Applying Population Viability Analysis to Inform Genetic Rescue That Preserves Locally Unique Genetic Variation in a Critically Endangered Mammal
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Effective Population Size and Genetic Conservation Criteria for Bull Trout
North American Journal of Fisheries Management 21:756±764, 2001 q Copyright by the American Fisheries Society 2001 Effective Population Size and Genetic Conservation Criteria for Bull Trout B. E. RIEMAN* U.S. Department of Agriculture Forest Service, Rocky Mountain Research Station, 316 East Myrtle, Boise, Idaho 83702, USA F. W. A LLENDORF Division of Biological Sciences, University of Montana, Missoula, Montana 59812, USA Abstract.ÐEffective population size (Ne) is an important concept in the management of threatened species like bull trout Salvelinus con¯uentus. General guidelines suggest that effective population sizes of 50 or 500 are essential to minimize inbreeding effects or maintain adaptive genetic variation, respectively. Although Ne strongly depends on census population size, it also depends on demographic and life history characteristics that complicate any estimates. This is an especially dif®cult problem for species like bull trout, which have overlapping generations; biologists may monitor annual population number but lack more detailed information on demographic population structure or life history. We used a generalized, age-structured simulation model to relate Ne to adult numbers under a range of life histories and other conditions characteristic of bull trout populations. Effective population size varied strongly with the effects of the demographic and environmental variation included in our simulations. Our most realistic estimates of Ne were between about 0.5 and 1.0 times the mean number of adults spawning annually. We conclude that cautious long-term management goals for bull trout populations should include an average of at least 1,000 adults spawning each year. Where local populations are too small, managers should seek to conserve a collection of interconnected populations that is at least large enough in total to meet this minimum. -
Genetic and Demographic Dynamics of Small Populations of Silene Latifolia
Heredity (2003) 90, 181–186 & 2003 Nature Publishing Group All rights reserved 0018-067X/03 $25.00 www.nature.com/hdy Genetic and demographic dynamics of small populations of Silene latifolia CM Richards, SN Emery and DE McCauley Department of Biological Sciences, Vanderbilt University, PO Box 1812, Station B, Nashville, TN 37235, USA Small local populations of Silene alba, a short-lived herbac- populations doubled in size between samples, while others eous plant, were sampled in 1994 and again in 1999. shrank by more than 75%. Similarly, expected heterozygosity Sampling included estimates of population size and genetic and allele number increased by more than two-fold in diversity, as measured at six polymorphic allozyme loci. individual populations and decreased by more than three- When averaged across populations, there was very little fold in others. When population-specific change in number change between samples (about three generations) in and change in measures of genetic diversity were considered population size, measures of within-population genetic together, significant positive correlations were found be- diversity such as number of alleles or expected hetero- tween the demographic and genetic variables. It is specu- zygosity, or in the apportionment of genetic diversity within lated that some populations were released from the and among populations as measured by Fst. However, demographic consequences of inbreeding depression by individual populations changed considerably, both in terms gene flow. of numbers of individuals and genetic composition. Some Heredity (2003) 90, 181–186. doi:10.1038/sj.hdy.6800214 Keywords: genetic diversity; demography; inbreeding depression; gene flow Introduction 1986; Lynch et al, 1995), the interaction of genetics and demography could also influence population persistence How genetics and demography interact to influence in common species, because it is generally accepted that population viability has been a long-standing question in even many abundant species are not uniformly distrib- conservation biology. -
4 Genetics of Small Populations: the Case of the Laysan Finch
Case Studies in Ecology and Evolution DRAFT 4 Genetics of Small Populations: the case of the Laysan Finch In 1903, rabbits were introduced to a tiny island in the Hawaiian archipelago called Laysan Island. That island is only 187 ha in size, in the middle of the Pacific Ocean about 1000 km northeast of Hawaii. Despite the benign intentions for having rabbits on the island, the released rabbits quickly multiplied and devoured most of the vegetation. Oceanic islands are often home to unique or endemic species that have evolved in isolation. Laysan was no exception. Well-known examples of island endemics include the finches on the Galapagos Islands and the dodo that was only known from the islands of Mauritius. On Laysan there were several species of birds and plants that were known only from that single island. The introduced rabbits on the island destroyed the food supply for various species of land birds. Several endemic species of plants and animals were driven extinct, including the Laysan rail, the Laysan honeycreeper, the millerbird, and plants like the Laysan fan palm. Only 4 of 26 species of plants remained on the island in 1923, 20 years after the rabbits first arrived. Populations of other species declined to very small levels. One of the two surviving endemic land birds was a small finch called the Laysan finch, Telespiza cantans. After the rabbits were finally exterminated in 1923, the population of finches recovered on Laysan Island. Over the last four decades the average population size of on Laysan Island has been about 11,000 birds. -
Amphibian Cascades Frog SOC X X Mountain Meadows, Bogs, Ponds Or
Taxa Species Species SMU/ESU/D Federal State BM CP CR EC KM NR WC WV NS Special needs Limiting factors Data gaps Conservation actions Key reference or plan, if available Common Scientific PS/Group Listing listing Name Name Status status Amphibian Cascades SOC X X Mountain meadows, bogs, ponds or potholes Montane species vulnerable to genetic Habitat requirements and how they may vary by Maintain connectivity of habitat. Monitor effects of fish http://www.fs.fed.us/psw/publications/documents/ frog above 2,400 feet elevation. Requires access isolation. Experiencing substantial elevation within the species' range. Habitat stocking and water quality on populations. Carefully manage psw_gtr244/psw_gtr244.pdf to permanent water. Lays eggs in shallow reductions in southern parts of range characteristics that could enhance migration livestock grazing in occupied wet meadows. Use prescribed sunny edges of ponds, or on low vegetation (e.g., CA). Potentially sensitive to and gene flow. Feeding habits. Effects of burning or hand-felling of trees periodically to set plant near ponds where warm sunlight speeds egg waterborne pathogens. pathogens airborne environmental pollution. succession. If reintroductions are warranted, use individuals development. Larvae may “school” in large Feasibility studies on reintroduction at historic from nearby populations and consult results of feasibility masses. sites. studies. Conservation actions in Oregon are particularly valuable given reductions in other parts of range. Amphibian Cascade X X Cold, fast-flowing, clear, permanent headwater Larvae take several years to reach sexual Basic inventory, abundance and population Maintain stream buffers to maintain cool water Howell, B.L. and N. M. Maggiulli. 2011. -
Translocations and the 'Genetic Rescue' of Bottlenecked Populations
Translocations and the ‘genetic rescue’ of bottlenecked populations ATHESIS SUBMITTED IN PARTIAL FULFILMENT OF THE REQUIREMENTS FOR THE DEGREE OF DOCTOR OF PHILOSOPHY IN WILDLIFE CONSERVATION AT THE UNIVERSITY OF CANTERBURY SOL HEBER SEPTEMBER 2012 Abstract Many species around the world have passed through severe population bottlenecks due to an- thropogenic influences such as habitat loss or fragmentation, the introduction of exotic predators, pollution and excessive hunting. Severe bottlenecks are expected to lead to increased inbreed- ing depression and the loss of genetic diversity, and hence reduce the long-term viability of post- bottlenecked populations. The objective of this thesis was to examine both the consequences of severe bottlenecks and the use of translocations to ameliorate the effects of inbreeding due to bot- tlenecks. Given the predicted increase in probability of inbreeding in smaller populations, one would expect inbreeding depression to increase as the size of a population bottleneck decreases. Deter- mining the generality of such a relationship is critical to conservation efforts aimed at minimising inbreeding depression among threatened species. I therefore investigated the relationship between bottleneck size and population viability using hatching failure as a fitness measure in a sample of threatened bird species worldwide. Bottleneck size had a significant negative effect on hatch- ing failure, and this relationship held when controlling for confounding effects of phylogeny, body size, clutch size, time since bottleneck, and latitude. All species passing through bottlenecks of ∼100–150 individuals exhibited increased hatching failure. My results confirm that the negative consequences of bottlenecks on hatching success are widespread, and highlight the need for conser- vation managers to prevent severe bottlenecks. -
The Alluring Simplicity and Complex Reality of Genetic Rescue
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Publications, Agencies and Staff of the U.S. Department of Commerce U.S. Department of Commerce 9-2004 The alluring simplicity and complex reality of genetic rescue David A. Tallmon University of Alaska Southeast, [email protected] Gordon Luikart University of Montana, [email protected] Robin Waples NOAA, [email protected] Follow this and additional works at: https://digitalcommons.unl.edu/usdeptcommercepub Tallmon, David A.; Luikart, Gordon; and Waples, Robin, "The alluring simplicity and complex reality of genetic rescue" (2004). Publications, Agencies and Staff of the U.S. Department of Commerce. 480. https://digitalcommons.unl.edu/usdeptcommercepub/480 This Article is brought to you for free and open access by the U.S. Department of Commerce at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Publications, Agencies and Staff of the U.S. Department of Commerce by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Review TRENDS in Ecology and Evolution Vol.19 No.9 September 2004 The alluring simplicity and complex reality of genetic rescue David A. Tallmon1, Gordon Luikart1 and Robin S. Waples2 aLaboratoire d’Ecologie Alpine, Ge´nomique des Populations et Biodiversite´, CNRS UMR 5553, Universite´Joseph Fourier, BP 53, 38041 Grenoble, Cedex 09, France bNational Marine Fisheries Service, Northwest Fisheries Science Center, 2725 Montlake Boulevard East, Seattle, WA 98112, USA A series of important new theoretical, experimental and yet crucial role in the evolution of small natural observational studies demonstrate that just a few populations and can, under some circumstances, be an immigrants can have positive immediate impacts on effective conservation tool. -
Understanding the Ecology of Extinction: Are We Close to the Critical Threshold?
Ann. Zool. Fennici 40: 71–80 ISSN 0003-455X Helsinki 30 April 2003 © Finnish Zoological and Botanical Publishing Board 2003 Understanding the ecology of extinction: are we close to the critical threshold? Tim G. Benton Institute of Biological Sciences, University of Stirling, FK9 4LA, UK (e-mail: [email protected]) Received 25 Nov. 2002, revised version received 20 Jan. 2003, accepted 21 Jan. 2003 Benton, T. G. 2003: Understanding the ecology of extinction: are we close to the critical threshold? — Ann. Zool. Fennici 40: 71–80. How much do we understand about the ecology of extinction? A review of recent lit- erature, and a recent conference in Helsinki gives a snapshot of the “state of the art”*. This “snapshot” is important as it highlights what we currently know, the tools avail- able for studying the process of extinction, its ecological correlates, and the theory concerning extinction thresholds. It also highlights that insight into the ecology of extinction can come from areas as diverse as the study of culture, the fossil record and epidemiology. Furthermore, it indicates where the gaps in knowledge and understand- ing exist. Of particular note is the need either to generate experimental data, or to make use of existing empirical data — perhaps through meta-analyses, to test general theory and guide its future development. Introduction IUCNʼs 2002 Red List, a total of 11 167 species are currently known to be threatened (http:// Few would argue that managing natural popu- www.redlist.org/info/tables/table1.html), though lations and their habitats is one of the greatest this is a gross underestimate of the true value, as, challenges for humans in the 21st century. -
Genetic Mixing for Population Management: from Genetic Rescue to Provenancing
Received: 20 August 2020 | Revised: 10 October 2020 | Accepted: 14 October 2020 DOI: 10.1111/eva.13154 REVIEWS AND SYNTHESES Genetic mixing for population management: From genetic rescue to provenancing Ary A. Hoffmann1 | Adam D. Miller2,3 | Andrew R. Weeks1,4 1School of BioSciences, Bio21 Institute, The University of Melbourne, Parkville, Vic., Abstract Australia Animal and plant species around the world are being challenged by the deleterious 2 School of Life and Environmental Sciences, effects of inbreeding, loss of genetic diversity, and maladaptation due to widespread Centre for Integrative Ecology, Deakin University, Warrnambool, Vic., Australia habitat destruction and rapid climate change. In many cases, interventions will likely 3Deakin Genomics Centre, Deakin be needed to safeguard populations and species and to maintain functioning eco- University, Geelong, Vic., Australia systems. Strategies aimed at initiating, reinstating, or enhancing patterns of gene 4cesar Pty Ltd, Parkville, Vic., Australia flow via the deliberate movement of genotypes around the environment are gen- Correspondence erating growing interest with broad applications in conservation and environmental Ary A. Hoffmann, School of BioSciences, Bio21 Institute, The University of management. These diverse strategies go by various names ranging from genetic or Melbourne, Parkville, Vic., Australia. evolutionary rescue to provenancing and genetic resurrection. Our aim here is to Email: [email protected] provide some clarification around terminology and to how these strategies are con- nected and linked to underlying genetic processes. We draw on case studies from the literature and outline mechanisms that underlie how the various strategies aim to increase species fitness and impact the wider community. We argue that under- standing mechanisms leading to species decline and community impact is a key to successful implementation of these strategies. -
Preserving Evolutionary Potential: the Role of Genetic Rescue Jill Hamilton North Dakota State University Genetic Consequences of Rarity
Preserving evolutionary potential: the role of genetic rescue Jill Hamilton North Dakota State University Genetic consequences of rarity Genetic Demographic variation variation Inbreeding depression Population growth rate Outbreeding depression Reproductive rates Ne Evolutionary Potential? Environmental variation Fluctuations Disease Stress How might genetic rescue impact a species evolutionary potential? Natural or facilitated introduction of genetic variation from unrelated individuals with an aim to increase population fitness Environmental change Extinction threshold (Hamilton and Miller 2016, Conservation Biology) Maladaptation to changing conditions could lead to extinction Environmental change Extinction threshold Maladaptation Extinction (Hamilton and Miller 2016, Conservation Biology) Evolutionary rescue from standing genetic variation Environmental change Rescue via standing variation Extinction threshold Maladaptation Extinction (Hamilton and Miller 2016, Conservation Biology) Gene flow reduces demographic consequences of maladaptation Environmental change Introduction Rescue via gene flow * of variation Rescue via standing variation Extinction threshold Maladaptation Extinction (Hamilton and Miller 2016, Conservation Biology) One of the rarest pine species in the world, Torrey pine is restricted to one mainland and one island population Santa Rosa Island an expanding population Torrey Pines State Reserve abiotic and biotic challenges Genetics: exceptionally low levels of genetic diversity in a conifer • 59 allozyme gene -
Forecasting Extinctions: Uncertainties and Limitations
Diversity 2009, 1, 133-150; doi:10.3390/d1020133 OPEN ACCESS diversity ISSN 2071-1050 www.mdpi.com/journal/diversity Review Forecasting Extinctions: Uncertainties and Limitations Richard J. Ladle 1,2 1 School of Geography and the Environment, Oxford University, South Parks Road, Oxford, UK; E-Mail: [email protected]; Tel.: +55-31-3899 1902; Fax: +55-31-3899-2735 2 Department of Agricultural and Environmental Engineering, Federal University of Viçosa, Viçosa, Brazil Received: 13 October 2009 / Accepted: 14 November 2009 / Published: 26 November 2009 Abstract: Extinction forecasting is one of the most important and challenging areas of conservation biology. Overestimates of extinction rates or the extinction risk of a particular species instigate accusations of hype and overblown conservation rhetoric. Conversely, underestimates may result in limited resources being allocated to other species/habitats perceived as being at greater risk. In this paper I review extinction models and identify the key sources of uncertainty for each. All reviewed methods which claim to estimate extinction probabilities have severe limitations, independent of if they are based on ecological theory or on rather subjective expert judgments. Keywords: extinction; uncertainty; forecasting; local extinction; viability 1. Introduction ―Prediction is very difficult, especially about the future‖ Nils Bohr, Nobel Prize winning physicist Preventing the extinction of species is probably the most emblematic objective of the global conservation movement. To fulfill this aim effectively requires that decision makers and environmental managers are provided with accurate information on: (1) the identities of specific species/populations with a high probability of going extinct without further interventions; (2) the predicted rates of extinction among a range of taxa in different geographic areas and biomes under various ecological scenarios. -
Evaluating the Small Population Paradigm for Rare Large-Bodied Woodpeckers, with Implications for the Ivory-Billed Woodpecker
Copyright © 2008 by the author(s). Published here under license by the Resilience Alliance. Mattsson, B. J., R. S. Mordecai, M. J. Conroy, J. T. Peterson, R. J. Cooper, and H. Christensen. 2008. Evaluating the small population paradigm for rare large-bodied woodpeckers, with implications for the Ivory-billed Woodpecker. Avian Conservation and Ecology - Écologie et conservation des oiseaux 3(2): 5. [online] URL: http://www.ace-eco.org/vol3/iss2/art5/ Research Papers Evaluating the Small Population Paradigm for Rare Large-Bodied Woodpeckers, with Implications for the Ivory-billed Woodpecker Évaluation du paradigme des petites populations pour les pics de grande taille et implications pour le Pic à bec ivoire Brady J. Mattsson 1, Rua S. Mordecai 1, Michael J. Conroy 1, James T. Peterson 1, Robert J. Cooper 1, and Hans Christensen 2 ABSTRACT. Six large-bodied, ≥ 120 g, woodpecker species are listed as near-threatened to critically endangered by the International Union for Conservation of Nature (IUCN). The small population paradigm assumes that these populations are likely to become extinct without an increase in numbers, but the combined influences of initial population size and demographic rates, i.e., annual adult survival and fecundity, may drive population persistence for these species. We applied a stochastic, stage-based single-population model to available demographic rates for Dryocopus and Campephilus woodpeckers. In particular, we determined the change in predicted extinction rate, i.e., proportion of simulated populations that went extinct within 100 yr, to concomitant changes in six input parameters. To our knowledge, this is the first study to evaluate the combined importance of initial population size and demographic rates for the persistence of large- bodied woodpeckers. -
Dynamics of Genetic Rescue in Inbred Drosophila Melanogaster Populations
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Springer - Publisher Connector Conserv Genet (2010) 11:449–462 DOI 10.1007/s10592-010-0058-z RESEARCH ARTICLE Dynamics of genetic rescue in inbred Drosophila melanogaster populations R. Bijlsma • M. D. D. Westerhof • L. P. Roekx • I. Pen Received: 11 October 2009 / Accepted: 23 December 2009 / Published online: 4 February 2010 Ó The Author(s) 2010. This article is published with open access at Springerlink.com Abstract Genetic rescue has been proposed as a man- deleterious at 25°C but lethal at 29°C. By comparing fitness agement strategy to improve the fitness of genetically eroded at 25°C (the temperature during the rescue experiment) and populations by alleviating inbreeding depression. We stud- 29°C, we show that the lethal allele reached significant ied the dynamics of genetic rescue in inbred populations of frequencies in most rescued populations, which upon Drosophila. Using balancer chromosomes, we show that the renewed inbreeding became fixed in part of the inbred lines. force of heterosis that accompanies genetic rescue is large In conclusion, in addition to the fitness increase genetic and allows even a recessive lethal to increase substantially in rescue can easily result in a substantial increase in the fre- frequency in the rescued populations, particularly at stress quency of mildly deleterious alleles carried by the immi- temperatures. This indicates that deleterious alleles present grants. This can endanger the rescued population greatly in the immigrants can increase significantly in frequency in when it undergoes recurrent inbreeding.