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<br />''\<'" ~ 8' 7 <br />;, I) .'J,' 0., <br />r_ ~_ ,_ L <br /> <br />under the Full Mit~gation scenario (Table S-9), impacts would be expected to be <br />less severe in all alternatives. It is not anticipated that all mitigation <br />measures would be fully implemented or successful, and the long-term reduction <br />in the elk herd would be expected to fall somewhere between the Partial and FUll <br />Mitigation scenarios. A viable, but reduced, elk herd would be expected to be <br />maintained in the long term under all action alternatives, except possibly under <br />Alternative E. <br /> <br />Table 5-9: Potential Reductions to the MB-SW Elk Herd by Alternative, Full Mitigation Scenario' <br /> <br />Alternative <br /> <br />% <br />Reduction <br /> <br />% of Current <br />PODulation Remainin2 <br /> <br />% Reduction Due <br />To NFSL tievelooments <br /> <br />Current Situation <br />A <br />B <br />E <br />F <br />G <br />H <br /> <br />100 <br />70-80 <br />70-80 <br />2D-40 <br />60-70 <br />55-6S <br />65-75 <br /> <br />>0' <br />>0' <br />50-60 <br />10-20 <br />15-25 <br />5-15 <br /> <br />20-30 <br />20-30 <br />60-80 <br />3D-40 <br />35-45 <br />25-35 <br /> <br />I Expeaed reductions in the size of the elk herd which spends at least a portion of the year within the pennit area, due to cumulative impactS associated <br />with full implementation of each of the alternatives and full mitigation applied <br />a Recreational activities on NFSL arc expected to increase under al1 altemativC$. These impacts do not affect habitat directly but will result in <br />disturbances and potential displacement from suitable habitat. The level of these impacts cannot be quantified at this time. <br /> <br />Impacts on the mule deer herd would be expected to be similar but much less <br />severe. Although deer are considered to be more tolerant of disturbance, the PA <br />deer population would be expected to be reduced some unquantifiable amount due <br />to actions associated with the alternatives. <br /> <br />Other Mammals <br /> <br />Bighorn Sheep would not be expected to be significantly affected under any of the <br />alternatives. <br /> <br />Development activities in all alternatives would render both NFSL and private <br />lands less valuable as black bear foraging habitat. Some changes to available <br />food sources would r,esult from the conversion of forest habitats to man-made <br />openings. Full buildout of private lands would render them unsuitable for black <br />bear summer foraging. Black bears are considered to be secure as a species <br />within the RA and none of the alternatives would jeopardize the overall species <br />viability. <br /> <br />Martens, voles and other small mammals would be most adversely affected by the <br />conversion of forest habitats to man-made openings (Table S-20l. <br /> <br />Avian Soecies <br /> <br />Impacts to avian species would likely be most significant in riparian habitats, <br />particularly for those species dependent upon large homogeneous blocks of <br />forested habitats and for snag-dependent species. Impacts would be least adverse <br />in Alternatives B, H, and F; and most adverse in G and E, respectively. <br /> <br />Residential development within the PA would render much of the private land <br />unsuitable for nesting by raptors in all alternatives. <br /> <br />Construction and maintenance of new lifts and ski trails would temporarily <br />displace most raptor species from foraging habitats adjacent to construction <br /> <br />Summary . 19 <br /> <br />