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Umatilla National Forest Watershed Vulnerability Assessment, Pacific Northwest Region (R6)<br />

Value-Risk Matrix<br />

Low Risk/Value High<br />

Rank L ML M MH H Rank<br />

High 7 M MH H H H 7 High<br />

Vulnerability<br />

6 ML M MH H H 6<br />

5 ML ML M MH MH 5<br />

4 L L ML M MH 4<br />

217 Assessing the Vulnerability of Watersheds to Climate Change<br />

Vulnerability<br />

Low 3 L L L ML M 3 Low<br />

Rank L ML M MH H Rank<br />

Low Risk/Value High<br />

Exposure was ranked from 3 to 7 and categorized as follows: 0-3=L; 4=ML; 5=M; 6=MH; 7=H.<br />

Data were categorized into 5 categories for values, sensitivity, and exposure, but were simplified into 3<br />

categories for the composite relative watershed vulnerability using the matrix.<br />

The composite analysis included all resource values and sensitivity and climate factors, to produce a<br />

composite relative watershed vulnerability rating. Two individual coarse-scale analyses were also<br />

performed to assess relative vulnerability of individual values for aquatic species and infrastructure in a<br />

similar process; however, only individual values and stressors and climate variables that could affect<br />

those individual values were included in the analysis.<br />

Individual Value Ranking: Infrastructure Vulnerability<br />

Infrastructure vulnerability (see figure below) was assessed using high-value developments<br />

(campgrounds, guard stations, and other buildings) as the value metrics. Sensitivity and vulnerability<br />

factors included in the analysis were similar to those used in composite analysis, with the exclusion of<br />

roads and developments. Change in SWE was the only climate factor used to assess exposure; changes in<br />

summer and winter temperature are not expected to have a direct effect on infrastructure and<br />

development.

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