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 ...
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
- Page 273 and 274: companies, 6 (40 percent) to jointl
- Page 275 and 276: Lastly, wildlife tends to congregat
- Page 277 and 278: Table 6.17: Major Safari Companies/
- Page 279 and 280: indicates that Botswana has more ar
- Page 281 and 282: 6.4 The Economic Impact of Tourism
- Page 283 and 284: weakest with agriculture, construct
- Page 285 and 286: As noted earlier, the greater major
- Page 287 and 288: Table 6.25: Estimated Tourism-Relat
- Page 289 and 290: evenue collection from the various
- Page 291 and 292: Despite these conflicting employmen
- Page 294 and 295: According to the study carried out
- Page 296 and 297: management positions in the tourism
- Page 298 and 299: Seventy four percent of the 50 loca
- Page 300 and 301: Table 6.33: List of Private Air Cha
- Page 302 and 303: CHAPTER SEVEN Natural Resource Util
- Page 304 and 305: natural resources of water and pris
- Page 306 and 307: According to personal interviews co
- Page 308 and 309: • • • • • • • • Dea
- Page 310 and 311: Experience shows that some animals,
- Page 312 and 313: inhabitants of the Okavango Delta r
- Page 314 and 315: control is vested with central gove
- Page 316 and 317: conservation area. This led to conf
- Page 318 and 319: Table 7.4: Main Stakeholders, Land
- Page 320 and 321: 7.2.3.1 Arable Farming and Wildlife
- Page 322 and 323: Table 7.6: Livestock Ownership in K
- Page 326 and 327: Botswana because populations of bot
- Page 328 and 329: Delta, while previously inhabitants
- Page 330 and 331: facilities that do not have boats,
- Page 332 and 333: • • • • • 7.2.6 Since the
- Page 334: different products, wood is perhaps
- Page 337 and 338: Today, Hyphaene petersiana palms as
- Page 339 and 340: populations in the rivers have drop
- Page 341 and 342: The importance of people remaining
- Page 343 and 344: CBNRM aims at alleviating poverty a
- Page 345 and 346: the wildlife populations and their
- Page 347 and 348: no longer an important livelihood s
- Page 349 and 350: • • • • • • 7.3.4 Clari
- Page 351 and 352: Leases are given for 15 year period
- Page 353 and 354: Table 7.10: Community-Based Organis
- Page 355 and 356: 7.3.6.3 The Okavango Paler's Trust
- Page 357 and 358: at the same time allowing them to d
- Page 359 and 360: eports on financial management and
- Page 361 and 362: Table 7.11: Brief Review on Progres
- Page 363 and 364: their land, etc., such as cash, mea
- Page 365 and 366: 7.4 Summary and Conclusion While th
- Page 367 and 368: 8.2 Impacts of Tourism on Local Cul
- Page 369 and 370: tourists in an area provide a sourc
- Page 371 and 372: are left to perform all the traditi
- Page 373 and 374: 8.3.1 Positive Environmental Impact
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