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Parks - IUCN

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KENTON R. MILLER AND LAWRENCE S. HAMILTON<br />

Second, re-scale protected area programmes<br />

Action is needed at local, regional, and global levels to conserve biodiversity and<br />

ecosystem services. Core areas (national parks and other <strong>IUCN</strong> Categories) are<br />

elements of greater, ecosystem-wide conservation areas. It is these ‘bioregions’ that<br />

now must become the ‘management unit’ – including core areas, their buffer zones,<br />

and the remaining surrounding lands and waters in farms, forests, wildlife and fishery<br />

production and infrastructure. Obviously, this requires a challenging level of<br />

cooperation with neighbours, other jurisdictions, and even adjacent countries where<br />

boundaries cut across common ecosystems.<br />

In some cases, parks and reserves themselves cannot be expanded to cover<br />

geographic spaces sufficiently large for maintaining biodiversity and generating the<br />

full array of ecosystem services. The bioregional approach raises the scale of planning<br />

to that of whole landscapes so that corridors, buffer zones, and cooperative<br />

programmes with neighbours can increase the effective biological size of the area.<br />

These mechanisms can also facilitate migration and dispersal in the face of climate<br />

change and sea-level rise, reduce land degradation, and increase the chances of<br />

meeting protected area goals. Globally, most countries have accepted the<br />

responsibilities of the 1992 Conventions on Biological Diversity, Climate Change, and<br />

Desertification. Goals and actions to save and wisely use diversity, develop response<br />

mechanisms for climate change, and halt land degradation call for international<br />

cooperation among national governments.<br />

Third, reform the institutions<br />

Finally, we need to establish mechanisms that permit and encourage protected area<br />

managers to work with neighbours and other institutions that can help design and<br />

implement management programmes. Such action can anticipate fragmentation and<br />

other forms of change and promote the full range of ecosystem services. This<br />

generally requires revision of policies, and occasionally of legislation. But, most<br />

important, it requires development of economic incentives and institutional agreements<br />

that encourage people to participate and cooperate. Furthermore, at scales greater<br />

than wild core areas, we will need to cooperate with those in charge of other<br />

jurisdictions, private and communal ownership, and ecosystems that range into other<br />

countries. This calls for new ways of negotiating and shaping agreements among<br />

those that benefit and are affected by these bioregional programmes. Transborder<br />

protected areas also can be effective in reducing international tensions (Westing<br />

1993) and even forming Peace <strong>Parks</strong>, as has been proposed for the Korean<br />

Demilitarized Zone by Westing (1999) and by the Peace <strong>Parks</strong> Foundation for<br />

Southern Africa (Hanks 1999). The benefits and drawbacks, and guidelines for<br />

effective transborder cooperation, have been discussed by Hamilton et al. (1996).<br />

Fourth, reconsider the role of protected area<br />

managers<br />

Managers will argue that they have enough problems addressing the issues they<br />

already face within their jurisdictional boundaries without adding further demands<br />

upon their limited time and resources. But, as our argument and the cases have<br />

shown, a new set of challenges is looming over the horizon that may simply<br />

overwhelm manager’s current agenda. The opportunity is for managers to adapt their<br />

policies and practices to meet these new challenges head-on while time permits.<br />

47

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