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Agroecology and the Struggle for Food Sovereignty ... - Yale University

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zimmerer<br />

31<br />

An Exp<strong>and</strong>ing Interface with Agriculture<br />

Will Change Global Conservation<br />

Karl S. Zimmerer<br />

The growth <strong>and</strong> evolution of conservation is resulting in a much-exp<strong>and</strong>ed interface<br />

with agriculture <strong>and</strong> o<strong>the</strong>r <strong>for</strong>ms of resource use (livestock-raising, <strong>for</strong>est extraction,<br />

fishing, hunting). The widespread commitment to protected-area conservation is<br />

argued to offer a number of similarities <strong>and</strong> some key differences with respect to<br />

o<strong>the</strong>r main dimensions of environmental globalization (see Mol 2001; Speth 2001).<br />

Rapid growth of <strong>the</strong> interface 1 of conservation with agriculture <strong>and</strong> resource use is<br />

driven by both <strong>the</strong> profusion of designated protected areas <strong>and</strong> <strong>the</strong> management<br />

characteristics of enlarged conservation ef<strong>for</strong>ts. The worldwide coverage of<br />

designated protected areas has exp<strong>and</strong>ed more than ten times in area during <strong>the</strong> past<br />

few decades (Zimmerer et al. 2004). Measuring less than 1 million km 2 in 1970, <strong>and</strong><br />

estimated at 5.2 million km 2 in 1985, <strong>the</strong> area of publicly designated protected areas<br />

grew to more than 12.2 million km 2 in 1997 <strong>and</strong> has been estimated to cover 14.2<br />

million km 2 by 2003.<br />

Incorporation of agriculture <strong>and</strong> resource use into conservation programs is an<br />

important characteristic of <strong>the</strong> expansion of global conservation <strong>and</strong> protected areas<br />

(Zimmerer 2005). By 1997, nearly 60 percent of protected areas were classified as<br />

zones of agricultural or resource use (Zimmerer et al. 2004). Equally or more<br />

persuasive than this quantitative measure, since it sums up <strong>the</strong> often inaccurate<br />

estimates of <strong>the</strong> global conservation databases, is <strong>the</strong> rhetorical purpose that is served<br />

by presenting <strong>and</strong> publicizing <strong>the</strong>se numbers. Certain influential segments of <strong>the</strong><br />

global conservation movement badly want to incorporate resource <strong>and</strong> l<strong>and</strong> uses,<br />

such as agriculture, into <strong>the</strong> main agenda (McNeely <strong>and</strong> Scherr 2003).<br />

The increased interface of conservation areas with agriculture <strong>and</strong> resource use is<br />

an integral part of a sustainability emphasis in conservation that gained prominence<br />

in <strong>the</strong> late 1980s <strong>and</strong> early 1990s. The term “sustainability,” which refers to <strong>the</strong><br />

exp<strong>and</strong>ed attention to l<strong>and</strong> use that is environmentally sound <strong>and</strong> adequately<br />

remunerative from an economic viewpoint, has become one of <strong>the</strong> defining goals of<br />

much conservation worldwide. The goal of sustainability has been granted a level of<br />

priority similar to strict preservation in certain conservation circles.<br />

1 The term “interface” highlights<br />

<strong>the</strong> fact that <strong>the</strong> interaction<br />

of <strong>the</strong> large expansion<br />

of designated conservation<br />

areas may present any one of<br />

several relations to agriculture<br />

that range from conflict to<br />

incorporation.<br />

yale school of <strong>for</strong>estry & environmental studies

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