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A guide for planners and managers - IUCN

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128 MARINE AND COASTAL<br />

PROTECTED AREAS<br />

Box I-14. Problems with Conventional Funding Sources <strong>for</strong> Marine Protected Areas<br />

It is becoming more <strong>and</strong> more difficult to raise the cash necessary to maintain<br />

protected areas from conventional funding sources. Both government <strong>and</strong> donor budgets<br />

are falling in most countries, tourism is often highly variable, <strong>and</strong> there is stiff competition<br />

<strong>for</strong> private investment funds from other sectors of the economy which are seen to<br />

generate higher, <strong>and</strong> more immediate, returns than marine conservation.<br />

The case of Kisite-Mpunguti Marine National Park epitomises many of these<br />

funding constraints. Throughout the decade, as public sector budgets in Kenya have fallen<br />

<strong>and</strong> expenditure has been rationalised <strong>and</strong> focused on priority areas <strong>for</strong> social development<br />

such as health <strong>and</strong> education, central government subventions to environmental<br />

conservation activities have been falling. The amount of programme <strong>and</strong> project aid being<br />

granted to Kenya from external donors has also decreased substantially. Since 1990 all<br />

national parks in Kenya have been under the management of the parastatal Kenya<br />

Wildlife Service, meaning that as well as being accorded a much greater degree of<br />

autonomy, parks have been expected to become increasingly financially self-supporting.<br />

However, relying almost entirely on tourist revenues <strong>for</strong> income, the Kenya<br />

Wildlife Service has been hit hard by the drastic downturn in tourism to Kenya over the<br />

last 5 years which has resulted from political unrest <strong>and</strong> civil insecurity in key tourist<br />

areas of the country, including the coastal strip. As a whole the Kenya Wildlife Service’s<br />

revenue base has been undermined, <strong>and</strong> budget allocations to Kisite-Mpunguti have also<br />

fallen substantially (from an average of US$ 400,000 a year at today’s prices during the<br />

late 1970s to only US$ 20,000 in the last financial year (Emerton, 1999)). Conventional<br />

funding sources are proving inadequate <strong>for</strong> Kisite-Mpunguti, which is having difficulties<br />

financing even its most basic management operations.<br />

Over recent years a wide range of more innovative financing mechanisms have<br />

started to be used to raise funds <strong>for</strong> marine conservation (Box I-15). These are mainly<br />

based on capturing as real income some of the economic values associated with the<br />

consumption of marine goods <strong>and</strong> services. Although many groups <strong>and</strong> individuals<br />

benefit from marine goods <strong>and</strong> services, <strong>for</strong> which they would be both willing <strong>and</strong><br />

able to pay, mechanisms do not exist by which they can be charged <strong>for</strong> their<br />

consumption, or can invest in the provision of marine goods <strong>and</strong> services.

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