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The cultural context of biodiversity conservation - Oapen

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<strong>The</strong> <strong>cultural</strong> <strong>context</strong> <strong>of</strong> <strong>biodiversity</strong> <strong>conservation</strong><br />

well as from above« (1999: 131ff.). <strong>The</strong> importance <strong>of</strong> cross-<strong>cultural</strong> negotiations,<br />

which imply the acceptance <strong>of</strong> a plurality <strong>of</strong> interpretations, meanings and approaches,<br />

has been discussed by Clay et al., who write that the success <strong>of</strong> long-term sustainable<br />

use and <strong>conservation</strong> efforts will be enhanced only »if indigenous peoples feel that<br />

they have ownership <strong>of</strong> a project« (2000: 14). However, a basic necessity, as suggested<br />

by the authors, is that communication takes place and that this endeavour needs time<br />

and trust. With regard to the indicated ›empowerment‹ <strong>of</strong> local communities, Redford<br />

et al. question the common assumption »that there is such a thing as local people who<br />

operate in a cohesive community fashion« (2006: 237). <strong>The</strong> recognition that groups <strong>of</strong><br />

people are not homogenous has also been referred to by Jeanrenaud, as she clearly<br />

points to the questions <strong>of</strong> how to define groups to which people belong: »What is a<br />

community? Who is local?« (1999: 127).<br />

Borrini-Feyerabend has attempted do answer the first question in her definition <strong>of</strong><br />

communities as »complex entities, within which differences <strong>of</strong> ethnic origin, class,<br />

caste, age, gender, religion, pr<strong>of</strong>ession, and economic and social status can create pr<strong>of</strong>ound<br />

differences in interests, capacities and willingness to invest in the management<br />

<strong>of</strong> natural resources« (cited in Redford et al. 2006: 237). According to a definition<br />

provided by Laird, a local community is »a group <strong>of</strong> people having a long-standing social<br />

organization that binds them together, <strong>of</strong>ten in a defined area« (2002: 458). Beyond<br />

specific conditions to be taken into consideration at the local level, Redford et al.<br />

(2006) assume that an understanding <strong>of</strong> the biological and social history <strong>of</strong> a given<br />

site, together with the particular political circumstances <strong>of</strong> its creation, is essential in<br />

creating feasible <strong>conservation</strong> programmes. <strong>The</strong>y specify their argument by asserting:<br />

Each site is linked to regional, national, and international scales through agri<strong>cultural</strong>, trade, and<br />

colonization policies and the politics <strong>of</strong> <strong>conservation</strong>, development, and local peoples. <strong>The</strong>se connections<br />

can interact with one another and create conditions that impact threats, partnerships, and policies.<br />

Moreover, there is no ›right scale‹, but a set <strong>of</strong> cross-scale dynamics important to <strong>biodiversity</strong>. When<br />

crafting local approaches, it is vital to understand the proximate and ultimate driving forces that have<br />

influenced and will continue to influence <strong>conservation</strong> actions (2006: 239).<br />

<strong>The</strong> authors remind to take into account that conflicts concerning a given <strong>conservation</strong>al<br />

setting shift over time, involving different threats, interest groups and social<br />

values. When developing ways <strong>of</strong> resolving these conflicts, it is important to understand<br />

these <strong>context</strong>s and not compromise the long-term viability <strong>of</strong> the protected area<br />

itself in the belief that resolving a given conflict will provide an ultimate solution. Protected<br />

areas are necessary, but not sufficient for the <strong>conservation</strong> <strong>of</strong> <strong>biodiversity</strong>. <strong>The</strong>y<br />

must be seen as an integral part <strong>of</strong> a larger national or eco-regional scheme that will<br />

effectively address <strong>conservation</strong> issues within, as well as outside park boundaries.<br />

Park-based <strong>conservation</strong> will not survive in isolation, but rather must be integrated<br />

with subordinate efforts focused on agriculture, forestry, pollution, water diversion<br />

and urban areas in order to ensure a compatible future for human societies (2006:<br />

240f.). Assuming that non-intervention is not an appropriate option to encounter the

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