Wildlife as exclusive land use - Rationale

 

Figure 19: Land capability and economic returns from land use in Namibia

In the development of the wildlife sector, non-consumptive tourism on high quality wildlife land will give by far the greatest economic returns (Barnes 2001, Martin 1993).

Brown (2004) and Martin (2004b) have pointed out that, given land capability in the arid situation of Namibia, the highest valued land uses over most of the country are those based on management of natural resources (Figure 19). National and international policy constraints, however, place wildlife at a competitive disadvantage with land use based on exotic species. As a consequence, the full potential of wildlife as landuse is not being realised at present.

Barnes (et al 2001) state that in the medium to long term the comparative advantages of land use based on domestic livestock can be expected to decline as international subsidies are phased out. They also point out that the comparative advantages of wildlife land uses can be expected to increase over time, due to continuing rapid expansion in international tourist markets, increasing scarcity of wildlife elsewhere, and the development of markets to capture international wildlife non-use values as income. Their results show that commercial livestock ranching has limited potential to compete economically with wildlife use because it is capital intensive and requires access to external markets.

The results of Barnes and de Jager (1995) suggest that, under present circumstances, there is little financial incentive for individual farmers practising livestock and game production systems to convert to pure game production either for consumptive or non-consumptive use. Their results clearly show that production at a larger scale within conservancies is likely to be more efficient both financially and economically than production at a ranch scale. Safari hunting on private land appears to have been profitable but only as a supplementary enterprise alongside livestock or other wildlife land uses. Its profitability appears, on livestock farms, to have provided the financial incentive for much investment in wildlife and this, in turn, has led to conditions where pure wildlife ranching is possible.

Requirements

The technical arguments for greater areas of Namibia to be put over to natural resource management will not, on their own, bring about the needed changes. It will require a high level political commitment and the correct suite of incentives to induce landholders (both communal and private) to convert to a land use based primarily on wildlife. The high level political commitment is already in place. In a speech delivered on 3rd February 2004, the former President, Dr Sam Nujoma, made the visionary statement that wildlife would be restored throughout the north of Namibia, that ownership of wildlife would be conferred on local peoples and that the economy would be transformed by diversification based on wildlife uses . . .

. . a dream where the animals returned, the forests were restored and the people were no longer poor and hungry. The return of animals to the land could benefit the people if the animals once again belonged to them . . .

Already the trends amongst commercial farmers and conservancies are extremely positive and Namibia's record of an expanding wildlife industry over the past 10-20 years is impressive. In 2004, there were more than 40 registered and emerging conservancies with 150,000 members managing wildlife over an area of 100,000 square kilometres in the areas where elephant populations are expanding. To maintain the momentum requires a greater devolution of authority for wildlife management, the development of co-management institutions and, in the specific case of elephant, an ability to realise far greater returns from the species. Perhaps the greatest danger that the vision will not be fulfilled lies in a possible perversion of the intent of policy during the course of putting it into practice (Corbett and Jones 2000).