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 ...

pfeiffer.nele60
from pfeiffer.nele60 More from this publisher
16.08.2013 Views

Furthermore, the NCS has failed to develop a legal framework by which it can coordinate the five environmental challenges it was established to address. Natural resource management is, therefore, the responsibility of the various government departments and ministries. This sectorial nature of land use policies causes conflict in the Okavango Delta, which threaten the sustainable management of wildlife in the area. For example, the Tawana Land Board is responsible for the allocation of agricultural land in the Okavango Delta, while the Ministry of Agriculture provides seeds and agricultural demonstrations to farmers, free livestock to Basarwa (San) farmers, and free veterinary assistance and vaccination of animals. There is very little or no co-ordination between these two government departments, even though they are both responsible for shaping agricultural production in the Okavango Delta. All these agricultural measures are implemented without consideration for wildlife conservation, due to the lack of co-ordination between agriculture and wildlife in Botswana (Mbaiwa, 1999). Despite the importance of the role of Environmental Impact Assessments (EIAs) in sustainable development, the NCS in all its 15 years of existence, has just recently finished formulating draft EIA legislation, which has not yet been passed in parliament. While EIAs have been carried out voluntarily in Botswana, there is no legal policy or act which makes it mandatory for EIAs to be carried out prior to any development initiatives. This has resulted in the possibility of seriously destructive projects, such as the erection of veterinary fences throughout the Ngamiland District, being carried out, as there is very little accountability for environmental degradation in Botswana. The erection of the veterinary fences in Botswana, at the expense of the country's wildlife, is a further example of the lack of integration between livestock production and wildlife management (Mbaiwa, 1999). The Department of Wildlife and National Park's wildlife utilization and management policies also lack provisions for the integration of wildlife management with other sectors and government departments. Although the Wildlife Conservation and National Parks Act of 1992 has consolidated the laws relating to wildlife conservation and management in Botswana, it has not addressed the question of how wildlife utilisation and management must relate to other sectors of the economy. The Act does not require EIAs to be conducted prior to the implementation of economic activities in National Parks, Game Reserves, Wildlife Management Areas and 300

Controlled Hunting Areas. The Act also makes it difficult to integrate wildlife utilization with other socio-economic activities. For example, the management of Moremi Game Reserve is not co-ordinated with the management of the surrounding community lands and areas. This results in these protected areas forming 'conservation islands' instead of larger, sustainable and continuous ecosystem areas that include the local communities living in the vicinity. Another example is that the wildlife tourism industry in the Okavango Delta ignores community development. Instead, local communities, such as those of Khwai village, are regarded by the tourism industry as a wildlife management problem. This is another aspect that encourages land use conflicts in the area because the various land use activities are not prioritized or co-ordinated. Wildlife management is therefore not conducted within the cultural and economic context of the people of the Okavango Delta who continue to view game parks and reserves as the property of the government, where local people are denied access to their former hunting and gathering lands (Mbaiwa, 1999). Although aimed at promoting wildlife conservation, the Botswana Government's efforts of zoning the Ngamiland District into WMAs and CHAs, has created problems for wildlife management. This is because the zoning did not take into consideration the other socio-economic activities in the area, nor was any Environmental Impact Assessment (EIA) or Social Impact Assessment (SIA) conducted. As a result, this has led to land use conflicts, especially between wildlife management and traditional hunting and gathering activities in the Okavango Delta area (Mbaiwa, 1999). Key informants in the wildlife industry in Ngamiland District appear to agree on the possibility of integrated wildlife management in the area, if it is associated with proper land use planning in the District. For example, members of the Okavango People's Wildlife Trust (OPWT) argued that integrated wildlife management in the area is possible if there is a return to the more traditional management methods and land use values. An example given is that of traditional pastoralism, which is more compatible with free-ranging wildlife populations as opposed to fenced commercial ranches (Mbaiwa, 1999). The DWNP holds the more realistic view that the traditional approach of integrating wildlife management with agricultural production was possible in pre-colonial 301

Controlled Hunt<strong>in</strong>g Areas. The Act also makes it difficult to <strong>in</strong>tegrate wildlife<br />

utilization with o<strong>the</strong>r socio-economic activities. For example, <strong>the</strong> <strong>management</strong> <strong>of</strong><br />

Moremi Game Reserve is not co-ord<strong>in</strong>ated with <strong>the</strong> <strong>management</strong> <strong>of</strong> <strong>the</strong> surround<strong>in</strong>g<br />

community lands and areas. This results <strong>in</strong> <strong>the</strong>se protected areas form<strong>in</strong>g<br />

'conservation islands' <strong>in</strong>stead <strong>of</strong> larger, susta<strong>in</strong>able and cont<strong>in</strong>uous ecosystem areas<br />

that <strong>in</strong>clude <strong>the</strong> local communities liv<strong>in</strong>g <strong>in</strong> <strong>the</strong> vic<strong>in</strong>ity. Ano<strong>the</strong>r example is that <strong>the</strong><br />

wildlife <strong>tourism</strong> <strong>in</strong>dustry <strong>in</strong> <strong>the</strong> Okavango Delta ignores community development.<br />

Instead, local communities, such as those <strong>of</strong> Khwai village, are regarded by <strong>the</strong><br />

<strong>tourism</strong> <strong>in</strong>dustry as a wildlife <strong>management</strong> problem. This is ano<strong>the</strong>r aspect that<br />

encourages land use conflicts <strong>in</strong> <strong>the</strong> area because <strong>the</strong> various land use activities are<br />

not prioritized or co-ord<strong>in</strong>ated. Wildlife <strong>management</strong> is <strong>the</strong>refore not conducted<br />

with<strong>in</strong> <strong>the</strong> cultural and economic context <strong>of</strong> <strong>the</strong> people <strong>of</strong> <strong>the</strong> Okavango Delta who<br />

cont<strong>in</strong>ue to view game parks and reserves as <strong>the</strong> property <strong>of</strong> <strong>the</strong> government, where<br />

local people are denied access to <strong>the</strong>ir former hunt<strong>in</strong>g and ga<strong>the</strong>r<strong>in</strong>g lands (Mbaiwa,<br />

1999).<br />

Although aimed at promot<strong>in</strong>g wildlife conservation, <strong>the</strong> Botswana Government's<br />

efforts <strong>of</strong> zon<strong>in</strong>g <strong>the</strong> Ngamiland District <strong>in</strong>to WMAs and CHAs, has created problems<br />

for wildlife <strong>management</strong>. This is because <strong>the</strong> zon<strong>in</strong>g did not take <strong>in</strong>to consideration<br />

<strong>the</strong> o<strong>the</strong>r socio-economic activities <strong>in</strong> <strong>the</strong> area, nor was any Environmental Impact<br />

Assessment (EIA) or Social Impact Assessment (SIA) conducted. As a result, this<br />

has led to land use conflicts, especially between wildlife <strong>management</strong> and traditional<br />

hunt<strong>in</strong>g and ga<strong>the</strong>r<strong>in</strong>g activities <strong>in</strong> <strong>the</strong> Okavango Delta area (Mbaiwa, 1999).<br />

Key <strong>in</strong>formants <strong>in</strong> <strong>the</strong> wildlife <strong>in</strong>dustry <strong>in</strong> Ngamiland District appear to agree on <strong>the</strong><br />

possibility <strong>of</strong> <strong>in</strong>tegrated wildlife <strong>management</strong> <strong>in</strong> <strong>the</strong> area, if it is associated with<br />

proper land use plann<strong>in</strong>g <strong>in</strong> <strong>the</strong> District. For example, members <strong>of</strong> <strong>the</strong> Okavango<br />

People's Wildlife Trust (OPWT) argued that <strong>in</strong>tegrated wildlife <strong>management</strong> <strong>in</strong> <strong>the</strong><br />

area is possible if <strong>the</strong>re is a return to <strong>the</strong> more traditional <strong>management</strong> methods and<br />

land use values. An example given is that <strong>of</strong> traditional pastoralism, which is more<br />

compatible with free-rang<strong>in</strong>g wildlife populations as opposed to fenced commercial<br />

ranches (Mbaiwa, 1999).<br />

The DWNP holds <strong>the</strong> more realistic view that <strong>the</strong> traditional approach <strong>of</strong> <strong>in</strong>tegrat<strong>in</strong>g<br />

wildlife <strong>management</strong> with agricultural production was possible <strong>in</strong> pre-colonial<br />

301

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!