watervulnerability
watervulnerability
watervulnerability
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Gallatin National Forest Watershed Vulnerability Assessment, Northern Region (R1)<br />
Exposure<br />
To evaluate exposure, we used the regional downscaled climate and hydrological projections developed<br />
by Littell et al. (2011), which build on research and data from the Climate Impacts Group (CIG) at the<br />
University of Washington. We chose their Ensemble model to examine potential climate change impacts<br />
more closely. This model is composed of the 10 best-fitting global circulation models (GCMs) for the<br />
Upper Missouri River Basin region. The modeled time periods available are 1916-2006 (historic), 2030-<br />
2049 (mid-21 st century), and 2070-2099 (late 21 st century).<br />
The climate projections are downscaled to 6 km 2 resolution and are most appropriately summarized at the<br />
HUC-5 scale. The HUC-6 subwatersheds were overlaid to examine how they may be influenced by these<br />
climate projections. The metrics retrieved for the most current run of the WVA include variable<br />
infiltration capacity (VIC) derived (Liang et al. 1994; Liang et al. 1996) hydrological projections:<br />
combined annual flow, seasonality of flow, and snowpack vulnerability (hydrologic regime). For the<br />
Upper Missouri River Basin, some of the overall trends predicted for the mid- to late 21 st century include<br />
increases in average annual air temperature, increases in seasonal air temperatures, increases in winter<br />
precipitation, and decreases in summer precipitation.<br />
Currently, we have used only the air temperature projections to examine predicted trends. In the future,<br />
these predicted air temperatures, combined with our stream temperature model (in development) and local<br />
air temperature data, may be used to model and predict stream temperatures across the forest.<br />
Potential Impacts to Water Resources<br />
1. Increased instances of low flows and lower flows<br />
• Water uses/diversions would amplify the anticipated low flows<br />
• Culverts currently passable by fish may become barriers during low flows<br />
2. Changes in flow regime<br />
• Increased winter flooding could increase summer low flows; increased/prolonged drought<br />
in the summer will further amplify the effects of changes in flow<br />
• Increased winter scouring of fall spawners (brook trout)<br />
− May favor native cutthroat trout<br />
3. Increased stream temperatures<br />
• Previously unsuitable stream habitats (too cold) may become suitable for fish<br />
• At lower elevations, native cold-water fish will be negatively affected<br />
− More tolerant invasive fish species may outcompete natives<br />
−<br />
4. Increased precipitation events<br />
• Roads would have increased sedimentation into streams<br />
• Culverts may need to be enlarged and/or maintained more frequently to accommodate<br />
higher flow<br />
• Some roads may need more frequent maintenance<br />
5. Increased drought events<br />
• Water use/diversions would exacerbate drought events<br />
• Possible increases in wildfires<br />
41 Assessing the Vulnerability of Watersheds to Climate Change