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Vol. 15 - Deutsches Primatenzentrum

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Page 62 Lemur News <strong>Vol</strong>. <strong>15</strong>, 2010<br />

Frequency<br />

Frequency<br />

Frequency<br />

Frequency<br />

Frequency<br />

Frequency<br />

Frequency<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

Anjanaharibe-Sud<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Morontandrano<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Ambatovaky<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Zahamena<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Betampona<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Anjozorobe<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Mantadia<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Frequency<br />

Frequency<br />

Frequency<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

0,4<br />

0,3<br />

0,2<br />

0,1<br />

0<br />

Andasibe<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Maromizaha<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Anosibe an'ala<br />

-0,5 -0,3 -0,1 0,1 0,3 0,5 0,7 0,9<br />

Relationship Coefficients<br />

Parent-Offspring Full Sibling Half Sibling<br />

Unrelated All Populations<br />

Fig. 4: Distributions of relationship coefficients estimated in<br />

each population overlaid on a simulation of 10,000 known<br />

genotypes and pedigreed relationships (Queller and Goodnight,<br />

1989).<br />

a significantly high FIS estimate. Considering relationship<br />

among the samples as one manner of capturing inbreeding,all<br />

populations show some degree of relationship above what<br />

would be expected if the sampled individuals were unrelated.<br />

This is not surprising since samples were collected as found<br />

and this could include individuals that are members of a family<br />

group which is supported by the relationship coefficient<br />

distributions in Fig. 2.<br />

All populations demonstrated some degree of recent reduction<br />

in the effective population sizes.The bottlenecks did not<br />

appear to have been a single global event as different populations<br />

showed differing degrees to which the bottlenecks<br />

were detected. Using Lawler’s (2008) 4*Neb*generations,<br />

the bottlenecks detected would have had an expected window<br />

of occurrence of up to 250 to 800 years ago, within the<br />

timeframe of human encroachment. Hence, we postulate<br />

that among other things, anthropogenic disturbances,<br />

whether habitat destruction or subsistence hunting, may<br />

have influenced the demographic reduction that we detected<br />

in the bottleneck test. These baseline values could be useful<br />

in long-term or future studies to determine genetic health<br />

trends over time under various forest or habitat conditions.<br />

Genetic diversity is considered to be the most important<br />

factor in determining the genetic health of a species or population.Among<br />

the lemurs,there is little information in the literature<br />

that addresses the genetic diversity estimations for<br />

multiple populations of a given species. Ranaivoarisoa et al.<br />

(2010) found the observed heterozygosity in three of four<br />

Eulemur collaris populations to be higher than the expected<br />

heterozygosity. In E. coronatus, Ramanamahefa et al. (2010a)

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