Forests Sourcebook - HCV Resource Network
Forests Sourcebook - HCV Resource Network
Forests Sourcebook - HCV Resource Network
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identification can be useful for strategically selecting costeffective<br />
indicators that can provide accurate information.<br />
Indicators can range from very broad to very specific. Furthermore,<br />
indicators may be layered such that an analysis<br />
begins with broad indicators and then adds increasingly<br />
specific indicators until the information needs are met<br />
(Buck and others 2006).<br />
The selected indicators should be relevant, precise, sensitive,<br />
easy to understand, and measurable. Measurement indicators<br />
must be able to recognize tradeoffs (short-term versus<br />
long-term, at different scales, for different stakeholders) that<br />
need to be addressed in the landscape for the indicators to be<br />
credible. When employing a landscape approach, more than<br />
just the physical indicators should be measured; local livelihood<br />
outcomes also should be assessed (see box 4.12).<br />
There may be multiple indicators associated with a specific<br />
criterion—some amenable to measurement at the<br />
landscape scale and others suitable for the site level. Similarly,<br />
indicators may vary by whether they are used to measure<br />
the state of a landscape or the impact of particular<br />
interventions on landscape performance (see box 4.13).<br />
At the landscape level it is realistic for performance to be<br />
measured not by whether a desirable end condition has<br />
been achieved, but by assessing whether the combination of<br />
influences affecting change is moving the landscape in the<br />
right direction relative to stated performance criteria.<br />
Box 4.12<br />
Potential Indicators to Monitor<br />
Biophysical indicators. Specific indicators will depend<br />
on the objectives that have been identified for the landscape,<br />
and may include, but are not limited to:<br />
■ species of concern<br />
■ human disturbances<br />
■ wildlife corridors<br />
■ infrastructure impacts<br />
■<br />
■<br />
external threats to the landscape<br />
ecological function and condition<br />
These measures should give a sense of deforestation,<br />
drivers for change in the landscape, level of fragmentation,<br />
the condition of the forests, and the population of<br />
species of concern.<br />
Natural capital can include measures of:<br />
■ deforestation rates<br />
■ frequency and size of fires<br />
■ extent of certified forests<br />
■ quality of land available for agricultural<br />
production<br />
Human capital can include measures of:<br />
■ quality of clinics and health care<br />
■ quality of education<br />
■ number of qualified people<br />
■ infant mortality<br />
■ level and use of traditional knowledge<br />
Livelihood indicators. Livelihood indicators can be<br />
based on the capital assets framework. These indicators<br />
can be applied to a sample of communities and then<br />
aggregated to a landscape scale. The capital assets<br />
framework has five types of capital: (i) financial, (ii)<br />
social, (iii) natural, (iv) human, and (v) physical.<br />
Financial capital can include measures of:<br />
■ formal sector employment<br />
■ household income<br />
■ price changes in basic products<br />
■ number of local credit associations<br />
Social capital can include measures of:<br />
■ community-based initiatives<br />
■ traditional governance effectiveness<br />
■ perceptions of levels of corruption<br />
■ state agency effectiveness<br />
Source: Authors’ compilation using USFS 2006 and Buck and others 2006.<br />
Physical capital can include measures of:<br />
■ household quality<br />
■ number of kiosks selling basic products<br />
■ sources of drinking water<br />
■ village accessibility<br />
Specific monitoring activities will depend on the<br />
objectives that have been identified for the landscape,<br />
and may include, but are not limited to:<br />
■ development of local communities<br />
■ species of concern<br />
■ human disturbances<br />
■ wildlife corridors<br />
■ infrastructure impacts<br />
■ external threats to the landscape<br />
■ ecological function and condition<br />
140 CHAPTER 4: OPTIMIZING FOREST FUNCTIONS IN A LANDSCAPE