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NEPA--Environmental Assessment

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Similar to Alternative 2, selecting Alternative 3 would have both positive and negative effects for<br />

sensitive species. Selecting Alternative 3 would have beneficial effects for sensitive species,<br />

compared to Alternative 2, because application of adaptive management strategies and project<br />

design criteria should result in more rapid improvements in habitat conditions in some localized<br />

areas where sheep grazing impacts are currently occurring. Also similar to Alternative 2, Alternative<br />

3 would have negative effects for sensitive species, compared to Alternative 1, because a few<br />

localized areas would continue to be affected by sheep grazing activities, such as near the<br />

alpine/spruce-fir interface, moist alpine areas adjacent to riparian zones or wet meadows, and upland<br />

willow stands in alpine basins.<br />

Selecting Alternative 3 would be more beneficial for sensitive species than selecting Alternative 2,<br />

but would be less beneficial than selecting Alternative 1. This is because improvement in habitat<br />

conditions would probably occur over a longer time frame than under Alternative 1, but a shorter<br />

time frame than Alternative 2 due to the application of adaptive management strategies and project<br />

design criteria. In general, habitat conditions for sensitive species are expected to continue to<br />

gradually improve in most areas under Alternative 3, but would continue to be impacted in a few<br />

localized areas.<br />

Compared to Alternative 2, the application of adaptive management strategies and project design<br />

criteria under Alternative 3 should result in more rapid improvements in habitat conditions in some<br />

localized areas where sheep grazing impacts are currently occurring because adaptive management<br />

strategies would not be fully applied under Alternative 2. Although more rapid improvement in<br />

habitat conditions for bighorn sheep, white-tailed ptarmigan and wolverine is expected under<br />

Alternative 3 than under Alternative 2, improvements in habitat conditions as a result of the adaptive<br />

management approach are likely to be too small to affect populations or the total amount of habitat<br />

available for these species in the Silverton Landscape.<br />

Selecting Alternative 3 would be much more beneficial for bighorn sheep than selecting Alternative<br />

2, although less so than selecting Alternative 1. Alternative 3 would be less beneficial for bighorn<br />

sheep than Alternative 1 because five allotments with areas of mapped overlap between domestic<br />

sheep and bighorn sheep summer range (Picayne/Mineral Point, Engine Creek/Deer Creek, Eureka,<br />

and Gladstone active allotments, and Flume vacant allotment) would remain open to sheep grazing<br />

under Alternative 3. However, the potential for contact between domestic sheep and bighorn sheep<br />

in these five allotments with areas of mapped overlap would be reduced from High to Moderate (4<br />

active allotments) or Low (1 vacant allotment).<br />

Alternative 3 would be much more beneficial for bighorn sheep than Alternative 2. This is because<br />

three vacant allotments would remain available for sheep grazing under Alternative 2 (Little<br />

Molas/West Needles Allotment, Needles Mountains Allotment, and Minnie Gulch Allotment) but<br />

would be permanently closed to grazing under Alternative 3 (Figure 3-1). These three allotments<br />

would have High Risk for contact if they were stocked with domestic sheep under Alternative 2, but<br />

would have Low Risk for contact if closed under Alternative 3. For this reason, the potential for<br />

physical contact between domestic sheep and bighorn sheep in these 3 allotments would be reduced<br />

from High to Low, and the project’s desired condition for bighorn sheep would be met in these three<br />

allotments.<br />

As a result of closing these three allotments, under Alternative 3 the amount of mapped overlap<br />

between areas suitable for domestic sheep and mapped bighorn sheep summer range in the Silverton<br />

Landscape would be reduced from about 10,285 acres (Alternative 2) to about 1,756 acres<br />

(Alternative 3). The areas of mapped overlap between bighorn sheep and domestic sheep ranges<br />

where risk of physical contact between bighorn and domestic sheep is thought to be High would all<br />

be reduced to Moderate Risk with the modification of allotment boundaries and the application of<br />

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