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

SUMMARY OF FINDINGS AND MANAGEMENT ACTIONS<br />

Forest-scale rating of relative watershed vulnerability to climate change shows that a majority of the<br />

Forest has “moderate” to “high” vulnerability, using categorical indicators for Water Values, Sensitivity,<br />

and Exposure. Two “hot spots,” or cluster watersheds, show the highest rating: mid-Columbia marine<br />

influence zone (temperature vulnerability), and upper NFJD, higher elevation snow zone (water supply<br />

vulnerability). A total of 29 HU12 subwatersheds, or 18%, ranked highest vulnerability. (A summary of<br />

vulnerability factors and management options is available at www.fs.fed.us/ccrc/wva/appendixes.)<br />

Bull trout habitat modeling shows current habitat quality and projected losses and fragmentation in<br />

response to warming climate. Populations in Upper NFJD may be more susceptible to human impacts.<br />

Groundwater and habitat complexity may buffer climate impacts in some watersheds. More resilient areas<br />

in Upper Lookingglass and Walla Walla could be a focus for protection and restoration.<br />

Management Actions<br />

• Verification: Field verification of potential susceptibility to hydrologic regime changes of<br />

campground and other high value developments. GIS analysis of these values was limited by<br />

quality of spatial data; some developments may or may not be vulnerable. Field verification and<br />

more detailed hydrologic modeling is needed.<br />

• Increase resilience: Use existing programs for protecting watersheds; measures include “Best<br />

Management Practices”, Forest Flood Emergency Response Plan, and land allocations<br />

(wilderness and roadless areas as refugia).<br />

• Actively restore: Evaluate restoration priorities and activities, and address vulnerable<br />

infrastructure, passage barriers, and riparian conditions.<br />

• Improve coordination: Forests are critical sources of water and habitat, but resource availability<br />

and conditions are changing, with more uncertainty. Consider findings in Forest planning,<br />

Regional vulnerability assessments, and restoration strategies. Engage with communities in<br />

adaptation strategies. Assess current juvenile bull trout populations in the key watersheds to begin<br />

the process of establishing the “thermal” limit of juvenile bull trout.<br />

• Improve monitoring: Follow the bull trout monitoring protocol and example application in the<br />

Secesh River basin (published by RMRS) to design bull trout monitoring protocol for the UNF.<br />

• Expand inventory of culvert barriers and compile other cumulative effects that may alter bull<br />

trout distribution.<br />

• Refine modeling to address variation in stream temperature scale; for example, site versus<br />

systematic variation at stream, landscape, and regional scales is an issue with many temperature<br />

studies (Isaak et al. 2010). There is a need to collect further climatic data at finer scales and<br />

consult PRISM data (OSU application) to make improvements to temperature models.<br />

222 Assessing the Vulnerability of Watersheds to Climate Change

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