ReviewThe effects of captive experience on reintroduction survival in carnivores: A review and analysis
Section snippets
Brief introduction and background
Humans have a long history of translocating animals, whether by intention or not. In the past, intentional translocations of animals have predominantly been for the purpose of supplementing game species. However, more recently, translocation for the purpose of re-establishing endangered animals into their native habitat has become an increasingly popular conservation technique (MacKinnon and MacKinnon, 1991, Stuart, 1991). The IUCN (International Union for the Conservation of Nature and Natural
Previous reintroductions for conservation
There have been a number of well publicized reintroductions carried out for conservation purposes, e.g. golden lion tamarin (Kleiman and Mallinson, 1998), red wolf (Oakleaf et al., 2004), California condor (Toone and Wallace, 1994), black-footed ferret (Russell et al., 1994), and Arabian oryx (Stanley Price, 1989). Most of the animals used in these projects were either captive-born or brought into captivity due to their near extinct status. To evaluate the outcome of these projects, many have
Previous reviews and their findings on the effect of source population
Out of the several previously published reviews, three in particular, Griffith et al., 1989, Wolf et al., 1996, Fischer and Lindenmayer, 2000, have reported differences between the success rates of reintroduction projects and the source of animals used, and in all cases projects using captive-born animals averaged a lower success rate than those using wild-caught. Further to their 1989 paper, Griffith et al. (1990) statistically reported that this difference was significant; however, they did
Why focus on carnivores?
Carnivores are well represented in reintroduction projects; this can be explained by the taxonomic bias observed in species selected for conservation. Conservation societies often use flagship species, for example the giant panda (Ailuropoda malanoleuca), to promote conservation efforts and these are often chosen for their visual appeal, e.g. flagship species are typically large mammals. This preference for animals with ‘visual appeal’ can also be seen in species selected for reintroduction
Main objectives
There are two main objectives for this paper. One was to statistically verify differences between the success rates of reintroduction projects (obtained from previously published reviews) based on their source of founder stock. The prediction is that projects using wild-caught animals will be more successful than those using captive-born animals (Mathews et al., 2005). The second objective was to provide an updated review and analysis on the survival rates of reintroduced and translocated
Literature search
The literature search was carried out on carnivore reintroduction and translocation projects that have been published post 1990. Literature was collected over a 5 month period in early 2005, and included over 25 journals, two of which were particularly applicable –Biological Conservation and Conservation Biology, and over 30 relevant books and symposium proceedings. Journals were searched via online databases and electronic journals, such as Web of Science, EBSCO, JSTOR, IngentaConnect, and
An analysis of success of reintroduction projects using wild-caught versus captive-born
The calculated G statistic on the results from Fischer and Lindenmayer’s (2000) review, shows that reintroduction projects appear to be significantly more likely to succeed when a wild source population is used (31% of 45 projects) than when animals from a captive source are used (13% of 52 projects); G = 4.466, df = 1, p = 0.035.
Survival of wild-caught versus captive-born animals and family differences
The results of the ANOVA show that wild-caught carnivores survived significantly more (53%) than captive-born carnivores (32%), F(1,4.66) = 17.697, p = 0.01; Fig. 1.
When
Success of projects based on results of previous publications
Our results support that the use of different source populations has an effect on the success of the project and corroborates Fischer and Lindenmayer, 2000, Griffith et al., 1989, Wolf et al., 1996 reviews. This evidence suggests that captivity negatively influences animals’ capabilities to survive, and can result in a lack of appropriate ‘wild’ type behaviours (Rabin, 2003). Other potential factors influencing captive animals’ lack of success can range from lack of immunities to diseases
Conclusion
Our findings support previous reports that reintroduction projects using wild-caught animals are more successful than those using captive-born animals. We also found that wild-caught carnivores are more likely to survive than captive-born carnivores in reintroductions and that this trend appears to remain consistent across species and families. Further reviews should be conducted on carnivores, as well as other species, in order to improve our understanding on how captivity affects survival in
Acknowledgements
The authors would like to thank the two reviewers for their constructive criticism and support, this manuscript has been much improved by incorporating their suggestions. We would also like to thank those members of our department who gave statistical advice and those who gave comments on final drafts.
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