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Principles of terrestrial ecosystem ecology.pdf

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Table 16.3. Examples <strong>of</strong> services provided by rivers,<br />

lakes, aquifers, and wetlands.<br />

Water supply<br />

Drinking, cooking, washing, and other household uses<br />

Manufacturing, thermoelectric power, and other<br />

industrial uses<br />

Irrigation <strong>of</strong> crops, lawns, etc.<br />

Aquaculture<br />

Supply <strong>of</strong> goods other than water<br />

Fish<br />

Waterfowl<br />

Clams and mussels<br />

Nonextractive or in-stream benefits<br />

Flood control<br />

Transportation<br />

Recreational swimming, boating, etc.<br />

Pollution dilution and water-quality protection<br />

Hydroelectric generation<br />

Bird and wildlife habitat<br />

Enhanced property values<br />

Nonuser values<br />

Data from Postel and Carpenter (1997).<br />

decisions <strong>of</strong>ten ignore the value <strong>of</strong> the resource<br />

and assume that the <strong>ecosystem</strong> service was<br />

“free” (Daily et al. 2000).<br />

Valuation <strong>of</strong> <strong>ecosystem</strong> services is a way to<br />

organize information to help make such decisions<br />

(Daily et al. 2000).Valuation <strong>of</strong> <strong>ecosystem</strong><br />

services requires sound ecological information<br />

and a clear understanding <strong>of</strong> alternatives and<br />

impacts. Ecological understanding is critical, for<br />

example, to characterize the services provided<br />

by <strong>ecosystem</strong>s and the processes by which they<br />

Table 16.4. Examples <strong>of</strong> <strong>ecosystem</strong><br />

services and valuation<br />

methods.<br />

Integrative Approaches to Ecosystem Management 367<br />

are generated. This information is frequently<br />

site specific, so local ecological knowledge is<br />

needed. Ecological and economic information<br />

must then be integrated to make sound decisions.<br />

Several approaches have been used to<br />

assign economic value to <strong>ecosystem</strong> goods<br />

and services. These include direct valuation<br />

approaches, by which economic worth is<br />

assigned according to avoided costs or to<br />

market value, and indirect approaches, which<br />

estimate the worth <strong>of</strong> a good or service through<br />

surveys and contingent valuation (Goulder and<br />

Kennedy 1997) (Table 16.4). Although the<br />

methodology is still developing, economic<br />

valuations <strong>of</strong> the provision <strong>of</strong> goods or services<br />

have successfully contributed to decision<br />

making about <strong>ecosystem</strong> management at a<br />

variety <strong>of</strong> scales (Daily et al. 2000) (Box 16.3).<br />

Valuation <strong>of</strong> goods and services requires<br />

both their identification and an assessment<br />

<strong>of</strong> their temporal and spatial variability, their<br />

vulnerability to stresses, and the extent to<br />

which they can be predicted using simulation<br />

models or indicators. Ecologists <strong>of</strong>ten have a<br />

sense for what allows an <strong>ecosystem</strong> or landscape<br />

to provide a given service, but we have a<br />

limited ability to quantify that service and to<br />

predict it in the future. When, for example,<br />

and under what conditions, will a watershed<br />

provide clean water? Do all mangroves protect<br />

shorelines?<br />

Valuation <strong>of</strong> <strong>ecosystem</strong> services is <strong>of</strong>ten<br />

applied to a single variable or resource (e.g.,<br />

Service Valuation method<br />

Inputs that support production<br />

Pest control avoided cost<br />

Flood control avoided cost<br />

Soil fertility avoided cost<br />

Water filtration avoided cost<br />

Sustenance <strong>of</strong> plants and animals<br />

Consumptive uses direct valuations based on market prices<br />

Nonconsumptive uses indirect valuations (travel cost or<br />

contingent aluation methods)<br />

Provision <strong>of</strong> existence values indirect valuations (contingent valuation<br />

method)<br />

Provision <strong>of</strong> option values empirical assessments <strong>of</strong> individual risk<br />

aversion<br />

Data from Goulder and Kennedy (1997).

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