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The conservation of tigers and other wildlife in oil palm plantations

The conservation of tigers and other wildlife in oil palm plantations

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Integrat<strong>in</strong>g <strong>oil</strong> <strong>palm</strong> management <strong>in</strong>to a collaborative l<strong>and</strong>scape<br />

approach to conserv<strong>in</strong>g unprotected areas<br />

<strong>The</strong> need for a l<strong>and</strong>scape approach to <strong>conservation</strong><br />

<strong>The</strong> results <strong>and</strong> recommendations <strong>of</strong> this report show the high negative impact <strong>oil</strong><br />

<strong>palm</strong> production has on the majority <strong>of</strong> <strong>wildlife</strong> species studied <strong>and</strong> a variety <strong>of</strong><br />

methods for reduc<strong>in</strong>g these impacts. It is clear that <strong>oil</strong> <strong>palm</strong> <strong>plantations</strong> will never be<br />

<strong>wildlife</strong> sanctuaries, but they can mitigate their impact by becom<strong>in</strong>g more sensitive to<br />

<strong>wildlife</strong> distributions <strong>and</strong> the survival requirements <strong>of</strong> local <strong>wildlife</strong> populations.<br />

However, isolated actions by <strong>in</strong>dividual <strong>plantations</strong> will not be sufficient to br<strong>in</strong>g large<br />

scale change to the crisis currently fac<strong>in</strong>g <strong>wildlife</strong> <strong>in</strong> Indonesia. Spar<strong>in</strong>g <strong>wildlife</strong><br />

populations through responsible plant<strong>in</strong>g is po<strong>in</strong>tless if those same populations are<br />

then left isolated <strong>and</strong> unprotected. Sett<strong>in</strong>g aside <strong>wildlife</strong> refuges is po<strong>in</strong>tless if there<br />

are no species <strong>of</strong> <strong>wildlife</strong> left to utilise them. Buffer zones are po<strong>in</strong>tless if the protected<br />

areas they are buffer<strong>in</strong>g are unprotected. Habitat corridors are po<strong>in</strong>tless if they have<br />

nowhere to connect to. Action with<strong>in</strong> the <strong>oil</strong> <strong>palm</strong> <strong>in</strong>dustry must therefore be carried<br />

out as part <strong>of</strong> a l<strong>and</strong>scape approach to biodiversity <strong>conservation</strong> at the regional level.<br />

<strong>The</strong> need for a l<strong>and</strong>scape approach can be best illustrated us<strong>in</strong>g a l<strong>and</strong>scape map.<br />

Figure 31 shows an area <strong>of</strong> approximately 50,000km 2 around Jambi, Sumatra from<br />

<strong>conservation</strong> perspective. About 12% <strong>of</strong> the area is legally protected. Eight percent is<br />

classed as core protected area (Taman Nasional) with the rema<strong>in</strong>der represented by a<br />

range <strong>of</strong> semi-protected areas (such as suaka marga satwa, hutan l<strong>in</strong>dung <strong>and</strong><br />

kawasan essensial). This is fairly representative <strong>of</strong> Indonesia as a whole where<br />

approximately 12% <strong>of</strong> the area is protected to some degree, although only about a<br />

quarter <strong>of</strong> this is national parks. Outside the various protected areas lie a range <strong>of</strong> l<strong>and</strong><br />

uses – <strong>oil</strong> <strong>palm</strong>, m<strong>in</strong><strong>in</strong>g, forestry, agriculture <strong>and</strong> settlements.<br />

Figure 32 - L<strong>and</strong>scape plann<strong>in</strong>g for <strong>conservation</strong> <strong>in</strong> eastern Sumatra. Polygons represent<br />

protected or semi-protected areas. Red shades represent likely <strong>conservation</strong> value from high<br />

(dark) to low (pale)<br />

It is generally imag<strong>in</strong>ed that the <strong>wildlife</strong> is found almost exclusively <strong>in</strong> the protected<br />

areas. However, if <strong>wildlife</strong> were truly restricted to these relatively isolated protected<br />

isl<strong>and</strong>s, many species could not be expected to survive. In reality, we know <strong>wildlife</strong> still<br />

exists outside protected areas. Many species <strong>in</strong> protected areas are likely to be<br />

supported by these rema<strong>in</strong><strong>in</strong>g populations outside. A likely distribution <strong>of</strong><br />

‘<strong>conservation</strong> value’ has therefore been mapped onto the l<strong>and</strong>scape. (In this case we<br />

are us<strong>in</strong>g likely terrestrial mammal distribution as our <strong>conservation</strong> value, but<br />

<strong>conservation</strong> value could <strong>in</strong>clude any species, ecosystem functions, value to local<br />

communities etc.). Dark red shows areas <strong>of</strong> high value, where most <strong>wildlife</strong> exists. <strong>The</strong><br />

medium shade <strong>in</strong>dicates medium value where <strong>wildlife</strong> persists but not <strong>in</strong> as high<br />

numbers as red. Pale red is low value, <strong>in</strong>dicat<strong>in</strong>g areas where <strong>wildlife</strong> is only<br />

occasionally present. No colour means negligible or no value, <strong>in</strong>dicat<strong>in</strong>g no<br />

compatibility with <strong>wildlife</strong> at all. Generally, most <strong>of</strong> the protected areas will conta<strong>in</strong><br />

high <strong>wildlife</strong> value, although problems <strong>of</strong> encroachment, hunt<strong>in</strong>g or simply unsuitable<br />

habitat will mean not all protected areas are uniformly high value. However,<br />

unprotected areas will also conta<strong>in</strong> significant value. Such areas may not be as<br />

valuable <strong>in</strong> their own right as red areas but can have crucial connect<strong>in</strong>g roles. <strong>The</strong>se<br />

areas would <strong>in</strong>clude l<strong>and</strong> uses with high <strong>wildlife</strong> compatibility such as the selective<br />

logg<strong>in</strong>g concession described <strong>in</strong> this report. Low density, wide-rang<strong>in</strong>g species <strong>in</strong> the<br />

smaller protected areas, such as <strong>tigers</strong> <strong>and</strong> elephants, may well depend entirely on<br />

these connection areas for their long term survival.<br />

<strong>The</strong> recommendations proposed for the <strong>oil</strong> <strong>palm</strong> <strong>in</strong>dustry to <strong>in</strong>crease compatibility<br />

54 Wildlife <strong>conservation</strong> <strong>in</strong> <strong>oil</strong> <strong>palm</strong> <strong>plantations</strong>

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