adaptation 147–148, 455 Phytophthora infestans 446 Phytophthora megakorya 447 Phytophthora ramorum 446–447 phytoplankton 52–53, 209 Pianka, Eric 350 Picea 92, 137 Picea glauca 76, 196, 502 Picea omorika 222 Piciformes 89–90 pickleweed 60, 176 Pielou, E. C. 72–73 pigeons birds 89 Darwin, Charles 165

xviii+598_Biodiversity_F.indd 590

first entry extinction 234, 235 natural selection 386 population biology 424 predation 439 restoration ecology 461 temperate deciduous forests 516 pigments 22–23 pigs 12, 333, 365 pikas 344, 538 pillbugs 158 Pilobolus 261 pilocarpine 67 Pilocarpus jaborandi 67 Pilosa 367 Pimentel, David 209 Pinaceae 137 Pinaroloxias inornata 169 Pinatubo, Mount 285 Pinchot, Gifford 239, 241, 347, 378, 413– 414, 548c pine(s) 200, 281 biogeography 76 biological classification 79 boreal and subalpine forests 92 coevolution 118–119 communities, ecological 127, 128 conifers 136, 137 disjunct species 196 disturbances, ecological 199–200, 201t fungi 264 greenhouse effect 281 hybridization 308 life history, diversity of 354 seed dispersal 471 seed plants 477, 478 succession, ecological 504 temperate coniferous forests 511 temperate dry forests 517, 518 pineal eye 246 pineapples 62, 63 pine bark beetles 297 pine needles 303 Pingelap Atoll 258 Pinguicula vulgaris 106 pink pygmy sea horse 250 pink salmon 467 pinnipeds 363–364 piñon-juniper woodlands 511 Pinus 79, 137 Pinus albicaulis 136, 137, 297, 540 Pinus aristida 92 Pinus banksiana 92 Pinus cembroides 518 Pinus contorta 200 Pinus coulteri 517 Pinus flexilis 137, 196 Pinus garryana 92 Pinus halepensis 517 Pinus lambertiana 518 Pinus longeava 92, 137, 138, 281, 354 Pinus muricata 128, 136, 196, 199, 200, 308, 428 Pinus pinea 517 Pinus ponderosa 136, 200, 518 Pinus radiata 138, 308, 330, 518 Pinus rigida 200 Pinus sabiniana 517 Pinus strobus 511 Pinus sylvestris 264, 511 Pinus thunbergii 511 Pinus torreyi 137 pipefishes 248–249 piranhas 248 pistillate cones 135–137 pistillate flower 252 pistils 419 biological classification 77 dicots 184, 188 flowering plants 252, 254 monocots 375, 377

pitcher plants 91, 106, 107, 438 pitch pines 200 Pitnick, Scott 479 Pitohni dichrous 436 pit vipers 181, 457 placenta 362 placental mammals biogeography 74–75 convergence 146, 146t mammals 359, 360, 362, 367–368 tropical rain forests and deforestation 527 placoderms 183, 246 placozoans 22 planarians 24 planctomycetes 231, 232 plankton 151, 170, 171 plant biogeography 179–180 plant breeders 58–59, 61 plant defenses 144–145, 303, 349 plant diseases 460 plant growth 296, 349 plant migration 296 plant range shift 296 plant reproduction 350 plants acid rain and fog 1 adaptation 3, 5–6 biodiversity, patterns of 49, 52 biodiversity, quantification of 54–57 biodiversity, resources for medicine 66 biogeochemical cycles 70, 72 biogeography 73–76 biological classification 77–79 bioremediation 84 bogs, life in 91 camouflage and mimicry 98–99 Carboniferous period, biodiversity in 105 carnivorous plants 106–107 coevolution 116–117 commensalism 124 communities, ecological 130 competition, ecological 132–134 convergence 144–145 Cretaceous extinction 151 Cretaceous period, biodiversity in 154–155 Darwin, Charles 166 decomposers 170 deserts, polar 174 deserts, warm 175, 178t–179t Devonian period, biodiversity in 183 disjunct species 194–195 disturbances, ecological 197–198 DNA studies of biodiversity 202 ecology 205, 206 ecosystems 208, 212 ecosystem services 213–217 endemic species 222 eukaryotes 232 extinction 234, 235 fossils and fossilization 257, 258 fungi 263–264 Galápagos Islands 272t greenhouse effect 289–293 herbivory 303–306 hybridization 308–311 Jurassic period, biodiversity in 341 life history, diversity of 351, 353 Linnaeus, Carolus 355 marshes and swamps 369 mass extinctions 374 Neogene period, biodiversity in 393 Paleogene period, biodiversity in 399 parasitism 403 Permian period, biodiversity in 412 pond species 468t population biology 424, 426–428 population genetics 431 predation 438

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tundra  Index 591 Quaternary period, biodiversity in 452 restoration ecology 463 rivers, streams, ponds, and lakes 467 seed dispersal 470–471 sexual selection 483–484 Silurian period, biodiversity in 488 speciation 491–492 temperate deciduous forests 512–516 Thoreau, Henry David 522 Triassic period, biodiversity in 524 tropical rain forests and deforestation 526, 527, 531 tundra 537–540 tundra species 539t plasmids 40 plasmodial slime molds 448 Plasmodium falciparum 509 plastic 172, 227, 251, 502 plasticity, phenotypic 3, 4, 132, 388, 432 plastron 455 Platanaceae 185 Platanus occidentalis 516 plateau pika 344 plated lizard 458 Plateosaurus 524 Platycerium veitchii 476 Platyhelminthes 24 platypus 361, 363 platyrrhines 442 pleiotropic genes 353–354 Pleistocene epoch 315, 450–452 Pleistocene extinction 414–417, 415t, 416t biodiversity, concept of 46 coevolution 118–119 extinction 234 keystone species 343 Quaternary period, biodiversity in 452 Wallace, Alfred Russel 544 Pleistocene overkill hypothesis 416, 501 Pleopeltis polypodioides 476 plesiadapiform 443 plesiosaurs 341 Plethodon jordani 481 plethodont salamanders 18 pleurodires 456 Pliny the Elder 548c plovers 89 plowing 391 plums 186 Pneumocystis 262 Poaceae 74, 376–377 Podocarpaceae 136 Poecilia reticulata 437 poison dart frogs 17, 18, 67 poison ivy 187, 298 poison oak 187 poisonous frogs 68, 436 poison sumac 187 Poland 516 polar bears x, 311 Pollan, Michael 13, 381 pollen 258, 416, 477, 484 pollen tubes 484 pollination 417–422, 418, 419 adaptation 6 coevolution 119–121 conifers 135 convergence 144 Darwin, Charles 166 ecology 206–207 ecosystem services 215 greenhouse effect and biodiversity 298 hybridization 308 insects 326 marshes and swamps 371 monocots 376, 377 sexual selection 483–484 speciation 492 temperate deciduous forests 513 tundra 538 pollinators x, 119, 120–121, 132, 253, 421

xviii+598_Biodiversity_F.indd 591

pollution 422–423 acid rain and fog 1–2 agriculture 12, 13 amphibians 18–19 biomagnification 80–82 bioremediation 83–84 deep oceans, biodiversity in 172–173 ecosystem services 214 environmental ethics 224, 227 federal government role in conservation (U.S.) 242, 243 fishes 250–251 greenhouse effect 289 lichens 348–349 marshes and swamps 372 pollution credits 2 polychelids 157 polyculture 62–63, 63, 391 Polygonum pensylvanicum 133 polymerase 69 polymorphism 430 polyps 23 Pombo, Richard 220 Pompilidae 498 ponderosa pines 127, 136, 200, 511 ponds. See rivers, streams, ponds, and lakes Pongo pygmaeus 444 poplar 186 poppies 177, 185, 497 POPs. See persistent organic pollutants population biology 423–430, 428 disjunct species 194–197 ecology 206 founder effect and genetic drift 258–259 natural selection 384 population control 438 population density 132 population genetics 139, 430–436, 431, 433t population growth 10, 48–49, 164, 385, 424–427 population variability 165 Populus deltoides 73, 187, 276, 483, 516 Populus tremuloides 92, 502 Populus trichocarpa 186 porcupines 353 pores 230–231, 350t Porifera 22, 22 pork tapeworms 31 Portugal 196, 298 Portuguese man-of-war 23 positive feedback 267, 268, 270 post oaks 200, 278, 296, 303, 304t, 309, 515 potassium 70, 212 potato beetle 325 potatoes 188 Potato Famine 446 Powell, John Wesley 548c power plant scrubbers 1 prairie dogs 198, 198, 344, 366 prairie potholes 468–469 prairies 274 biodiversity, resources for agriculture 62 biogeography 76 biomimicry 83 communities, ecological 128 deserts, cool 173 disturbances, ecological 198–200 grasslands and savannas 274–276 ice ages 317 natural systems agriculture 391 restoration ecology 461 prawns 157 praying mantis 322, 481 Precambrian 268–270, 315, 372 precipitation deserts, warm 175 ecology 206 greenhouse effect 285–286

greenhouse effect and biodiversity 298 hydrological cycle 311–314 shrublands 486 temperate deciduous forests 513 tropical rain forests and deforestation 525, 531 tropical seasonal forests 535 tundra 538 predation 436–441, 437, 439 biodiversity, patterns of 51 Cambrian explosion 96 camouflage and mimicry 99 coevolution 116–119 fishes 246–248 predators agriculture 13 animals 27, 28 arthropods 36 birds 89 communities, ecological 126, 130 competition, ecological 132 coral reefs 149 deep oceans, biodiversity in 170, 171 ecology 206 Jurassic period, biodiversity in 341 keystone species 344 Leopold, Aldo 347 mammals 363 marshes and swamps 370 parasitism 401, 402 population biology 428 reptiles 456 predator satiation 437 predator switching 51 predatory insects 327–328 premature birth 351–352 preservation 345, 378 pressure 32, 171 prey 117, 206, 436–438. See also predation prey mimicry 98–99 Priapulida 28 prickly pear cactus 61, 127 primary productivity 209 primary succession 504–505, 505 primates 352t, 366, 441–445, 442t, 444, 527 Primer of Population Biology, A (Wilson and Bossert) 545–546 Princess Anne tree 425–427 Principles of Geology (Lyell) 163 Priodontes maximus 367 prions 210 Pristionchus pacificus 124 Proboscidea 366–367 Procapra gutturosa 173 Procellariiformes 89 Prochlorococcus 42 progymnosperms 183 prokaryotes 32–33, 40, 230, 231 prolegs 37 promiscuous mating systems 482 pronghorns 119, 173 Prontosil 68 prosimians 441 prostate cancer 66 Protacanthopterygii 248 protected areas 139, 301–302 proteins 147, 231, 432–433 Proterozoic 33, 42 Protista 79, 348, 548c protists 445–449, 445t amphibians 18 animals 20 biological classification 79 decomposers 170 deep oceans, biodiversity in 170 eukaryotes 232 lichens 348 mutualism 381 parasitism 402, 404 symbiogenesis 509, 510 protostomes 24

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592 Index 592 tundra 

first entry

Prototaxites 488 Prunus 186 Prunus africana 66 Prunus serotina 186, 516 Prunus virginiana 303, 511 Psammolepis 183 Psaronius 105 Pseudomonas 124 Pseudomonas aeruginosa 41 Pseudomyrmex ants 380, 497 Pseudomyrmex spinicola 380 pseudopods 446 Pseudopterogorgia elisabethae 67 pseudoscorpions 36 Pseudotsuga menziesii 137 Psilophyta 476 Psilotum 476 Psudomyrmex 380 Pteridinium 217 Pteridium aquilinum 476 Pteridophyta 472, 474–476 pteridosperms 477 Pteris ensiformis 84 pterosaurs 155–156, 454, 524 Pterospora 110, 144 public health 333, 390, 460 public lands 239–242, 244 Puccinia 263 Puereria montana 333, 333 Puerto Rican tree frogs 18 puffballs 260 Pulex irritans 38, 323 pulmonary circulation 360, 455 pumiliotoxin 17 punctuated equilibria 387, 490 puncture vine 145, 168, 180, 470 pupae 323, 324 pupfishes 180, 301 Purgatorius 156, 443 Purísima Hills, California 128, 428 purple loosestrife 330, 372 purple-striped jellyfish 23 Putuo Island 235 Pycnogonida 36–37 pygmy forests 128 pygmy sea horse 250 pygmy shrew 196 Pygopodidae 457–458 pyrethrin insecticides 59 pyrite 71 Pyrolobus fumarii 32 Pyrus 186 Pythium 447 Pythonidae 456

Q

quadrate bone 361 quartz 71, 102 Quaternary period, biodiversity in 315, 450, 450–453, 451t–452t Queensland, Australia 196 Quercus adaptive radiation 6 biogeography 73 biological classification 79 dicots 185 hybridization 308 shrublands 487 temperate deciduous forests 515 Quercus agrifolia 129 Quercus alba 185 Quercus carmenensis 222 Quercus deliquescens 222 Quercus douglasii 6, 7, 128, 129, 278 Quercus dumosa 6, 7 Quercus kelloggii 309, 345 Quercus macrocarpa 6, 7, 303, 309, 511 Quercus marilandica 515 Quercus nigra 185, 185 Quercus petraea 318

xviii+598_Biodiversity_F.indd 592

Quercus robur 6, 7, 303, 318 Quercus rubra 506 Quercus stellata 304t dicots 185 disturbances, ecological 200 grasslands and savannas 278 greenhouse effect and biodiversity 296 herbivory 303 hybridization 309 temperate deciduous forests 515 Quercus suber 6, 7 Quercus virginiana 6, 7, 185, 369, 515 Quercus wislizenii var. frutescens 309 Quercus x guadalupensis 309 Quercus x morehus 309 quillworts 474 quinoa 62 quinolone 68 quorum sensing 41

R

radial cell division 28 radial symmetry 20, 20, 23–24 radiation 549c radioactive waste 82 radiolarians 448 radish 310 radula 26 Raffesia 402–403 Rafflesia arnoldii 527 ragweed 298 railroads 238 rainfall. See precipitation rain forest(s) 17 agriculture 8–9 biodiversity, patterns of 48, 52 competition, ecological 133 Darwin, Charles 163 dicots 186 herbivory 304 hydrological cycle 313 Janzen, Daniel H. 338–339 succession, ecological 502 tropical rain forests and deforestation 525 rain shadows 130, 176, 176 rainy season 168, 169 ramets 431 range shift of plants 296 rank-free classification 80 Ranunculaceae 185 rapamycin 66 Rapa Nui 66 Raphanobrassica 310 Raphanus sativus 310 Raphus cucullatus 234 rat(s) 68, 145–146, 273, 360, 459, 460 rat fleas 38, 323 rat-tailed maggots 467 rattlesnakes 457 Rattus rattus 273 Raup, David 372, 373 Ravenala madagascariensis 222 raw fish 30 Ray, John 548c ray-finned fishes 247–249, 356 rays 171, 246–247, 341 razorback pigs 12 rbc gene 231 Reagan, Ronald, and administration 2 recessive allele 434 recreation 229 recurring patterns 373 red algae 232, 448 redback spider 498 red blood cells 360 red cedars 200, 313 red crab 156, 157 REDD Program 533 red fir 92

red foxes 330 red jungle fowl 89 red kangaroo 363 red-naped sapsuckers 344 red-necked phalarope 481 red oaks 73, 185, 308, 309, 506 Red River basin 465 red squirrel 333 red-winged blackbirds 370 redwoods 136, 222, 356, 518 regeneration 27 reindeer 82, 538 reindeer lichens 348 reindeer moss 381 reinsurance industry 214 relative density 55 relative dominance 55 relative frequency 54–55 relictual population 194, 196 religion 10, 163, 164, 224–226, 228 Remipedia 158 renewable production 217 Repenomamus robustus 156 Report on the Lands of the Arid Regions of the United States (Powell) 548c reproduction animals 24–26, 28, 31 arthropods 35 bacteria 41 birds 87 conifers 136 conservation biology 139 fishes 249 fungi 260, 262 insects 322 life history, diversity of 349–354 Linnaeus, Carolus 355 population biology 426 predation 437 protists 447 reptiles 455 speciation 492–493 spiders 498 reproductive expenditure 481–482 reproductive interference 480 reproductive isolation 78, 489–493, 544 reproductive organs 26, 87, 481, 482 reproductive patterns 308 reproductive rates 352 reproductive success 387 reproductive systems 145–146 reptiles 454–459, 454t, 455, 456 amphibians 16 Carboniferous period, biodiversity in 106 cladistics 110, 112, 113 Cretaceous extinction 151 Cretaceous period, biodiversity in 154 dinosaurs 190–193 Jurassic period, biodiversity in 341 life history, diversity of 353 living fossils 356 mammals 360, 361 Neogene period, biodiversity in 393 Permian period, biodiversity in 412 Quaternary period, biodiversity in 452 Triassic period, biodiversity in 524 Republican Party 244, 270, 292 reservoirs 312 resistance, evolution of 327, 390, 459–460 resource allocation patterns 349–352 resource competition 47–48, 132, 134 resource extraction 533 resource investment patterns 349–352 resource limitations 385 resources 212 respiration 20–21, 42, 86, 101, 267, 268 restoration ecology 345, 460–465, 461, 464 resurgence 207 resurrection fern 476 retroviruses 67, 68

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tundra  Index 593 Reznick, David 390 Rhabdophis tigrinus 438 Rhagoletis pomonella 492, 493 Rhea americana 173, 481 rheas 87, 173, 481 Rheobatrachus silus 68–69 Rheobatrachus vitellinus 68–69 Rheum palaestinum 179 Rhincodon typus 246 Rhinella margaritifera 98 rhinoceros 235 Rhinocodontidae 171 Rhizobium 42 Rhizoctonia 263 Rhizodus hibberti 105 rhizoids 473–474 rhizomes 474–476 rhizomorphs 262 Rhizopus nigricans 261 Rhodophyta 448 rhubarb 179 Rhynia 183, 476 rhyniophytes 472–473 Rhysocaryon 113 ribbonweed 371 ribbon worms 28 ribosomes 40, 230, 231, 508 ribs 15, 16, 192, 458 rice 62, 263 Rice, Stanley 194, 303, 483 Richelia 381 ricin 187, 303 Ricinus communis 187–188, 303 Rieseberg, Loren 310 Riftia pachyptila 122, 172 ring-necked pheasants 330 ring species 494 ringworm 262 Rio de Janeiro, Brazil 549c Rio Grande system 465 Rio Summit 549c riparian forests 200 river blindness 31 rivers, streams, ponds, and lakes 1, 316– 317, 465–469, 468t riwoche horses 56 RNA 231 Robinia pseudoacacia 186 robins 234 rock pigeons 386 Rocky Mountain National Park 537 Rocky Mountains 538 biogeography 73, 76 boreal and subalpine forests 92 conifers 137 disjunct species 196 disturbances, ecological 200 succession, ecological 502 temperate coniferous forests 511 tundra 537 Rodentia 366 rodents 74, 360, 366, 459, 460 Rodhocetus 399 Rodrigues Island 235 Rohrabacher, Dana 103, 290 Roosevelt, Theodore 239, 241, 378, 413, 414, 548c roots 177, 376, 381 Rosaceae 186 rose family 186 rosids 185–188 rosinweed 61 rosy periwinkle 66, 67, 67, 527 rotenone 303 Rotifera 28 rotifers 21, 28 Roughgarden, Joan 483 roundworms 27, 29, 31, 353 Roystonea 369 rubber tree 188 rubisco 111, 231, 508

xviii+598_Biodiversity_F.indd 593

Rubus 186 ruminants 365, 378 runoff amphibians 18 biogeochemical cycles 70 disturbances, ecological 197 ecosystem services 215 federal government role in conservation (U.S.) 243 hydrological cycle 312–313 marshes and swamps 372 pollution 422, 423 restoration ecology 462, 463 rivers, streams, ponds, and lakes 466 rushes 377 rye 310

S

Sabatia campestris 431 Sabbath of the Fields 224 Saccharomyces cerevesiae 262 Sacculina 158 Sagan, Carl 369 Sagan, Dorion 508 sagebrush desert 173 sage scrub 487 saguaro 180 Sahara Desert 175, 176, 312, 316 Sahelanthropus 443 St. Francis of Assisi 224, 225 St. Helena Island 75 Sakai, Ann 492 salamanders 16–18, 481 Salicaceae 186 Salicornia 176 Salicornia bigelovii 60 salicylic acid 67 saline pools 180 saline soils 60 salinity 23, 32, 370 salinization 464 Salix 74 Salminen, Juha-Pekka 303 salmon 248, 249, 251, 467 Salmonella 404 salt cedars 333 Salticidae 497 salt marsh blue crabs 297 salt marshes 370 salt marsh grasses 310 saltwater crocodile 456 Salvinia 476 Salvinia molesta 372, 467 Samoa 26 sandalwood tree 403 sandburs 145 Sand County Almanac, A (Leopold) 226, 347, 549c sand dollars 28 sand dunes 504–505, 506 sand grasshoppers 181 sandhill cane 180 sandpaper trees 278 sandpipers 89 San Francisco Bay 370 San Francisco Peaks 76 San Joaquin Valley, California 463 Santa Ana winds 200 Santa Barbara oil spill (1969) 242 Santa Lucia fir 222 Santalum 403 Santa Rosa Island 75 “Santa Rosalia” (Hutchinson) 549c Sapelo Island 354 Sapindaceae 187 Saprolegnia ferax 18 Saratoga Springs 301 Sarcophilus harrisii 363 sarcopterygian fishes 15, 249 Sargasso Sea 171

Sargassum seaweeds 171 Sarracenia purpurea 91, 106 sashimi 30 saurischians 191–192 sauropods 191 Sauroposeidon proteles 191 savannas 318. See also grasslands and savannas Savolainen, Vincent 203 Saxifraga oppositifolia 174 Scablands 317 scala naturae 50, 78, 356 scales 16, 455, 457 Scalesia trees 272 scallops 25, 26 Scandinavia 91 Scarabaeidae 170 scarab beetle 170, 325 scatterboarding 471 scavengers 208 Schemske, Douglas 492, 494 Schiedea salicaria 492 Schierenbeck, Christina 12 Schinus terebinthinifolius 372 Schistosoma 30 schistosomes 30 schistosomiasis 30 Schluter, Dolph 169 Schulman, Edward 281 Schulman Log 281 Schulte, David 463 Schweitzer, Mary Higby 190 Sciurus carolinensis 333 Sciurus vulgaris 333 Scleroctinia 263 scolecophid snakes 457 Scoliopus bigelovii 420 scorpion flies 420 scorpions 35, 36, 36, 184, 436 Scotland 487 Scots pines 264, 511 scramble competition 131 scrubbers (power plant smoke) 1 scrub oaks 6, 487 sculpins 467 scurvy 11, 58 sea crocodiles 341 sea fan coral 250 seafood 82 seagulls 89 seahorses 248–249, 250 sea ice 285 sea krait 98 sea levels 285, 396 seals 222, 469 Sea of Japan 172 sea pens 218 Searcy, K. 484 sea scorpions 396 seaside alder 139, 194–195, 221, 222, 308 seasonal forests 525 seasonal patterns 296, 304, 522 sea spiders 36–37 sea turtle 455 sea urchins 28, 29 seaweed 141–142, 171, 446 secondary palate 456 secondary succession 500, 502, 504 sedges 91, 195, 377, 538, 540 sedimentary layers 152 sedimentary rocks 256 sediments 70, 91, 407, 408, 416 seed bank 428 seed dispersal 92, 118, 119, 470–472, 520–522, 532 seed ferns 412, 477, 524 seedless plants 203, 472–477, 473t, 474–476 seedlings 532 seed plants 105, 135–138, 252, 258, 477–478

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594 Index 594 tundra  seed predators 117–118, 471 seeds 371, 477 Seed Savers Exchange 59 seed vaults 59 segmented bodies 34 Seilacher, Dolf 217–218 S¸ ekercio, Çagˇan 297 Selaginella 474 Selaginella plana 475 selective logging 533 selenium 84 Selenocosmia stirlingi 181 semelparous species 350 semen 481 Senate, U.S. 109 senescence 353, 354 sepals 184, 252, 252, 254, 375, 376 Sepkoski, J. J. 373 sequoia 130, 136 Sequoiadendron giganteum 136, 222, 354, 502, 511 Sequoia National Park 239, 537 Sequoia sempervirens 136, 518 Serbian spruce 222 Serial Endosymbiotic Theory 509 serotinous pine forests 199–200 serpentine soils 72 sewage 13, 30, 61, 172, 466 sex hormones 99 sex ratios 387, 424 sexual adornment 5 sexual classification system 355 sexual mimicry 98–99 sexual reproduction amphibians 16 animals 21, 29 arthropods 35 birds 87 fungi 260, 261, 263 seedless plants 472 spiders 498 symbiogenesis 508 sexual selection 478–485 adaptation 3, 5 biodiversity, patterns of 50 competition, ecological 134 Darwin, Charles 166 natural selection 384 parasitism 402 sexy sons hypothesis 479 Seychelle Islands 234, 493 shade 214, 216 shade-intolerant trees 499 shade-tolerant trees 499, 500 shafts (feathers) 85 shallow seas 339 Shannon, Claude 55 Shannon-Wiener diversity index 55 sharks biodiversity, resources for medicine 66 Carboniferous period, biodiversity in 105 Cretaceous period, biodiversity in 154 deep oceans, biodiversity in 171 fishes 246–247, 250 Jurassic period, biodiversity in 341 keystone species 344 Neogene period, biodiversity in 392 Paleogene period, biodiversity in 399 Permian period, biodiversity in 412 Quaternary period, biodiversity in 452 Triassic period, biodiversity in 523 sheath-winged beetles 37 sheep 12, 429 shells 25, 455 Shenandoah National Park 2 shield bugs 323 shield shrimp 180 shifting agriculture 531–532 shortgrass prairies 173, 198–200, 274–276 short-term carbon cycle 101

xviii+598_Biodiversity_F.indd 594

first entry short-term mineral cycle 70, 71 shrew opossums 363 shrews 195–196, 367 shrimp 156–158, 172, 180, 305–306, 380, 381 shrublands 173, 486–488, 486t–487t shrubs 129, 174, 174t, 176, 177, 180, 187, 196 Shubin, Neil 15–16 Shuvuuia 156 Siberia biogeography 75 boreal and subalpine forests 91, 92 Carboniferous period, biodiversity in 105 Devonian period, biodiversity in 182 endemic species 222 Ordovician period 396 rivers, streams, ponds, and lakes 469 tundra 537 Siberian Traps 409 sibling conflict 352 sickle-cell anemia 434 Sideroxylon grandiflorum 462 sidewinder 457 Siegesbeck, Johann 355 Sierra Club 378, 548c Sierra Madre 511 Sierra Nevada 129, 130 biogeography 76 boreal and subalpine forests 92 communities, ecological 127 conifers 136, 137 disjunct species 196 endemic species 222 Muir, John 377–378 succession, ecological 502 temperate coniferous forests 511 tundra 537 Silene virginica 418 Silent Spring (Carson) 82, 108, 109, 242, 549c silicon 71 silk 83, 497, 498 Silphium integrifolium 61 Silphium laciniatum 276 Silphium terebintinaceum 276 Silurian period, biodiversity in 472–473, 488–489, 489t silverfish 321 silver maples 187 Simberloff, Daniel 134, 336, 546 Simmondsia chinensis 61 Simpson’s diversity index 55 Singer, S. Fred 2 single-species groups 436–437 Sinocodon 361 Siphonaptera 38, 323 Siphunculata 322 Sipuncula 28 Sirenia 365 Sitka spruce 518 sixth mass extinction 228, 233, 235, 269, 374–375, 410, 417 size 366 size dimorphism 480 skeletons 20, 22, 95, 96, 246, 247, 249, 258 skin 17, 18, 455, 457 skin bacteria 379 skinks 457, 458 skull bones 360–361, 454 sky islands 336 slash and burn agriculture 531–532 SliME (subsurface lithoautotrophic microbial ecosystems) 43 slime molds 446, 448, 449 sloths 367, 367 slugs 25 smallpox 404, 428, 501 Smith, Thomas Bates 389 Smithsonian magazine 338

smokestacks 1 snails 25, 25, 26, 66, 172, 331 snakes 155, 181, 333, 400, 438, 454–458, 456 snapping shrimp 156–157 snapping turtles 370 snow 312 Snow, Allison 484 Snowball Earth 218, 269–270, 315 snow gum 92 snowshoe hare 438 soap 327, 466 soapberry bug 389, 493 soapberry trees 187 social mimicry 99–100 social parasitism. See social mimicry social structures 352 social systems 38 sociobiology 546 Sociobiology: The New Synthesis (Wilson) 546 sockeye salmon 467–468 sodium 212 soft-shell turtles 455 soft tissue 190 soil acid rain and fog 1 biodiversity, resources for agriculture 60–61 biogeochemical cycles 72 bioremediation 84 boreal and subalpine forests 92 communities, ecological 128 decomposers 170 deserts, warm 179 disturbances, ecological 198 fungi 263 restoration ecology 461 shrublands 486 succession, ecological 502 temperate deciduous forests 515 tropical rain forests and deforestation 530–531 tundra 538 soil bacteria 41, 66 Soil Conservation Service, U.S. 242, 549c soil erosion 13, 128, 242, 391, 461, 463 soil nutrients 42 Solanaceae 188 Solanum tuberosum 188 solar flares 373 solar power 83, 181 solar radiation 270, 315 sole 249 Solenopsis invicta 325, 331, 332 solifugids 35–36 Solnhofen limestone 257 Solomon, Susan 280 somatic cells 353, 384 somatic mutations 384, 431 Sonoran Desert 175, 181, 301 soot 1 Sorex minutus 196 sorghum 12 Sorghum bicolor 12, 61 Sorghum halepense 12, 61 South Africa continental shelves, biodiversity on 141 deserts, warm 180 greenhouse effect and biodiversity 296 Permian extinction 408–409 shrublands 486 speciation 491 temperate dry forests 517 South America agriculture 9 Bates, Henry Walter 45 biodiversity, resources for agriculture 62 biogeography 74, 75 birds 87

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tundra  Index 595 Cretaceous period, biodiversity in 154 Darwin, Charles 163 deep oceans, biodiversity in 171 deserts, cool 173 deserts, warm 175, 177, 179–180 dicots 189 grasslands and savannas 276–278 Humboldt, Alexander von 307 mammals 363, 367 Pleistocene extinction 415 temperate rain forests 519 tropical rain forests and deforestation 527, 531, 532 Wallace, Alfred Russel 542 South Dakota 91, 127, 128, 196, 198, 199, 303, 511 Southeast Asia 12, 62, 519, 533, 534 Southern Hemisphere 73–74, 87, 92, 136, 316 Soviet Union 263, 463–464 soybeans 534 Spain 196, 296, 298 Spartina alterniflora 297, 310 Spartina foliosa 370 Spartina maritima 310 Spartina x townsendii 310 spatial patterns 522 spawning grounds 251 specialists (consumers) 208 specialization 126, 418, 513, 526 speciation 489–496, 495t adaptive radiation 8 biogeography 73 Darwin’s finches 169 ecology 207 parasitism 402 pollination 420 Quaternary period, biodiversity in 452 tropical rain forests and deforestation 526 species xi species-area relationship 48, 335 species diversity 373–374 species interactions 206–207, 269 Species Plantarum (Linnaeus) 548c species richness 54, 56 specific mate recognition system 489–490 spectacled lizards 458 Spencer, Herbert 165 sperm 20, 23, 29 spermatophore 481 sperm cells 473–476, 479, 481 sperm nuclei 477 Sphaeralcea coccinea 128 Sphagnum 474 sphagnum moss 91, 540 Spheniciformes 89 Sphenodon 458 sphinx moth 37, 62, 324 spice plants 305 spices 116, 117, 188 spicules 22 spiders 496–498, 496–499 animals 27 arthropods 35 deserts, warm 181 Devonian period, biodiversity in 184 predation 437 rivers, streams, ponds, and lakes 467 sexual selection 481 spider silk 83 spikes 376, 377, 470 spines 144, 303 spinifex hopping-mouse 181 spiny anteater 361 spiny-headed worms 28 spiny lobster 157 spiracles 320 spiraea bush 66 Spiraea ulmaria 66 spirilla 40

xviii+598_Biodiversity_F.indd 595

spiritualism 544–545 spirochetes 40, 231, 232, 509 spitting cobra 457 split-middle whip scorpions 36 Spondias mombin 338 sponges 22, 22, 66, 67, 69, 231, 381, 449 spongouridine 67 spoon worms 28 sporangia 260, 261, 474, 475 spores 260, 261, 348, 397, 473–475, 475 sporophytes 472–477 Sporormiella 416 spotted owl 520 Sprigg, Reginald 217 Spriggina 217, 218 spring budburst 296 springtails 263, 321 spruce bark beetles 297, 328 spruce trees biogeography 76 boreal and subalpine forests 92 conifers 137 endemic species 222 fossils and fossilization 258 succession, ecological 502 temperate coniferous forests 511 temperate rain forests 518 spurges 133–134, 177, 180, 187 squalamine 66 Squalodon 399 squamates 454, 456–458 squids 25–26, 171 squirrels 117, 333, 471 squirting cucumbers 470 Sri Lanka 527 stabilizing selection 387, 388t, 389 staghorn ferns 475, 476 stalk 261, 377 stalked crinoids 397 stamens 252, 376, 419 biological classification 77 dicots 184, 186, 188 flowering plants 252, 254 monocots 375–377 Stamets, Paul 264 staminate cones 135, 136 staminate flower 252 Stanford, Alice 113 stapes 16, 361 staphlinid beetles 145 staphylococci 41 starfish 28, 29, 149, 154, 431 starlings 330 stealth 481 Stegosaurus 341 stem cells 353 stems 376–377, 467 stem veins 254 Stenocereus thurberi 180 stenopods 157 Stenopterygii 248 Stensen, Niels 256 Stentor 447 steppes 199, 276–278 Sterna paradisaea 89 Sternula antillarum 196 sternum 86 Stethacanthus mirabilis 105 steward 225 Stewart, Caro-Beth 110 stick and leaf insects 321–322 stickleback fish 481, 493–494 stigmas 377 stinging tentacles 23 stink bugs 323 stinkhorns 260 Stipa 278 stochastic processes 522 Stockholm Convention 82 stomach 365 stoneflies 466

strata 154, 256 stratification 469 strawberries 186 streams. See rivers, streams, ponds, and lakes streamside habitats 200 Strepserrhini 366 streptococci 41 Streptococcus mitis 43 Streptomyces avermitilis 59 stress 229 Strigiformes 89 strip-cropping agriculture 391 Strix occidentalis 520 strobilurins 59 Strobilurus tenacellus 59 stromatolites 408 strontium-90 72 structural defense 436–437 sturgeons 222, 247, 356 subalpine forests. See also boreal and subalpine forests acid rain and fog 2 biodiversity, quantification of 55, 56t boreal and subalpine forests 92–94 communities, ecological 125 disjunct species 196 keystone species 344 temperate rain forests 519 tundra 540 succession, ecological 499–507, 500, 503t, 504–507 bogs, life in 91 competition, ecological 134–135 ecology 207 Thoreau, Henry David 520, 522 “Succession of Forest Trees, The” (Thoreau) 521 succulents 98, 128, 144, 177, 179–180, 376 sugar maples 187, 462, 504, 515, 515 sugar molecules 208 sugar pines 511, 518 sulfa drugs 68 sulfate ions 71 sulfur 70, 71 sulfur dioxide 1, 2, 409 sulfuric acid 1, 43, 71 sumac family 186 Sumatra 116 sumpweeds 9 sundews 91, 106, 438 sunfish 308 sunflowers 9, 60–62, 61, 84, 188, 310, 492, 494 sunlight bacteria 41 biodiversity, patterns of 48 deep oceans, biodiversity in 171 ecology 205 ecosystems 208, 210, 211 greenhouse effect 286 tundra 538, 540 sunscorpions 35–36 sunspots 285 superior traits 387 Supersaurus 191, 191, 192, 341 Supreme Court, U.S. 238 surgery 229 survival of the fittest 165 survivorship 427–428 Sus scrofa 12 Svalbard Islands 174 Svalbard seed vault 59 swamp locusts 119 swamps 274, 339, 473. See also marshes and swamps swans 89 sweat glands 5 swifts 89 Switzerland 2 sycamores 185, 516

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596 Index 596 tundra 

first entry

symbiogenesis 507–510 bacteria 42 ecology 207 eukaryotes 231, 232 lichens 347–349 Margulis, Lynn 368–369 speciation 491, 494 Symbion pandora 28 symbiosis 116t coevolution 116 commensalism 123–124 ecology 207 Ediacaran organisms 218 lichens 347–349 Margulis, Lynn 368 mutualism 380 parasitism 402 symbiogenesis 507 symbiotic cyanobacteria 22–23 symmetry 20, 20, 480 sympatric speciation 490–491 Symphyla 35 symplesiomorphy 110 synapomorphy 110–112 synapsids 360–361, 412, 454, 455 synecology 206–207 Synemosyna 497 syphilis 404 Systema Naturae (Linnaeus) 548c systemic circulation 360, 455

T

Tachypleus gigas 46 Taenia rhynchus saginatus 30–31 Taenia solium 31 Taft, William Howard 414 taiga 91, 92 tail feathers 86 tailless whip scorpions 36 Taiwan 221 Taklamakan Desert 173 tallgrass prairies 274 biodiversity, resources for agriculture 62 biogeography 76 biomimicry 83 deserts, cool 173 disturbances, ecological 198–200 grasslands and savannas 274–276 ice ages 317 restoration ecology 461 tamarisks 179, 313 Tamarix 179, 313, 333 tammar kangaroo 362 Tanganyika, Lake 6 tannins 303, 304t Tansley, Arthur 549c Tanystropheus 524 Taoism 226 tapeworms 24–25, 30, 30–31 Taq polymerase 69 tarantula hawk wasps 498 tarantulas 497, 498 Taraxacum officinale 330, 491 tarballs 142 tardigrades 27 Tarrant Regional Water District 242 tarsiers 441 Tarsius syrichta 443 Tasmania 12 Tasmanian devil 363 Tasmanian tiger 549c Taxaceae 136 taxidermy 162 Taxodiaceae 136 Taxodium distichum 137, 512, 513 taxol 66, 67 taxonomy 77, 355 Taxus brevifolia 66 teak 188, 537

xviii+598_Biodiversity_F.indd 596

Tectona grandis 188 teeth dinosaurs 191, 192 fishes 246, 248 fossils and fossilization 256–257 mammals 360–363, 366 reptiles 455 teleosts 247, 248, 524 telomeres 231 temperate coniferous forests 511–512, 519 temperate deciduous forests 185–186, 512–517, 513, 514t–515t, 515 temperate dry forests 517–518, 517t, 518 temperate rain forests 518, 518–520, 519t temperate zones 13, 49, 115–116 temperature 49, 176, 206, 465, 466 temperature extremes 32 temperature patterns 115, 116, 279–284, 307, 316 temperature regulation 86–87 Tennessee 55 Tennyson, Alfred, Lord 386 ten percent law 50, 209, 439 tentacles 23 teosinte grass 11, 60 termites 38, 322, 322, 379–381, 510 terns 89, 196 terrapin 455 terra preta de Indio 461, 531 terrestrial ecosystems 209 terrestrial plants 374 terrestrial vertebrates 454k–458 territory 480 terrorism 226 testudines 455–456 Tethys Sea 523 Tetrahymena 447 tetraploids 309 tetrapods 16, 17, 249, 454 Tetrastigma 403 tetrodotoxin 17 Tevnia jerichonana 172 Texas 76, 175, 515 Thar Desert 175 Thaumaptilon 218 Thaumarcheota 33 thecodont 361 Theobroma cacao 60 Theophrastus 356, 548c Theraphosa blondi 498 therapsids 361, 454 therian 362 thermodynamics, second law of 270 Thermoplasma 32, 509 Thermotoga 32 Thermus aquaticus 43 Thermus aquatilis 69 theropods 87, 192 Thinopyrum intermedium 61 Thiobacillus concretivorans 43 Thiomargarita namibiensis 40 Thomas, Lewis 266 Thomas, Matthew 328 Thomson, Sir C. Wyville 548c thorax 37, 320 Thoreau, Henry David 228–229, 363, 520–523 Thorius 17 thorns 144 three-color vision 366 “three sisters” crops 62 thrush 262 thumb 366, 441 Thunnus thynnus 172, 250 thylacines 363, 549c Thyreophores 192 thysanurans 321 Tibet 56, 344 ticks 35, 36, 403, 404 tickspiders 36 tidepools 142

Tidestromia oblongifolia 134, 176, 176, 177 tigers 308, 365, 537 tiger sharks 247 Tiktaalik roseae 15–16, 16, 184 Tilia americana 506 tillage 391 timberline 540 tinamous 87 Tinea 262 tipping points 286 tissue 190 Titanoboa 400 Titanus giganteus 324 toadfishes 248 toadflax 403 toads 18, 235, 331, 332 tobacco 310 tobacco hornworm caterpillars 306 tolerance 49, 177, 180–181, 304–305, 513 Tolstoy, Leo 521 Tolypocladium inflatum 66 Tolypocladium niveum 262 tomatoes 188, 501 tomato pinworm 328 tongue 17, 456, 457 tools 482 tooth enamel 258 Torreya 222 Torreya taxifolia 137, 222 Torrey pine 137 tortoises 272, 273, 455–456, 456 toxic chemicals/compounds 42, 80–82, 133, 303, 304 toxic ions 84, 303 Toxicodendron 187 toxic peptides 66 toxic plant chemicals 187–188 toxins amphibians 18 animals 23 biodiversity, resources for medicine 66, 67 ecology 207 herbivory 304 succession, ecological 502 tropical rain forests and deforestation 526 trace fossils 258, 397 tracheae 21, 35, 36, 320, 497 Trachycaryon 113 Tradescantia ohiensis 376 Tragopogon 492 trait linkage 388 traits 110–112, 166, 369 transcendentalism 520–522 transitional zones 537, 540 transmutation 165, 166 transpiration 313, 525 trapdoor spider 497 Trapelia 84 Trapezia ferruginea 381 trapping 328 traveler’s palm 222 Trebouxia 348 tree(s) biodiversity, quantification of 56 commensalism 124 Devonian period, biodiversity in 183 dicots 185–188 environmental psychology 228, 229 fungi 263 greenhouse effect 291–293 hybridization 309 life history, diversity of 349–351 marshes and swamps 369 mutualism 380 succession, ecological 499, 500, 502 wood pores 350t tree cactuses 272 tree ferns 475

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tundra  Index 597 tree finches 167 tree frogs 17, 18 tree hibiscus 235 tree-of-heaven 350 tree of life 507–509 Tree of Life project 79–80 tree planting 358–359 tree rings 137, 257, 281 tree shrews 367 trematodes 24 Treponema pallidum 404 Triassic mass extinction 372–373 Triassic period, biodiversity in 454, 477, 523–525, 523t, 524 tribal cultures 66, 159–160, 534 Tribrachidium 217 Tribulus cistoides 180 Tribulus terrestris 144, 145, 180 Triceratops 155 Trichilia rubescens 305 Trichinella spiralis 31 trilobites 96, 105, 182, 396, 488 trimerophytes 473 Trionychidae 455 Triops australiensis 180 Tripsacum 234 Tritemnodon 400 Triticale 310 Triticum aestivum 12, 310 Triticum boeoticum 310 Triticum dicoccoides 310 Triticum dicoccum 310 Triticum monococcum 310 Triticum spelta 310 Trivers, Robert 352 trochanter 320 Trombicula 36 trophic cascade 130, 344 trophic levels 208, 209 tropical alpine tundra 540 tropical biodiversity 47–49, 52 tropical countries 29–31 tropical fish 150 tropical rain forests and deforestation 525, 525–535, 526, 528t–530t, 531, 532 agriculture 8–9 biodiversity, patterns of 47, 49, 52 biodiversity, resources for medicine 66 cloud forests 115–116 competition, ecological 133 Darwin, Charles 163 dicots 186, 188 herbivory 304 Janzen, Daniel H. 338–339 succession, ecological 502 temperate rain forests 519 tropical seasonal forests 380, 525, 535–537, 536t tropic of Cancer 535 tropic of Capricorn 535 trout 248 true bugs 322–323 true ferns 475–476 true shrimp 157 truffles 260–261 trumpet creepers 120 Tsuga 137 Tsuga canadensis 128, 511 tuataras 356, 454 tube feet 29 tuberculosis 404 tubeworms 171, 172 Tubifex tubifex 467 Tubulidentata 367 Tulare Lake 463 tule elk 221 tunas 249 tundra 537–541, 538, 539t, 540 biogeography 74, 76 boreal and subalpine forests 92 communities, ecological 125

xviii+598_Biodiversity_F.indd 597

life history, diversity of 351 restoration ecology 462 succession, ecological 501 tunicates 29 Turbellaria 467 turbot 249 Turkestan Desert 173 turkey vultures 124 turtles 349, 353, 370, 454–456, 455, 524 Twain, Mark 544 Typhaceae 377 Typhlosaurus 458 typhoons 286 Tyrannosaurus rex 191, 192, 192, 257

U

Uintatherium 401 Ukraine 82 Ulmus 73 ultraviolet radiation 18, 502, 540 Umbellularia californica 129 umbrella palm 222 understory 526, 531 understory birches 264 underwater plants 467 undulipodia 509 UNEP. See United Nations Environment Programme UNESCO (United Nations Educational, Scientific and Cultural Organization) 273 ungulates 365 unicorn plant 470 unidirectional lungs 86 unique traits 110 United Nations 140, 533 United Nations Billion Tree Campaign 359 United Nations Climate Change Conference 549c United Nations Convention on Biological Diversity 549c United Nations Environment Programme (UNEP) 235, 358–359 United Nations Food and Agriculture Organization (FAO) 58 United Nations Framework Convention on Climate Change 549c universe, age of 268 Ural Mountains 105 uranium 84 urban planners 228 urea 18, 455 uric acid 455 Urnisa guttulosa 181 ursodeoxycholic acid 66 Ursus americanus 518 Ursus arctos 516 Urticaceae 75 USDA. See Agriculture, U.S. Department of Utah 173 Utricularia vulgaris 106–107

V

vaccination 544 vaginal yeast infections 262 Vallisneria 371 vampire bats 403 Vampyroteuthis infernalis 171 vanes (feathers) 85 Varanus komodoensis 457 variability 431–435 vascular system 29 vascular tissue 472–473, 477 vectors 404, 405, 417 vegetarian diets 209–210 vegetation zones 317m veins 254, 375 Velcro 83 Velociraptor 156 velocity 465

velvetleaf 330, 356, 501 velvet worms 28 venom 17, 456–57 venomous spiders 496, 498 Venter, J. Craig 171 ventral surface 20, 34 Venus flytrap 106, 438 Verbenaceae 145 Verkoyansk, Siberia 92 Vermeij, Geerat 52 vertebrae 458 vertebrate amphibians 147 vertebrate health 378–379 vertebrates animals 20, 29 birds 84–90 Carboniferous period, biodiversity in 105–106 cladistics 110 Cretaceous period, biodiversity in 154, 155 Devonian period, biodiversity in 182–184 fishes 244–251 Jurassic period, biodiversity in 341 Neogene period, biodiversity in 392, 393 Ordovician period 397 Paleogene period, biodiversity in 399, 400 Permian period, biodiversity in 412 Quaternary period, biodiversity in 452 Silurian period, biodiversity in 488 Triassic period, biodiversity in 523– 524 vestimentiferan worm 122 Vibrio fisheri 41 vicariance 73–75, 194, 195 viceroy butterfly 437 Victoria, Lake 6–7, 332 Vietnam 56, 533 vinblastine 66, 67, 527 vincristine 66, 67, 527 vinegar flies 324 vinegaroons 36 vines 124 Viperidae 457 vipers 457 viral encephalitis 324 Virgil 13, 63 virgin forest 500 Virginia creeper 187 Virginia opossums 354, 362 viruses 114, 231, 402–404 vision 363, 366, 441 Vitaceae 187 vitamin C deficiency 58 vitamins 378–379 Vitis 187 Vitis rotundifolia 60, 187 Vitis vinifera 60 Vitousek, Peter 72 vivipary 371, 479, 538 volcanic ash 531 volcanoes adaptive radiation 7 Cretaceous extinction 151–152 deep oceans, biodiversity in 172 greenhouse effect 285 mass extinctions 374 Permian extinction 409 succession, ecological 506 voles 481 Volk, Tyler 267 Vonnegut, Kurt 165 Vostok ice core 282, 283 Voyage of HMS Beagle, The (Darwin) 163, 522 Vulpes vulpes 330 vultures 89, 132

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598 Index 598 tundra 

first entry

W

Wagner, Warren 109 Walden, or Life in the Woods (Thoreau) 521 wallabies 363 Wallace, Alfred Russel 542–545, 543, 548c Bates, Henry Walter 45 biodiversity, patterns of 50 biogeography 72 Darwin, Charles 165 natural selection 384 tropical rain forests and deforestation 527 Wallace’s line 527, 543 Wallin, Ivan E. 368, 508 walnuts 113, 186, 427 Walsh, Benjamin 493 Walsh, Christopher 67, 68 Waltheria ovata 169 wandering spider 498 warblers 405, 494, 533 Ward, Peter 223, 268, 373, 374 warm-blooded animals. See homeotherms Washingtonia filifera 179, 195 wasps arthropods 38 camouflage and mimicry 99 coevolution 120, 121 convergence 145 Cretaceous period, biodiversity in 155 insects 325–326 natural selection 389 pollination 420 spiders 498 wastewater 466 “Was the World Made for Man?” (Twain) 544 water balance 86 water bears 27 water birds 89 water boatmen 467 water chestnut 377 water cycle. See hydrological cycle water-holding frog 180 water hyacinth 84, 332–333, 372, 467 water lettuce 332–333, 372, 467 water molds 446 water oaks 185, 185 water ouzel 466 water pressure 171 water resources 242 water scorpions 467 watersheds 129 water storage 177 water striders 467 water temperature 465 water vapor 287, 311, 313 water vascular system 29 water velocity 465 wax myrtle 333 weapons 480 web(s) 497 webbed feet 456 Wedgwood, Emma 163, 164 Wedgwood, Josiah 161, 162 weeds xi agriculture 12–14 deserts, warm 180 life history, diversity of 349–351 population biology 426 resistance, evolution of 459–460 succession, ecological 501 weevils 325 Weinberg, W. 433 Weis, Arthur 389 Weller, Steve 492 Wells, W. C. 384 Welwitschia mirabilis 180 werewolf 264 West Africa 527 West Nile virus 404 Westoby, Mark 484

xviii+598_Biodiversity_F.indd 598

wetland animals 370 wetland oxygen depletion 13 wetland plants 371, 371t Weyerhauser Corporation 239 whales 111, 124, 171, 365, 365, 399 whale shark 246 wheat 10, 12, 58, 60, 263, 310 wheatgrass 61 whip scorpions 36, 436 whirligig beetles 467 whisk ferns 476 whistling spider 181 White, Gilbert 162 White, Lynn, Jr. 224, 225 whitebark pines 136, 137, 297, 540 white blood cells 353 white firs 502, 511 white oaks 6, 7, 73, 185, 308, 309 white pines 511 white spruce 76, 196 white-tailed deer 338, 518 Whittaker, Robert 55, 125 Wiener, Norbert 55 wild barley 10 wild cattails 61 wild coffee trees 60 wild donkeys 173 Wilderness Act 549c Wilderness Areas 242 wilderness preservation 378 wildfires boreal and subalpine forests 92 Carboniferous period, biodiversity in 103 deserts, cool 173 disturbances, ecological 198–201 greenhouse effect 286, 287 keystone species 343 temperate dry forests 517 tropical rain forests and deforestation 534 tundra 540 wildflowers 177, 199 adaptation 5–6 communities, ecological 128 deserts, warm 177 dicots 186 disjunct species 194–195 disturbances, ecological 198 Neogene period, biodiversity in 393 shrublands 487 speciation 491 tundra 538 wild grains 10 wild grapes 60, 187 wildlife management 347 wild mustard 12 wild oats 12, 278 wild plant species 57–60 wild pollinators x, 421 wild tobacco 419, 420 wild type 430 wild wheat 10, 60 wild wheatgrass 61 will-o’-the-wisp 370 willow bark 66 willows 74, 186, 505, 538 Willson, Mary 483 Wilson, Edward O. x, 57, 225–228, 235, 247, 335, 336, 545–547 wind dispersal 253, 470 wind pollination coevolution 119–120 conifers 135 convergence 144 flowering plants 253 monocots 376 pollination 417 temperate deciduous forests 513 tropical rain forests and deforestation 526

wine industry 60 wings 37, 147, 320, 321, 365–366 witchcraft 264 witchweed 403 within-habitat diversity 48 Woese, Carl R. 32–33, 508, 549c Wolbachia 203, 404 Wolffia 467 wolf spiders 498, 498 Wollemia nobilis 51, 136 Wollemi pine 51, 136, 477 wolves 46, 78, 220, 308, 344, 363 wombats 363 wood 253 woodpecker finch 134, 169 woodpeckers 89–90, 134 wood pores 350t woolly adelgid bugs 2 World War II 149, 263 worms 24, 26–29, 31, 122, 172, 402, 403, 467 Wrangel Island 75 Wright, Angus 109, 422 Wright, Sewall 434 Wright, Shane 49 wrist 16 Wyoming 220, 511

X

Xenopsylla cheopsis 38, 323 Xenopus laevis 18 Xenoturbellida 28 xiphosuran arthropods 46 Xylaria 264 xylem 183, 254, 255, 472, 477 Xyphosura 37

Y

Yakushima Island 137 yaws 404 yeast 262, 380 yeast infections 262 yellow-billed oxpeckers 122 yellow fever 324 Yellowstone National Park 220, 239, 537, 548c Yellowstone to Yukon Conservation Initiative 302 yews 66, 67, 136 Yosemite National Park 239, 345, 378 Yosemite Valley 377–378 Younger Dryas 285 Yucatán rain forest 527 yucca 175

Z

Zahavi, Amotz 480 Zaire 56 Zea diploperennis 234 Zea mays 12, 234 zebra mussels 26, 330 zebras 98 Zhang, Xiaoyang 296 zoo animals 159, 234 zoonotic diseases 404 zooplankton 345, 469 zoospores 447 zooxanthellae 122, 149, 447 zosterophylls 473 Zuk, Marlene 480 Zygochloa paradoxa 180 Zygomycota 261 Zygophyllaceae 180 zygosporangium 261 zygote 473, 474, 477

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