Parks - IUCN
Parks - IUCN
Parks - IUCN
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
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