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environmental degradation. If <strong>the</strong> Okavango Delta and its wildlife is to rema<strong>in</strong> a<br />

healthy, function<strong>in</strong>g and protected ecosystem, <strong>the</strong> areas surround<strong>in</strong>g <strong>the</strong> Delta must<br />

also be conserved. The Okavango Delta is too complex an ecosystem to survive as<br />

a 'protected island' surrounded by commercial development (OPWT, 1998).<br />

7.2.1.4 Hunt<strong>in</strong>g<br />

The Department <strong>of</strong> Wildlife and National Parks (DWNP), faced with <strong>the</strong> task <strong>of</strong><br />

monitor<strong>in</strong>g wildlife <strong>management</strong> <strong>in</strong> Ngamiland, is severely constra<strong>in</strong>ed <strong>in</strong> terms <strong>of</strong><br />

manpower and <strong>resource</strong>s, and hence cannot monitor <strong>the</strong> hunt<strong>in</strong>g <strong>in</strong>dustry <strong>in</strong> <strong>the</strong><br />

Okavango Delta effectively. Consequently, uncontrolled hunt<strong>in</strong>g, based on<br />

unscientific methods and quotas are hav<strong>in</strong>g a negative impact on biomass and<br />

diversity. Specific impacts <strong>in</strong>clude:<br />

• Over-hunt<strong>in</strong>g;<br />

• Selective species hunt<strong>in</strong>g, caus<strong>in</strong>g imbalances;<br />

• Hunt<strong>in</strong>g dur<strong>in</strong>g <strong>the</strong> mat<strong>in</strong>g season. Removal <strong>of</strong> territorial breed<strong>in</strong>g animals<br />

and harassment, affect<strong>in</strong>g reproduction patterns and rates; and<br />

• Hunt<strong>in</strong>g <strong>of</strong> prime and immature male animals, <strong>the</strong>reby affect<strong>in</strong>g <strong>the</strong> gene<br />

pool (OPWT, 1998).<br />

Elephant range <strong>in</strong>creased as a result <strong>of</strong> <strong>the</strong> ban imposed on elephant hunt<strong>in</strong>g <strong>in</strong><br />

1983, after which elephants gradually moved out <strong>of</strong> <strong>the</strong> Moremi Game Reserve and<br />

Chobe National park <strong>in</strong>to <strong>the</strong> <strong>the</strong>n aga<strong>in</strong> safe areas throughout <strong>the</strong> whole <strong>of</strong> nor<strong>the</strong>rn<br />

Botswana. However, s<strong>in</strong>ce elephant hunt<strong>in</strong>g was re<strong>in</strong>troduced <strong>in</strong> 1996 this process<br />

is already beg<strong>in</strong>n<strong>in</strong>g to reverse. Elephant are once aga<strong>in</strong> start<strong>in</strong>g to concentrate only<br />

<strong>in</strong> non-hunt<strong>in</strong>g areas, such as <strong>the</strong> Moremi Game Reserve, Chobe National Park and<br />

<strong>the</strong> photographic concession areas <strong>in</strong> <strong>the</strong> Okavango Delta. This is lead<strong>in</strong>g to habitat<br />

degradation through <strong>the</strong> over-population <strong>of</strong> elephant <strong>in</strong> <strong>the</strong>se areas. The congestion<br />

<strong>of</strong> elephant <strong>in</strong> <strong>the</strong> Moremi Game Reserve dur<strong>in</strong>g <strong>the</strong> years prior to 1983, caused <strong>the</strong><br />

destruction <strong>of</strong> <strong>the</strong> Acacia eri%ba, Acacia tortilis, Acacia nigrescens and Hyphaene<br />

ventricosa (real fan palm - used heavily <strong>in</strong> basket mak<strong>in</strong>g) populations <strong>of</strong> <strong>the</strong><br />

reserve (OPWT, 1998).<br />

285

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