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Genotypic and phenotypic consequences of reintroduction history in the black-footed ferret (<Emphasis Type="Italic">Mustela nigripes</Emphasis>)
Authors:Samantha M Wisely  Rachel M Santymire  Travis M Livieri  Sara A Mueting  JoGayle Howard
Institution:(1) Division of Biology, Kansas State University, 116 Ackert Hall, Manhattan, KS 66506, USA;(2) Davee Center for Epidemiology and Endocrinology, Lincoln Park Zoo, 2001 N. Clark Street, Chicago, IL 60614, USA;(3) Department of Reproductive Science, Conservation &; Research Center, Smithsonian’s National Zoological Park, 1500 Remount Road, Front Royal, VA 22630, USA;(4) Prairie Wildlife Research, P.O. Box 308, Wellington, CO 80549, USA;(5) Department of Reproductive Sciences, Smithsonian’s National Zoological Park, 3001 Connecticut Avenue NW, Washington, DC 20008, USA
Abstract:Population augmentation with translocated individuals has been shown to alleviate the effects of bottlenecks and drift. The first step to determine whether restoration for genetic considerations is warranted is to genetically monitor reintroduced populations and compare results to those from the source. To assess the need for genetic restoration, we evaluated genetic diversity and structure of reintroduced (n = 3) and captive populations of the endangered black-footed ferret (Mustela nigripes). We measured genotypic changes among populations using seven microsatellite markers and compared phenotypic changes with eight morphometric characters. Results indicated that for the population which rapidly grew post-reintroduction, genetic diversity was equivalent to the captive, source population. When growth languished, only the population that was augmented yearly maintained diversity. Without augmentation, allelic diversity declined precipitously and phenotypic changes were apparent. Ferrets from the genetically depaupertate population had smaller limbs and smaller overall body size than ferrets from the two populations with greater diversity. Population divergence (F ST = 0.10 ± 0.01) was surprisingly high given the common source of populations. Thus, it appears that 5–10 years of isolation resulted in both genotypic divergence and phenotypic changes to populations. We recommend translocation of 30–40 captive individuals per annum to reintroduction sites which have not become established quickly. This approach will maximize the retention of genetic diversity, yet maintain the beneficial effects of local adaptation without being swamped by immigration.
Keywords:Genetic monitoring  Genetic restoration  Population bottleneck  Reintroduction  Translocation
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