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THE UNIVERSITY OF LEIPZIG

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ights and rules defining the range of impacts and opportunities available to actors. It also<br />

looks at the procedures for settling disputes and adjusting the system of rights and rules for<br />

compliance. Regimes may arise spontaneously as a product of uncoordinated efforts of many<br />

individuals. 62 Regimes may also be negotiated by some general principles or by some general<br />

purpose authority. Hence a resource regime refers to the management and administration<br />

structures in place to regulate resources usage for instance a water authority, an environmental<br />

management authority or a forestry authority. 63<br />

1.7 Biodiversity: An insight into the contemporary debates and notions<br />

In the following sub-section, we discuss the contending debates and notions relating to<br />

biodiversity management and governance. These shall be discussed in light of the current<br />

policies and procedures that obtain in Kenya’s biodiversity resource regimes. The following<br />

notions will also be articulated alongside the views and opinions collected from national level<br />

respondents through a national level institutional mapping exercise.<br />

The Globalcentric notion<br />

This is the most dominant view arising from the international level perspectives on<br />

biodiversity. It emphasizes resources management and is a brainchild of dominant<br />

international institutions particularly the World Bank and the major Northern Environmental<br />

Conservation Organizations such as the World Conservation Union (ICUN) and the World<br />

Wildlife Fund (WWF). These are backed by the weight of the Group of Eight rich nations<br />

(G8). The globalcentric notion is based on the particular representation of the threats to<br />

biodiversity that emphasize loss of habitats, species reduction and fragmentation due to<br />

habitat reduction rather than underlying causes. 64 This notion offers a set of prescriptions for<br />

the conservation and sustainable use of resources at the international, national and the local<br />

levels. As a result, it suggests appropriate mechanisms for biodiversity management,<br />

including the in-situ and ex-situ conservation in the national biodiversity planning processes.<br />

It calls for the establishment of appropriate mechanisms for compensation and economic use<br />

of biodiversity, chiefly through intellectual property rights. However, the dilemmas that<br />

surround the entire scheme of property rights and bio-prospecting need no recapitulation.<br />

Dedeurwaerder notes with pain that this process has been a reap-off on the side of the local<br />

communities. 65 He notes that many of the access and benefit sharing agreements have been<br />

signed but are largely bilateral contractual arrangements between the rich countries and poor<br />

countries and are not based on the principle of informed consent. It is further agonizing to<br />

Science 277:494-499.<br />

62<br />

Berkes, F. 2002. Cross-scale institutional linkages: perspectives from the bottom up. In The drama of the<br />

Commons edited by E. Ostrom et al.,293-321. Washington: National Academy Press.<br />

63<br />

Friedheim, R. L. 2001. Toward a sustainable whaling regime. Washington: University of Washington Press.<br />

64<br />

Brush, S. 1998. Prospecting for the Public Domain. Center for Latin America Studies, University of Chicago.<br />

65<br />

Morris, M.L et al. 1999. Genetic Change in Farmer Recycled Maize Seed : A review of Evidence. CMMYT.<br />

Economics working Paper No- 99.<br />

16

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