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

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

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• • • • • • • • Death of wildlife and domestic stock, including animals burnt to death along veterinary fences while trying to escape (several thousand animals are burnt to death along fences throughout Botswana each winter or dry season); Disruption of natural migration patterns; Habitat loss - Animals flee burnt areas and overcrowd unburned areas, resulting in unhealthy competition, reduced breeding rates, overgrazing, etc.; Exposure of floodplains and subsequent increase in evapo-transpiration rates; Soil composition change; Sheet erosion; 7.2.1.2 Fences Ash poisoning leading to 'dead-water' and possibly fish die-off; and Loss of human life and property (OPWT, 1998). Ill-placed veterinary fences, constructed without environmental or social impact assessments continue to trap and kill significant numbers of wildlife. Fragmentation, obstruction of vital territorial and migratory movements, loss of access to critical resources, among other impacts, causes severe stress, increasing death rates and decreasing birth rates. Irreversible population declines have occurred and appear to be ongoing (OPWT, 1998). Severe declines in the number of roan antelope, eland, wildebeest and giraffe have been observed recently along newly constructed fences in the Ngamiland District. Continued impacts threaten the demise of the remaining wildlife populations to the west and north of the Okavango Delta (OPWT, 1998). 7.2.1.3 Cattle Ranching Plans to develop private, commercial cattle ranches to the west and north of the Delta are a threat to wildlife populations. Such developments will further fragment habitats, block migration routes, displace local communities and generally lead to 284

environmental degradation. If the Okavango Delta and its wildlife is to remain a healthy, functioning and protected ecosystem, the areas surrounding the Delta must also be conserved. The Okavango Delta is too complex an ecosystem to survive as a 'protected island' surrounded by commercial development (OPWT, 1998). 7.2.1.4 Hunting The Department of Wildlife and National Parks (DWNP), faced with the task of monitoring wildlife management in Ngamiland, is severely constrained in terms of manpower and resources, and hence cannot monitor the hunting industry in the Okavango Delta effectively. Consequently, uncontrolled hunting, based on unscientific methods and quotas are having a negative impact on biomass and diversity. Specific impacts include: • Over-hunting; • Selective species hunting, causing imbalances; • Hunting during the mating season. Removal of territorial breeding animals and harassment, affecting reproduction patterns and rates; and • Hunting of prime and immature male animals, thereby affecting the gene pool (OPWT, 1998). Elephant range increased as a result of the ban imposed on elephant hunting in 1983, after which elephants gradually moved out of the Moremi Game Reserve and Chobe National park into the then again safe areas throughout the whole of northern Botswana. However, since elephant hunting was reintroduced in 1996 this process is already beginning to reverse. Elephant are once again starting to concentrate only in non-hunting areas, such as the Moremi Game Reserve, Chobe National Park and the photographic concession areas in the Okavango Delta. This is leading to habitat degradation through the over-population of elephant in these areas. The congestion of elephant in the Moremi Game Reserve during the years prior to 1983, caused the destruction of the Acacia eri%ba, Acacia tortilis, Acacia nigrescens and Hyphaene ventricosa (real fan palm - used heavily in basket making) populations of the reserve (OPWT, 1998). 285

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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