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the role of tourism in natural resource management in the okavango ...

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for several consecutive years, <strong>the</strong> devastation that <strong>the</strong> fences and <strong>the</strong> <strong>in</strong>creas<strong>in</strong>g<br />

livestock population has on <strong>the</strong> wildlife can be seen on <strong>the</strong> largest scale. Wildebeest<br />

are <strong>of</strong>ten <strong>the</strong> most seriously affected species <strong>in</strong> <strong>the</strong> Southwestern System s<strong>in</strong>ce <strong>the</strong>y<br />

are completely dependent on water. The largest concentration <strong>of</strong> wildebeest dur<strong>in</strong>g<br />

<strong>the</strong> wet season is along <strong>the</strong> boundary between <strong>the</strong> Ghanzi and Kgalagadi districts.<br />

However, <strong>the</strong>ir migration to <strong>the</strong> permanent water <strong>of</strong> <strong>the</strong> Okavango Delta <strong>in</strong> <strong>the</strong> dry<br />

season is restricted due to <strong>the</strong> Kuke Fence (Crowe, 1995). This restriction has<br />

caused a vast reduction <strong>in</strong> <strong>the</strong> wildebeest population. As Ross (1987) shows, <strong>the</strong><br />

drought years <strong>of</strong> <strong>the</strong> 1980s had a huge effect on <strong>the</strong> wildebeest population, where<br />

approximately 52 000 <strong>of</strong> <strong>the</strong> 80 000 wildebeest that migrated died.<br />

Eland and hartebeest populations have also been greatly affected by <strong>the</strong><br />

construction <strong>of</strong> <strong>the</strong> veter<strong>in</strong>ary cordon fences. The hartebeest <strong>in</strong> <strong>the</strong> Southwestern<br />

System historically migrated <strong>in</strong> a north-easterly direction from <strong>the</strong> Kgalagadi and<br />

Ghanzi districts. This movement however, is now restricted due to <strong>the</strong> construction<br />

<strong>of</strong> fences and an <strong>in</strong>creas<strong>in</strong>g amount <strong>of</strong> human settlements <strong>in</strong> <strong>the</strong> area. Hartebeest<br />

numbers have <strong>the</strong>refore decl<strong>in</strong>ed dramatically <strong>in</strong> <strong>the</strong> last 15 years, result<strong>in</strong>g <strong>in</strong> a loss<br />

<strong>of</strong> 83% <strong>of</strong> <strong>the</strong> population. As shown <strong>in</strong> Figure 5.11, <strong>the</strong> comb<strong>in</strong>ed seasonal<br />

distribution <strong>of</strong> wildebeest, hartebeest and eland requires a vast area to susta<strong>in</strong> <strong>the</strong>se<br />

populations over <strong>the</strong> long term. It is obvious that this movement can not be<br />

accomplished due to an <strong>in</strong>creas<strong>in</strong>g human population <strong>in</strong> Botswana (Crowe, 1995).<br />

Taolo (1997) notes that a comparison <strong>of</strong> <strong>the</strong> distribution <strong>of</strong> <strong>the</strong> biomass <strong>of</strong> wild<br />

species with that <strong>of</strong> domestic livestock suggests that <strong>the</strong> two seem to be mutually<br />

exclusive and thus wildlife numbers will only <strong>in</strong>crease <strong>in</strong> areas where <strong>the</strong> livestock<br />

biomass has decreased. It is likely that with cont<strong>in</strong>ued livestock expansion, wildlife<br />

will be displaced. This creates an <strong>in</strong>verse relationship between <strong>the</strong> wildlife and<br />

livestock populations, a relationship which is a reflection <strong>of</strong> human distribution and a<br />

result <strong>of</strong> <strong>the</strong> disturbance to <strong>the</strong> wildlife migration patterns to which this distribution<br />

has contributed.<br />

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