The use of non-invasive molecular techniques to confirm the presence of mountain bongo Tragelaphus eurycerus isaaci populations in Kenya and preliminary inference of their mitochondrial genetic variation

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dc.contributor.author Kavembe, Geraldine D.
dc.contributor.author Faria, P. J.
dc.contributor.author Jung’a, J. O.
dc.contributor.author Kimwele, C. N.
dc.contributor.author Estes, L. D.
dc.contributor.author Reillo, P. R.
dc.contributor.author Mwangi, A. G.
dc.contributor.author Bruford, M. W.
dc.date.accessioned 2015-02-03T07:21:50Z
dc.date.available 2015-02-03T07:21:50Z
dc.date.issued 2011-06
dc.identifier.citation Conservation Genetics June 2011, Volume 12, Issue 3, pp 745-751 en_US
dc.identifier.issn 1566-0621
dc.identifier.uri http://www.princeton.edu/~lestes/Bongo/Results_files/Bongo%20Genetics.pdf
dc.identifier.uri http://hdl.handle.net/123456789/843
dc.description DOI 10.1007/s10592-011-0181-5 en_US
dc.description.abstract The mountain bongo antelope Tragelaphus eurycerus isaaci has rapidly declined in recent decades, due to a combination of hunting, habitat degradation and disease. Endemic to Kenya, mountain bongo populations have shrunk to approximately 100 individuals now mainly confined to the Aberdares mountain ranges. Indirect observation of bongo signs (e.g. tracks, dung) can be misleading, thus methods to ensure reliable species identification, such as DNA-based techniques, are necessary to effectively study and monitor this species. We assessed bongo presence in four mountain habitats in Kenya (Mount Kenya National Park, Aberdare National Park, Eburu and Mau forests) and carried out a preliminary analysis of genetic variation by examining 466 bp of the first domain of the mtDNA control region using DNA extracted from faecal samples. Of the 201 dung samples collected in the field, 102 samples were molecularly identified as bongo, 97 as waterbuck, one as African buffalo and one as Aders’ duiker. Overall species-identification accuracy by experienced trackers was 64%, with very high error of commission when identifying bongo sign (37%), and high error of omission for waterbuck sign (82%), suggesting that the two species’ signs are easily confused. Despite high variation in the mtDNA control region in most antelope species, our results suggest low genetic variation in mountain bongo as only two haplotypes were detected in 102 samples analyzed. In contrast, the analysis of 63 waterbuck samples from the same sites revealed 21 haplotypes. Nevertheless, further examination using nuclear DNA markers (e.g. microsatellites) in a multi-locus approach is still required, especially because the use of mitochondrial DNA can result in population overestimation as distinct dung samples can potentially be originated from the same individual. en_US
dc.language.iso en en_US
dc.publisher Springer Verlag en_US
dc.subject Bongo antelope en_US
dc.subject Non-invasive genetics en_US
dc.subject Endangered species en_US
dc.subject Genetic diversity en_US
dc.subject mtDNA control region en_US
dc.title The use of non-invasive molecular techniques to confirm the presence of mountain bongo Tragelaphus eurycerus isaaci populations in Kenya and preliminary inference of their mitochondrial genetic variation en_US
dc.type Article en_US


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