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Policies to Reduce Emissions from Deforestation and Degradation ...

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Table 3.1<br />

Utility <strong>and</strong> Cost of<br />

Optical Sensors<br />

Currently Used <strong>to</strong><br />

Moni<strong>to</strong>r<br />

<strong>Deforestation</strong><br />

Source: reproduced <strong>from</strong><br />

DeFries et al. (2006)<br />

with the establishment of a local governance institution (Trines et al. 2006). <strong>Degradation</strong> can also<br />

result <strong>from</strong> large-scale selective logging, which is more costly <strong>to</strong> abate.<br />

Forest degradation can be defined by a tree cover criterion, a forest biomass criterion, or some<br />

combination thereof. The decision of how <strong>to</strong> define degradation <strong>and</strong> whether <strong>to</strong> moni<strong>to</strong>r it will<br />

affect the cost <strong>and</strong> complexity of a moni<strong>to</strong>ring program.<br />

Mollicone et al. (2007) suggest a categorization scheme that divides l<strong>and</strong> in<strong>to</strong> intact forest, nonintact<br />

forest, <strong>and</strong> nonforest, based on a combination of canopy cover criteria <strong>and</strong> human impact criteria.<br />

This scheme accounts for the degradation of carbon s<strong>to</strong>cks that can occur in forests. Although<br />

this scheme allows for more accurate accounting of carbon s<strong>to</strong>cks, it is also more costly<br />

<strong>and</strong> more difficult <strong>to</strong> employ because of the higher-resolution imagery required <strong>to</strong> distinguish<br />

among forest categories.<br />

Measurement of Distinctions Among Categories<br />

A number of studies have concluded that current technology can accurately measure tropical deforestation<br />

(DeFries et al. 2005, 2006; UNFCCC 2006; Mollicone et al. 2007). However, continued<br />

moni<strong>to</strong>ring capabilities rely on the successful launch of the latest L<strong>and</strong>sat sensor, scheduled for<br />

2010, without which l<strong>and</strong> cover moni<strong>to</strong>ring will be compromised (DeFries et al. 2005). Existing<br />

data will allow for the establishment of baseline deforestation rates against which current rates<br />

can be compared (DeFries et al. 2005). Table 3.1 provides an overview of the technologies available<br />

<strong>to</strong> moni<strong>to</strong>r deforestation.<br />

Geographic <strong>and</strong> ecological characteristics, such as seasonality of forests, slope, <strong>and</strong> cloud cover<br />

affect the choice of appropriate methodologies. For example, a deciduous forest in a temperate<br />

climate would have <strong>to</strong> be observed in the summer lest it appear not <strong>to</strong> meet a forest canopy criterion.<br />

Other types of forests would have <strong>to</strong> be moni<strong>to</strong>red multiple times per year. Although no<br />

single methodology will be appropriate for all forest types, many suitable methods <strong>and</strong> pro<strong>to</strong>cols<br />

exist or can be developed through the adaptation of existing methodologies.<br />

SENSOR EXAMPLES OF UTILITY FOR<br />

RESOLUTION CURRENT SENSORS MONITORING COST<br />

Very high (10–20 ha) <strong>and</strong> locate<br />

“hotspots” for further<br />

analysis with high<br />

resolution<br />

3 <strong>Policies</strong> <strong>to</strong> <strong>Reduce</strong> <strong>Emissions</strong> <strong>from</strong> <strong>Deforestation</strong> <strong>and</strong> <strong>Degradation</strong> in Developing Countries

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