Strategic Planning for Species Conservation: A Handbook - IUCN
Strategic Planning for Species Conservation: A Handbook - IUCN
Strategic Planning for Species Conservation: A Handbook - IUCN
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8. Actions<br />
might there<strong>for</strong>e be recommended as an Action. Where the process of developing<br />
Objectives and Objective Targets highlights important in<strong>for</strong>mation needs, the recommended<br />
Actions should specify means of addressing these needs.<br />
In some cases, there may be considerable uncertainty about the environmental, social or<br />
political conditions under which species conservation will be attempted. For example, some<br />
parts of the world are prone to political instability; elsewhere, the effects of climate change<br />
on future habitat suitability may be uncertain. It may be helpful, in developing SCSs, to<br />
explicitly recognise such uncertainty where it exists, and to consider the potential of<br />
particular Actions to achieve their Targets under different plausible scenarios. In some<br />
cases it may be possible to develop contingency plans to deal with alternative future<br />
scenarios.<br />
8.3 How to identify which Actions to recommend?<br />
In a well-designed SCS, the Objectives (see Chapter 7) should be carefully <strong>for</strong>mulated to<br />
address the key threats and constraints identified in the Status Review (see Chapter 5) and<br />
wider problem analysis (see Chapter 7). The Actions identified as necessary to reach each<br />
Objective should there<strong>for</strong>e mitigate the threats or constraints faced by the species of<br />
concern. Although the structure of the SCS process should ensure that this is the case, in<br />
preparing such a strategy it is still worth checking that all of the Actions address the threats<br />
and constraints, and that, in turn, all of the key threats and constraints are addressed by the<br />
Actions. For example, if a species’ persistence were threatened by widespread habitat<br />
destruction, taking measures to secure or restore habitat would be appropriate Actions; in<br />
contrast, captive breeding might not be appropriate.<br />
Some constraints on successful conservation may not feasibly be mitigated by those<br />
responsible <strong>for</strong> developing or implementing the SCS (e.g., climate change, human<br />
population growth, or large infrastructure projects). In such cases, Actions will often need to<br />
focus on proximate threats. However, the need to address ultimate threats and/or<br />
constraints still needs to be clearly stated; it may also be appropriate to include Actions<br />
such as lobbying or sensitizing those organizations which do have power to influence such<br />
factors.<br />
In deciding which Actions to recommend, it may be helpful to consider multiple Actions to<br />
ameliorate the same threat or constraint. Many threats will be multi-faceted and several<br />
Actions will be required to reduce their impact. For example, reducing illegal logging might<br />
require a combination of increased patrol ef<strong>for</strong>t by <strong>for</strong>est rangers, environmental education<br />
to explain the ecosystem services provided by intact <strong>for</strong>est, and capacity development to<br />
allow initiation of <strong>for</strong>est-based tourism enterprises at the local scale, while legal action,<br />
advocacy, or consumer-boycott initiatives might be needed at the national or international<br />
scale. Box 8.1 provides some real-world examples of multiple approaches to particular<br />
threats.<br />
Once possible management approaches have been identified, but be<strong>for</strong>e any Actions are<br />
definitively recommended in the SCS, their likely effectiveness should be evaluated and<br />
documented. This is critically important: ineffective Actions waste money and other<br />
resources without contributing to the conservation of the species concerned. Indeed, there<br />
are sufficient examples of well-intentioned Actions which could reasonably have been<br />
expected to improve species’ conservation status, but in fact made matters worse (<strong>for</strong> the<br />
same or another species), to warrant routine evaluation of conservation measures,<br />
particularly <strong>for</strong> critically endangered species (see Table 8.3). The need to conduct such