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THE UNIVERSITY OF LEIPZIG

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ights relating to biodiversity, a situation which usually degenerates into forced access to most<br />

of the conserved resource regimes. 533 Given the existing institutional inadequacies and<br />

inconsistencies, enforcement has largely become hard even in the post independence era. This<br />

results from the varied users and uses of biodiversity, ranging from the provision of food,<br />

direct economic benefits, to promotion of culture. 534<br />

In light of the above, the different post independence legal regimes relating to biodiversity<br />

management ought to have taken into consideration the aspirations of these different users. 535<br />

Although the Kenyan Wildlife Services seems to portray this in its public memorandum, the<br />

fact remains that biological diversity is strictly and closely controlled by government. Both,<br />

the pre and the post-independence legal regime relating to biodiversity undermined and<br />

consequently weakened the traditional institutions of natural resource management in<br />

Kenya. 536 The new institutions of resource management alienated the local people hence<br />

taking away conservation roles from the natives. 537 This is illuminated by the laws that were<br />

finally enacted.<br />

The existing legislations make mutual existence almost impossible and this in part explains<br />

why cases of encroachment on biodiversity remain high. Thus, because of this state of affair,<br />

the governmental biodiversity governance regimes have largely remained unmitigated and<br />

subsequently less effective. Nagendra, like many scholars in the realm of biological resource<br />

usage has pointed out that in governing common pool resources such as forests, there may be<br />

conditions that tempt individuals to cheat and gain substantially higher benefits. This happens<br />

especially when rule mitigation and compliance is weak. 538 In light of such a scenario,<br />

resource commons in this regard are bound to be vulnerable to externalities. This significantly<br />

obtains in the Kenyan resource regime structure.<br />

5.5 Current legal and policy regimes in conservation of biodiversity<br />

In the opening section of this chapter, we did mention that although biodiversity is an<br />

important national resource, it does not appear in the provisions of the supreme law in Kenya.<br />

Further still, there are no clear cut policies that are spelt out for conservation of biodiversity as<br />

a resource. Furthermore, there are no provisions for local biodiversity notions. However,<br />

issues relating to biodiversity conservation are entailed in scattered, divergent legal and policy<br />

frameworks. This means that, in order to analyse the institutional approaches in biodiversity<br />

management entails an evaluation of related acts and policies. The study will detail itself on<br />

the following acts: The Forests Act, the Wildlife Conservation Act, the Agricultural Act and<br />

the Environmental Management and Coordination Act.<br />

533<br />

Fischer.E Opcit.<br />

534<br />

Conservation awareness, The Daily Nation April 17 1997.<br />

535<br />

Kenya will not allow the hunting of Wildlife. The Daily Nation September 1997.<br />

536<br />

Ibid<br />

537<br />

The Kenya Wildlife Act Cap376 Section 34(c), of the laws of Kenya.<br />

538<br />

Nagendra, H. 2002. Tenure and forest conditions: Community forestry in Nepal.Terai. Environmental<br />

Conservation 29:530–539.<br />

110

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