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WSP09652
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Last modified
1/26/2010 2:55:00 PM
Creation date
10/12/2006 3:47:15 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8200.765
Description
White River General
State
CO
Basin
Yampa/White
Water Division
6
Date
3/1/1994
Author
USFS
Title
Snowmass Ski Area - Final Environmental Impact Statement - White River National Forest - Aspen Ranger District - Volume I
Water Supply Pro - Doc Type
Report/Study
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<br /> <br />between the Snowmass and Tiehack Ski Areas., Due in large part to its <br />inaccessibility for recreation, the Main willow Creek drainage is considered to <br />be the best remaining summer range within the MB-SW. Most of the proposed <br />expansion area contains summer range of low-to-moderate suitability for elk. <br />Some lower elevations, however, provide habitat of high suitability during early <br />summer. <br /> <br />During years with deep snows, winter range represents the most limiting habitat <br />factor on the MB-SW elk herd. Approximately 11,600 acres (28%) of the big game <br />LA are classified as winter range. The majority of the winter range is in <br />private ownership and zoned for some level of development. Approximately 700 elk <br />from various summer ranges, including those on the PA, use this winter range. <br /> <br />Spring and fall transition ranges used by the MB-SW elk herd are found on the <br />eastern portion of the permit area and include adjacent private lands as well as <br />NFSL between the Snowrnass and Tiehack Ski Areas. <br /> <br />The MB-SW elk herd traditionally migrates between winter range, north of the PA, <br />and summer range, in the Burnt Mountain area, crossing within 0.4 miles on either <br />side of the Brush Creek-Owl Creek (Glendale) Divide. Private land and ski area <br />development have significantly reduced the historic elk migration corridor to <br />approximately ten percent of its pre-development size. ' <br /> <br />Veqetative Habitat Tvces <br /> <br />There have been substantial changes in the quantity and distribution of habitat <br />types since ski resort development began. Most notable are increased acreages <br />of man-made openings and corresponding decreases in the forested types -- <br />spruce/fir mixed conifer, aspen, and lodgepole pine. Prior to development, a <br />total of 1,735 acres, of man-made opening existed on the LA, primarily as <br />agricultural fields. Since then, an additional 2,120 acres of wildlife habitat <br />have been altered (18 percent of the LA) . <br /> <br />One undeveloped block of natural habitat between the Tiehack and Snowrnass Ski <br />Areas, approximately 2 . 5 miles wide, remains within the upper Roaring Fork <br />Valley.' All of the remaining old growth within the LA is located on NFSL in <br />three blocks of spruce fir/mixed conifer forest -- one directly east of the ridge <br />that separates the Elk Camp pod from Burnt Mountain, one directly east of the <br />existing permit area boundary adjacent to mid-Burnt Mountain, and one below <br />Hanging Valley. <br /> <br />Wetlands and riparian communities are considered to be the habitats which support <br />the highest densities and diversities of wildlife species. Development <br />activities which affect these habitats will generally have the most significant <br />impacts. <br /> <br />2. Environmental Consequences <br /> <br />Elk and Deer <br /> <br />Two scenarios are used to assess potential impacts from NFSL and private land <br />development on big game habitats. A "Partial Mitigation" Scenario, equivalent <br />to the scenario assessed in the DEIS, incorporates (1) avoidance and mitigation <br />of impacts inherent in the design of the range of alternatives, and (2) an <br />estimate for private land development within the PA, outside of East Village, of <br />one house every 35 acres. An additional "Full Mitigation" scenario is assessed <br />at the request of Pitkin County and includes (1) avoidance and mitigation of <br />impacts inherent in the design of the alternatives, (2) a reduced estimate of <br />private land development based upon aggressive implementation of 1041 <br />requirements, and (3) implementation of a variety of additional mitigation <br />measures. The full mitigation scenario is not applied to Alternative E because <br />its basic design is inconsistent with objectives for additional habitat <br />protection. <br /> <br />Summary . 16 <br />
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