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White River National Forest Watershed Vulnerability Assessment, Rocky Mountain Region (R2)<br />

sensitivity is an artifact of its inherent characteristics, such as geology, elevation, precipitation, etc. In<br />

other words, we can’t affect most of the attributes that influence resiliency. Therefore, the focus narrows<br />

to the few things that management can actually affect – the anthropogenic influences such as water uses,<br />

roads, and vegetation management.<br />

In the subwatersheds with the highest sensitivities, any activity that maintains or increases water quantity<br />

or runoff timing would ultimately be beneficial. Specific actions could include contesting new water<br />

rights proposals, exploring ways to convert existing water rights into instream flows, and anticipating<br />

storage proposals (which are likely to increase in both size and frequency).<br />

This analysis could also help guide implementation of our travel management plan by directing where<br />

roads should be decommissioned or where reconstruction/maintenance should be scheduled to<br />

hydrologically disconnect roads from the stream network. Similarly, this analysis could also help<br />

prioritize aquatic organism passage projects at road-stream crossings to ensure that aquatic residents are<br />

able to migrate to suitable habitat as streamflow and temperatures change. Selecting the subset of high<br />

vulnerability watersheds in high pine beetle mortality areas would also help prioritize road-stream<br />

crossings for upgrades relative to floods and debris.<br />

Lastly, with a half million acres of pine beetle mortality on the Forest, the results of this analysis could<br />

help direct where active vegetation management could benefit the recovery process by enhancing natural<br />

reproduction, hydrologic recovery, stream shading, and future large woody debris recruitment.<br />

Integration with the Watershed Condition Framework Process<br />

The recently completed process for the watershed condition assessment ended with a condition rating for<br />

each subwatershed on the forest. There were 12 attributes that were rated, but the following subset of<br />

those could be directly affected by climate change:<br />

• 1.2 - Water Quality Problems<br />

• 2.1 - Water Quantity<br />

• 4 - Aquatic Biota (Exotics and Invasives)<br />

• 10.1 - Vegetation Condition<br />

• 12 - Forest Health (Insects and Disease)<br />

Changes in runoff from climate change would have direct effects on water quantity (attribute 2.1), and<br />

indirect effects on water quality (attribute 1.2) as dilution flows diminish. Less runoff may also mean<br />

more indirect effects on aquatic and riparian biota (attribute 4.0), because exotic species tend to compete<br />

well in environments with modified flows and temperatures.<br />

Changes in air temperature and the distribution of precipitation types would eventually affect the<br />

distribution of vegetation types and the overall vegetation condition (attribute 10.1). Local experience<br />

with the mountain pine beetle has shown that insects and diseases (attribute 12) can propagate in<br />

unexpected ways with small changes in air temperature.<br />

Since the Watershed Condition Framework assessment and this climate change vulnerability assessment<br />

were both conducted at the subwatershed scale, they are easily integrated. Identifying areas where<br />

diminished watershed condition attributes overlap with high climate change vulnerability can help target<br />

restoration priorities.<br />

127 Assessing the Vulnerability of Watersheds to Climate Change

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