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Helena National Forest Watershed Vulnerability Assessment, Northern Region (R1) climate variables assigned to each resource value. Lastly the sensitivity analysis outcome was overlaid with the exposure analysis outcome to show final watershed vulnerability for each HUC-6. Several different analysis units were used as part of this assessment. Sensitivity analysis was summarized at the subwatershed level as delineated by the sixth level (12-digit) hydrologic unit (HUC-6) hierarchy in the US Geological Survey (USGS) National Hydrography Dataset (NHD). Because many of the forest management decisions and projects are conducted at the subwatershed scale or smaller, we chose to use this scale to make this analysis most useful on the ground. This analysis includes 151 subwatersheds within the assessment area. The exposure analysis was conducted at the watershed scale (HUC-5) (Figure 2). This scale was used because the climate data was downscaled to around a 6 km hydrologic output; this data fit our analysis best at the HUC-5 watershed level. To resolve these differences in scale, we used the sensitivity analysis at the subwatershed scale and overlaid climate predications at the watershed scale to show how underlying subwatersheds may be influenced by the climate predictions, while keeping the focus at a reasonable management scale. Figure 2. HUC-6 subwatersheds and HUC-5 watersheds within Helena National Forest WATER RESOURCE VALUES The following water resource values were chosen for the vulnerability analysis. Although there are many water resource values on the Helena National Forest, we analyzed the three values that we believe are of greatest concern to the Forest. 48 Assessing the Vulnerability of Watersheds to Climate Change

Helena National Forest Watershed Vulnerability Assessment, Northern Region (R1) Bull trout • Listed as a Threatened Species throughout their range under the Endangered Species Act since 1999. • Have important habitat on the Helena National Forest west of the continental divide in the headwaters of the Columbia River. • Require colder water temperatures than most salmonids. • Require the cleanest stream substrates for spawning and rearing. • Need complex habitats, including streams with riffles and deep pools, undercut banks, and lots of large logs. • Rely on river, lake, and ocean habitats that connect to headwater streams for annual spawning and feeding migrations. Cutthroat trout • One of two subspecies of native cutthroat found in Montana. • Montana’s state fish. • Historic range was west of the Continental Divide as well as the upper Missouri River drainage. • Range has been seriously reduced due to hybridization with rainbow and/or Yellowstone cutthroat and habitat loss and degradation. • Designated a Montana Fish of Special Concern in Montana. • Common in both headwaters lake and stream environments. Infrastructure • Roads, campgrounds near streams and rivers, water diversions, bridges, etc. • Can become a safety concern for all forest users recreating in areas where streams are subject to higher flows, flash floods, etc. • Important financial investment for the Forest Service. EXPOSURE Information on predicted climate changes anticipated on the Helena National Forest came from a variety of sources. Published reports from the Rocky Mountain Research station were used to describe the general projections for the region including the projected change in the climate variable, the anticipated watershed response, and the potential consequences to watershed services (Table 1) (Rieman and Isaak, 2010). Generally, predictions agree on a warmer and sometimes drier climate (Rieman and Isaak, 2010). This will include an increase in summer maximum temperatures of approximately 3 °C by the mid-21 st century, and an increase in spring and summer precipitation accompanied by a decrease in fall and winter precipitation. 49 Assessing the Vulnerability of Watersheds to Climate Change

Helena National Forest Watershed Vulnerability Assessment, Northern Region (R1)<br />

climate variables assigned to each resource value. Lastly the sensitivity analysis outcome was overlaid<br />

with the exposure analysis outcome to show final watershed vulnerability for each HUC-6.<br />

Several different analysis units were used as part of this assessment. Sensitivity analysis was summarized<br />

at the subwatershed level as delineated by the sixth level (12-digit) hydrologic unit (HUC-6) hierarchy in<br />

the US Geological Survey (USGS) National Hydrography Dataset (NHD). Because many of the forest<br />

management decisions and projects are conducted at the subwatershed scale or smaller, we chose to use<br />

this scale to make this analysis most useful on the ground. This analysis includes 151 subwatersheds<br />

within the assessment area.<br />

The exposure analysis was conducted at the watershed scale (HUC-5) (Figure 2). This scale was used<br />

because the climate data was downscaled to around a 6 km hydrologic output; this data fit our analysis<br />

best at the HUC-5 watershed level.<br />

To resolve these differences in scale, we used the sensitivity analysis at the subwatershed scale and<br />

overlaid climate predications at the watershed scale to show how underlying subwatersheds may be<br />

influenced by the climate predictions, while keeping the focus at a reasonable management scale.<br />

Figure 2. HUC-6 subwatersheds and HUC-5 watersheds within Helena National Forest<br />

WATER RESOURCE VALUES<br />

The following water resource values were chosen for the vulnerability analysis. Although there are many<br />

water resource values on the Helena National Forest, we analyzed the three values that we believe are of<br />

greatest concern to the Forest.<br />

48 Assessing the Vulnerability of Watersheds to Climate Change

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