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A Primer of Conservation Genetics
The biological diversity of our planet is rapidly being depleted due to di-
rect and indirect consequences of human activities. As the size of animal
and plant populations decreases, loss of genetic diversity reduces their
ability to adapt to
changes in the environment,
with inbreeding depres-
sion an inevitable consequence for many species. This concise, entry-level
text provides an introduction to the role of genetics in conservation and
presents the essentials of the discipline. Topics covered include:
r
loss of genetic diversity in small populations
r
inbreeding and loss of fitness
r
resolution of taxonomic uncertainties
r
genetic management of threatened species
r
contributions of molecular genetics to conservation
The authors assume only a basic knowledge of Mendelian genetics and
simple statistics, making the book accessible to those with a limited back-
ground in these areas. Connections between conservation genetics and
the wider field of conservation biology are interwoven throughout the
book.
The text is presented in an easy-to-follow format, with main points
and terms clearly highlighted. Worked examples are provided throughout
to help illustrate key eq
uations. A glossary and sugges
tions for further
reading provide additional support for the reader and many beautiful
pen-and-ink portraits of endangered species help bring the material to
life.
Written for short, introductory-level courses in genetics, conservation
genetics and conservation biology, this book will also be suitable for prac-
tising conservation biologists, zoo biologists and wildlife managers need-
ing a brief, accessible account of the significance of genetics to conserva-
tion.
dick frankham was employed in the Department of Biological Sci-
ences at Macquarie University, Sydney for 31 years and was Hrdy Visiting
Professor at Harvard University for spring semester 2004. He holds hon-
orary professorial appointments at Macquarie University, James Cook
University and the Australian Museum.
jon ballou is Head of the Depar
tment of Conservation Biology at the
Smithsonian Institution’s National Zoological Park.
david briscoe is Associate Professor at the Key Centre for Biodiversity
and Bioresources, Department of Biological Sciences, Macquarie Univer-
sity, Sydney.
A Primer of
Conservation Genetics
Richard Frankham
Macquarie University, Sydney
Jonathan D. Ballou
Smithsonian Institution, Washington, DC
David A. Briscoe
Macquarie University, Sydney
Line drawings by
Karina H. McInnes
Melbourne
cambridge university press
Cambridge, New York, Melbourne, Madrid, Cape Town, Singapore, São Paulo
Cambridge University Press
The Edinburgh Building, Cambridge cb2 2ru, UK
First published in print format
isbn-13 978-0-521-83110-9
isbn-13 978-0-521-53827-5
isbn-13 978-0-511-18661-5
© R. Frankham, Smithsonian Institution, D. Briscoe 2004
2004
Information on this title: www.cambrid
g
e.or
g
/9780521831109
This publication is in copyright. Subject to statutory exception and to the provision of
relevant collective licensing agreements, no reproduction of any part may take place
without the written permission of Cambridge University Press.
isbn-10 0-511-18661-4
isbn-10 0-521-83110-5
isbn-10 0-521-53827-0
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for external or third-party internet websites referred to in this publication, and does not
guarantee that any content on such websites is, or will remain, accurate or appropriate.
Published in the United States of America by Cambridge University Press, New York
www.cambridge.org
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Contents
Preface
page ix
Take-home messages
xi
Acknowledgments
xiii
Chapter 1 Introduction
1
The ‘sixth extinction’ 2
Why conserve biodiversity? 2
Endangered and extinct species 3
What is a threatened species? 4
What causes extinctions? 6
What is conservation genetics? 6
Suggested further reading 10
Chapter 2 Genetic diversity
12
Importance of genetic diversity 13
What is genetic diversity? 13
Measuring genetic diversity 13
Hardy Weinberg
equilibrium 16
Extent of genetic diversity 20
Low genetic diversity in threatened species 29
What components of genetic diversity determine
the ability to evolve? 30
Suggested further reading 30
Chapter 3 Evolutionary genetics of natural
populations
31
Factors controlling the evolution of populations 32
Origin and regeneration of genetic diversity 33
Mutation 33
Migration and gene flow 35
Selection and adaptation 37
Genotype × environment interaction 47
Mutation selection balance 49
Suggested further reading 50
Chapter 4 Genetic consequences of small population
size
52
Importance of small populations in conservation biology 53
Loss of genetic diversity 54
Chance effects and genetic drift 54
Genetic drift 55
vi CONTENTS
Effects of sustained population size
restrictions on genetic
diversity 57
Inbreeding 58
Inbreeding in small random mating populations 63
Measuring population size 64
Population fragmentation 70
Selection in small populations 75
Suggested further reading 75
Chapter 5 Genetics and extinction
76
Genetics and the fate of endangered species 77
Inbreeding depression 77
Measuring inbreeding depression 80
Relationship between inbreeding and extinction 82
Relationship between loss of genetic diversity
and extinction 86
Geneticall
y viable populations 88
Population viability analysis (PVA) 93
Suggested furth
er reading 99
Chapter 6 Resolving taxonomic uncertainties and
defining management units
101
Importance of accurate taxonomy in conservation biology 102
What is a species? 104
Sub-species 105
How do species arise? 106
Use of genetic analyses in delineating species 108
Genetic distance 112
Constructing phylogenetic trees 114
Outbreeding depression 116
Defining management units within species 118
Suggested further reading 121
Chapter 7 Genetic management of endangered
species in the wild
123
Genetic issues in endangered populations 124
Increasing
population size 126
Diagnosing genetic problems
128
Recovering small inbred populations with low
genetic diversity 129
Genetic management of fragmented populations
131
Genetic issues
in reserve design 136
Introgression and hybridization 137
Impacts of harvesting 138
Genetic management of species that are not outbreeding
diploids 139
CONTENTS vii
Evaluating recovery strategies
140
Supplemental breeding and assisted reproductive
technologies 142
Suggested further reading 144
Chapter 8 Captive breeding and reintroduction
145
Why captive breed? 146
Stages in captive breeding and reintroduction 147
Founding captive populations 148
Growth of captive populations 149
Genetic management during the maintenance phase 149
Ex situ conservation of plants 155
Management of inherited diseases 155
Reintroductions 157
Case studies in captive breeding and reintroduction 165
Suggested further reading 167
Chapter 9 Molecular genetics in forensics and
understanding species biology
168
Forensics: detecting illegal hunting and collecting 169
Understan
d
ing species’ b
iology is critical to its
conservation 171
Gene trees and coalescence 172
Population size and demographic history 177
Gene flow and population structure 180
Reintroduction and translocation 184
Breeding systems, parentage, founder relationships
and sexing 185
Disease 191
Diet 192
Suggested further reading 192
Final messages
193
Glossary
194
Sources and copyright acknowledgments
206
Index
212
[...]... relative frequency of a particular allele in a population (often referred to as gene frequency) For example, if a population of a diploid species has 8 A1 A1 individuals and 2 A1 A2 individuals, then there are 18 copies of the A1 allele and 2 of the A2 allele Thus, the A1 allele has a frequency of 0.9 and the A2 allele a frequency of 0.1 Polymorphic The presence in a species of two or more alleles at... populations are considered to be a valuable genetic resource for re-establishing mainland populations, particularly in Australia and New Zealand However, molecular genetic analyses revealed that the black-footed rock wallaby population on Barrow Island, Australia (a potential source of individuals for reintroductions onto the mainland) has extremely low genetic variation and reduced reproductive rate... breeds All derive from the gray wolf Genetic diversity can be measured at a number of different levels This includes diversity in measurable characters (quantitative variation), the visible direct effects of deleterious alleles, variation in proteins, and direct measurement of variation in DNA sequences Quantitative variation The characters of most importance in conservation are quantitative characters... years When extinctions are balanced by the origin of new species (speciation), biodiversity is maintained Mass extinctions, such as the cosmic cataclysm that eliminated much of the flora and fauna at the end of the Cretaceous, 65 million years ago, are different It took many millions of years for proliferation of mammals and angiosperm plants to replace the pre-existing dinosaurs and gymnosperm plants... , A1 A2 or A2 A2 Genotypes are heterozygous (A1 A2 ) or homozygous (A1 A1 or A2 A2 ) Genome The complete genetic material of a species, or individual; the entire DNA nucleotide sequence, including all of the loci and all of the chromosomes Homozygote An individual with two copies of the same allele at a locus, e.g A1 A1 Heterozygote An individual with two different alleles at a locus, e.g A1 A2 Allele... stochasticity, inbreeding, inbreeding depression, purging, speciation, stochastic, threatened, vulnerable Selection of threatened species: Clockwise: panda (China), an Australian orchid, palm cockatoo (Australia), tuatara (New Zealand), poison arrow frog (South America), lungfish (Australia), Wollemi pine (Australia) and Corsican swallow-tail butterfly 2 INTRODUCTION The ‘sixth extinction’ The biological... inbreeding) Some numerically smaller and more endangered mainland populations are genetically healthier and are therefore a more suitable source of animals for reintroductions to other mainland localities Alternatively, the pooling of several different Black-footed rock wallaby 9 10 INTRODUCTION island populations of this wallaby could provide a genetically healthy population suitable for reintroduction... and a substantial proportion of currently threatened species, are on islands (Table 1.1) For example, 81% of all extinct birds lived on islands, four-fold greater than the proportion of bird species that have lived on islands Extent of endangerment 18% of vertebrate animal species, 29% of invertebrates and 49% of plant species are classified as threatened IUCN, the World Conservation Union, defines as... reintroduction Molecular analyses may provide additional information on the historical distribution of species, expanding possibilities for conservation action For ecological reasons, reintroductions should preferably occur within a species’ historical range The northern hairy-nosed wombat exists in a single population of approximately 100 animals at Clermont in Queensland, Australia DNA samples obtained from... population genetics (allele frequencies and Hardy Weinberg equilibrium) Conservation professionals with little genetics background wishing for a brief authoritative introduction to conservation genetics should find it understandable These include wildlife biologists and ecologists, zoo staff undertaking captive breeding programs, planners and managers of national parks, water catchments and local government areas, . species
Selection of threatened species:
Clockwise: panda (China), an
Australian orchid, palm cockatoo
(Australia), tuatara (New Zealand),
poison arrow frog (South
America),. species that are
incapable
of surviving in their natural
habitats. Captive popula-
tions of threatened species are typically managed to retain 90% of
their
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