Final Evaluation of the - UNEP
Final Evaluation of the - UNEP
Final Evaluation of the - UNEP
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2. To support community-led rehabilitation <strong>of</strong> degraded rangelands related to pastoralism.<br />
3. To develop sustainable management systems where indigenous knowledge is supported by<br />
modern concepts <strong>of</strong> range management.<br />
32. The achievement <strong>of</strong> localized project-funded successes on <strong>the</strong> ground is not <strong>of</strong> major<br />
importance. The key to success at <strong>the</strong> end <strong>of</strong> <strong>the</strong> project is whe<strong>the</strong>r o<strong>the</strong>r communities in<br />
similar ecosystems could adopt and replicate <strong>the</strong>se methods without similar large injections <strong>of</strong><br />
cash. The answer is no. If USD15 million failed to have a major impact on localized<br />
community management <strong>of</strong> rangelands, <strong>the</strong> chances <strong>of</strong> o<strong>the</strong>r communities being able to<br />
manage <strong>the</strong>ir range sustainably are low. The assessment <strong>of</strong> project results suggests that <strong>the</strong><br />
objective above was not achieved and is unlikely to be achieved without more time and more<br />
funding. The project has <strong>of</strong> course led to some positive consequences, <strong>the</strong> most important<br />
being community awareness raising, a modest degree <strong>of</strong> community empowerment<br />
particularly concerning NRM, and limited range rehabilitation activities. Overall, <strong>the</strong> FE<br />
echoes <strong>the</strong> MTE but elaborates with <strong>the</strong> following observations:<br />
33. The word “model” is academic and essentially meaningless to most people or at least has<br />
connotations <strong>of</strong> ma<strong>the</strong>matical or computer models. ‘Methods’, ‘systems’ or even<br />
‘methodologies’ might have been preferable. It is unrealistic to expect pastoralists and<br />
communities in ASALs to be interested in biodiversity conservation per se unless <strong>the</strong>y can<br />
derive added value from that biodiversity (e.g. Hoodia, marula or Gum Arabic). The type <strong>of</strong><br />
biodiversity should be specified viz. indigenous plants or, more specifically, range vegetation<br />
<strong>of</strong> use to communities. In degraded rangelands, invasive plants (including indigenous ones)<br />
can take hold, for example when bush invasion follows <strong>the</strong> banning <strong>of</strong> controlled burning, or<br />
when overgrazing causes unpalatable species to thrive. No clear distinction was made in <strong>the</strong><br />
PD between indigenous plant species that should be encouraged (e.g. <strong>the</strong> highly-prized<br />
Umbrella Thorn, [Acacia tortilis]) and invasive native species <strong>of</strong> low palatability and low<br />
digestibility that can reduce rangeland productivity (e.g. Acacia reficiens)1.<br />
1 The African acacias are no longer in <strong>the</strong> Australian genus Acacia and have been re-classified into o<strong>the</strong>r genera<br />
such as Faidherbia, Vachellia, Senegalia etc. For simplicity, <strong>the</strong> old generic name will be used.<br />
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