42 research outputs found

    Differences between Pygmy and Non-Pygmy hunting in Congo Basin forests

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    We use data on game harvest from 60 Pygmy and non-Pygmy settlements in the Congo Basin forests to examine whether hunting patterns and prey profiles differ between the two hunter groups. For each group, we calculate hunted animal numbers and biomass available per inhabitant, P, per year (harvest rates) and killed per hunter, H, per year (extraction rates). We assess the impact of hunting of both hunter groups from estimates of numbers and biomass of prey species killed per square kilometre, and by examining the proportion of hunted taxa of low, medium and high population growth rates as a measure of their vulnerability to overhunting. We then map harvested biomass (kg-1P-1Yr-1) of bushmeat by Pygmies and non-Pygmies throughout the Congo Basin. Hunting patterns differ between Pygmies and non-Pygmies; Pygmies take larger and different prey and non-Pygmies sell more for profit. We show that non-Pygmies have a potentially more severe impact on prey populations than Pygmies. This is because non-Pygmies hunt a wider range of species, and twice as many animals are taken per square kilometre. Moreover, in non-Pygmy settlements there was a larger proportion of game taken of low population growth rate. Our harvest map shows that the non-Pygmy population may be responsible for 27 times more animals harvested than the Pygmy population. Such differences indicate that the intense competition that may arise from the more widespread commercial hunting by non-Pygmies is a far more important constraint and source of conflict than are protected areas

    Co-occurrence patterns of five species of anurans at a pond network in Victoria Lake, Kenya RID F-2663-2011

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    we examine the community structure and co-occurrence patterns of amphibians inhabiting a pond network at Lake Victoria. Specifically, we answer to the following key questions: (i) within a same landscape scale, are amphibian assemblages from natural ponds different from those inhabiting artificial ponds? (ii) Are the amphibian communities randomly or nonrandomly organized? The results from multivariate analyses revealed the existence of three groups of species: (i) Xenopus victorianus being linked exclusively to artificial ponds, (ii) Phrynobatrachus natalensis being linked essentially to artificial ponds, and (iii) a third group being constituted by species mainly (Ptychadena mascareniensis) or exclusively (Hoplobatrachus occipitalis and Hemisus guineensis) linked to natural ponds. The recent origin of our artificial ponds seems linked to the random organization of the anuran communities
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