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 ...
has become a matter of great contention in some areas in recent years. The beaches of some resort developments along the Mediterranean coasts of Greece and Turkey, for example, are used by rare turtle populations as breeding grounds, whereby clutches of eggs are laid in chambers dug out of the sand. In certain resorts, conservationists have taken to distributing multi-lingual leaflets warning tourists not to lay towels on the sand (which can reduce the temperature of the eggs incubating beneath), not to use beach umbrellas (which can spike whole clutches) and not to light bonfires at night (which can disorientate hatchlings trying to reach the sea) (Greth, 1989; Morrison and Selman, 1991; Pattullo, 1996). This example demonstrates both the strength of feeling that can be generated against tourism impacts, and the profound impacts of seemingly innocent and relatively passive tourist activities. Similar fears over tourist disruption to important breeding grounds have been expressed by, for example, Erize (1987) with reference to cruises to the Antarctic, and Walker (1991) when considering the management of Heron Island in the Great Barrier Reef of Australia, for sea-bird and sea-turtle breeding areas. Even in the non-breeding period, animals will still experience stress from the presence of tourists. Many of the animals (including birds) in mountain forests, for example, are severely disturbed by the activities of skiers and walkers. In trying to escape the tourists, the rapid use of their energy resources can result in starvation if the disturbance is frequent, especially during harsh winter months (Pattullo, 1996). The disturbance caused by tourists, amongst others, is thought to be responsible for an 80% decline in the giant petrel population of Ardly Island in the South Shetland Islands of Antarctica (Tribe et aI, 2000). The insensitivity of tourists towards nesting penguins is also noted in the study, where these animals were deliberately disturbed for wildlife photography. The almost daily disturbance by tourists of cheetah populations in the Serengeti National Park, Tanzania, has seriously affected these animals (McLaren, 1998). In certain areas, the sheer rarity of the plant and animal communities results in their destruction even before tourists arrive. Such is the case for the island of Saint Martin in the West Indies, where plans to construct a land/sea link to facilitate tourism development destroyed many of the unique plant communities of the island through colonisation by incoming alien species (Monnier, 1987). Similarly, the unique flora of the Tiede National Park in Tenerife, Canary Islands, is at risk from exotic seeds 50
carried unintentionally on the shoes and bodies of park visitors (Romeril, 1989; Hunter and Green, 1995). On a more positive note, there are numerous studies in the literature which emphasise the actual or potential benefits of tourism to the fauna and flora of an area. Tourism may result in the establishment, or continued existence, of a wildlife park or reserve, for example. Similarly, habitat restoration appears to be increasingly associated with tourism projects. Luxmoore (1989) concludes that wildlife tourism and controlled hunting are amongst the less intensive forms of wildlife exploitation, and tends to be of greater benefit to wildlife conservation than the more intensive forms of wildlife exploitation and production. McLaren (1998) states that many national parks and wildlife reserves in Kenya have benefited greatly from tourist expenditure and associated publicity, while others owe their continued existence to the tourism industry. In discussing the network of protected natural areas in the Sahel, spanning several African countries, Hunter and Green (1995) argue that tourism provides the national governments of the Sahel states with an economic incentive for the continued protection of the natural areas. Alternatively, O'Donnell (1991) stresses the positive role of rural or agri-tourism in preserving the rural environment and culture of Ireland. Briereton (1991) recognises the development and upgrading of national parks and natural attractions in parts of the Caribbean resulting from tourism. Finally, Martinez-Taberner et al (1990) in describing the major criteria required for the restoration of a coastal marsh ecosystem in Majorca, Spain, conclude that such projects are essential to maintaining the appeal of an area for tourists. 2.11.1.2 Pollution Pollution entails the anthropogenic introduction of substances or energy into the environment. Pollution may affect human health, cause harm to living resources and ecological systems, damage to structures or amenity, and interfere with the legitimate use of the environment. Since tourism (as a legitimate use of the environment) relies, in part, on amenity value, one might reasonably assume that the tourism industry has a history of concern over the potential threat posed by pollution to the success of destination areas. This is, however, generally not the case. Additionally, the tourism industry itself has been, and still is, a major contributor to 51
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has become a matter <strong>of</strong> great contention <strong>in</strong> some areas <strong>in</strong> recent years. The<br />
beaches <strong>of</strong> some resort developments along <strong>the</strong> Mediterranean coasts <strong>of</strong> Greece<br />
and Turkey, for example, are used by rare turtle populations as breed<strong>in</strong>g grounds,<br />
whereby clutches <strong>of</strong> eggs are laid <strong>in</strong> chambers dug out <strong>of</strong> <strong>the</strong> sand. In certa<strong>in</strong><br />
resorts, conservationists have taken to distribut<strong>in</strong>g multi-l<strong>in</strong>gual leaflets warn<strong>in</strong>g<br />
tourists not to lay towels on <strong>the</strong> sand (which can reduce <strong>the</strong> temperature <strong>of</strong> <strong>the</strong> eggs<br />
<strong>in</strong>cubat<strong>in</strong>g beneath), not to use beach umbrellas (which can spike whole clutches)<br />
and not to light bonfires at night (which can disorientate hatchl<strong>in</strong>gs try<strong>in</strong>g to reach<br />
<strong>the</strong> sea) (Greth, 1989; Morrison and Selman, 1991; Pattullo, 1996). This example<br />
demonstrates both <strong>the</strong> strength <strong>of</strong> feel<strong>in</strong>g that can be generated aga<strong>in</strong>st <strong>tourism</strong><br />
impacts, and <strong>the</strong> pr<strong>of</strong>ound impacts <strong>of</strong> seem<strong>in</strong>gly <strong>in</strong>nocent and relatively passive<br />
tourist activities. Similar fears over tourist disruption to important breed<strong>in</strong>g grounds<br />
have been expressed by, for example, Erize (1987) with reference to cruises to <strong>the</strong><br />
Antarctic, and Walker (1991) when consider<strong>in</strong>g <strong>the</strong> <strong>management</strong> <strong>of</strong> Heron Island <strong>in</strong><br />
<strong>the</strong> Great Barrier Reef <strong>of</strong> Australia, for sea-bird and sea-turtle breed<strong>in</strong>g areas.<br />
Even <strong>in</strong> <strong>the</strong> non-breed<strong>in</strong>g period, animals will still experience stress from <strong>the</strong><br />
presence <strong>of</strong> tourists. Many <strong>of</strong> <strong>the</strong> animals (<strong>in</strong>clud<strong>in</strong>g birds) <strong>in</strong> mounta<strong>in</strong> forests, for<br />
example, are severely disturbed by <strong>the</strong> activities <strong>of</strong> skiers and walkers. In try<strong>in</strong>g to<br />
escape <strong>the</strong> tourists, <strong>the</strong> rapid use <strong>of</strong> <strong>the</strong>ir energy <strong>resource</strong>s can result <strong>in</strong> starvation if<br />
<strong>the</strong> disturbance is frequent, especially dur<strong>in</strong>g harsh w<strong>in</strong>ter months (Pattullo, 1996).<br />
The disturbance caused by tourists, amongst o<strong>the</strong>rs, is thought to be responsible for<br />
an 80% decl<strong>in</strong>e <strong>in</strong> <strong>the</strong> giant petrel population <strong>of</strong> Ardly Island <strong>in</strong> <strong>the</strong> South Shetland<br />
Islands <strong>of</strong> Antarctica (Tribe et aI, 2000). The <strong>in</strong>sensitivity <strong>of</strong> tourists towards nest<strong>in</strong>g<br />
pengu<strong>in</strong>s is also noted <strong>in</strong> <strong>the</strong> study, where <strong>the</strong>se animals were deliberately disturbed<br />
for wildlife photography. The almost daily disturbance by tourists <strong>of</strong> cheetah<br />
populations <strong>in</strong> <strong>the</strong> Serengeti National Park, Tanzania, has seriously affected <strong>the</strong>se<br />
animals (McLaren, 1998).<br />
In certa<strong>in</strong> areas, <strong>the</strong> sheer rarity <strong>of</strong> <strong>the</strong> plant and animal communities results <strong>in</strong> <strong>the</strong>ir<br />
destruction even before tourists arrive. Such is <strong>the</strong> case for <strong>the</strong> island <strong>of</strong> Sa<strong>in</strong>t Mart<strong>in</strong><br />
<strong>in</strong> <strong>the</strong> West Indies, where plans to construct a land/sea l<strong>in</strong>k to facilitate <strong>tourism</strong><br />
development destroyed many <strong>of</strong> <strong>the</strong> unique plant communities <strong>of</strong> <strong>the</strong> island through<br />
colonisation by <strong>in</strong>com<strong>in</strong>g alien species (Monnier, 1987). Similarly, <strong>the</strong> unique flora <strong>of</strong><br />
<strong>the</strong> Tiede National Park <strong>in</strong> Tenerife, Canary Islands, is at risk from exotic seeds<br />
50