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THE UNIVERSITY OF LEIPZIG

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marine and fresh water resources and as well the ozone layer. 556 As earlier noted, the Act<br />

creates NEMA as the agency responsible for the implementation of specified clauses of this<br />

Act. In relating this act to institutional related aspects, Section 43 of the Act points out that the<br />

interests of local communities customarily resident within and around lakeshores, wetland,<br />

coastal zones, riverbanks or forest can be declared to be of protected interests. 557<br />

The Act however, does not define what protected interests are and for whom. This<br />

shortcoming as earlier pointed out, is consistent in most of the legal regimes. Since protected<br />

interests are not well defined, utilisation and conservation becomes suspect. This same fact is<br />

illustrated by Section 54(2) which states that a Minister in consultation with the lead agency<br />

can declare an area of land, sea, or river to be a protected natural environment for the purpose<br />

of promoting and preserving specific ecological processes, natural environmental systems,<br />

natural beauty or species of indigenous wildlife or the preservation of biological diversity in<br />

general. More still, using Section 54(2), the National Environment Management Authority<br />

(NEMA) may issue guidelines and prescribe measures for the management and protection of<br />

any area considered to be of environmental significance under the section. 558<br />

An informed analysis of the above sections and several others portrays a picture of a legal<br />

framework aimed at extreme formalisation of environment and biodiversity management in<br />

particular. Though this is aimed at preventing further destruction of the environment and<br />

biodiversity including that found in private and commonly owned resources, it may face a<br />

dilemma of misperception. The Act is also at variance with informal institutions such as<br />

customary law in the management of environment or biodiversity. More so, the Act curtails<br />

customary rights of access to environmental resources and proposes no steps for<br />

compensation to affected communities or individuals. 559<br />

Therefore given such an evaluation, structuring and mediation of formal and informal<br />

institutions co-existence in regard to biodiversity is of paramount importance. We ought to<br />

appreciate March and Olson who put it that mediation between formal and informal<br />

institutions is imperative because it constrains individual behaviour. 560 It also goes without<br />

saying that institutions constrain the actions of individuals hence individual behaviours are<br />

bounded to some degree. This similar situation can be likened to what Khadaha and Gurung<br />

described as a catch–all strategy in relation to the Forest Nationalisation and Management Act<br />

in Nepal. The duo mentions that when the Nepalese Government nationalised the country’s<br />

Forests, it took away collective and individual control of local forest resources. Thus<br />

communal responsibility for forestry management rapidly disappeared in the country. Forests<br />

were converted into open access areas as a common property resource, with communities<br />

having no stake in forest preservation. Yet at the time of nationalisation, the state was unable<br />

556<br />

The Kenya Environment Management and Co-ordination Act, Article 9(2)o.<br />

557<br />

The Kenya Environment Management and Co-ordination Act, Section 7.<br />

558<br />

The Kenya Environment Management and Co-ordination Act, Section 54(2).<br />

559<br />

The Kenya Environment Management and Coordination Act, Section 54(1).<br />

560<br />

March.E and J.P Olson .1984. New Institutionalism: Organisational Factors in Political life. American<br />

Political Science Review 78: 9734-749.<br />

115

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