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r � <br />As oak and serviceberry have grown taller, large windbreaks have been created. In the winter, these <br />areas hold the snow, which becomes deep enough to limit all access by deer and elk. Thirty years of <br />observations on the permit area have shown that winter use of the mountain shrub type by elk and <br />deer is highly dependent on snow depth and severity of winter weather conditions. The use of <br />serviceberry has been limited to shrubs near the edges of the stands where less snow buildup occurs. <br />Depending on snow depth, elk and deer populations tend to concentrate on south facing hill slope <br />areas where snow depth is minimal. <br />Colowyo began fencing the boundaries of the Federal lease during the fall of 1976. The fencing was <br />completed during the summer of 1977. At this time all cattle were removed from the lease area. The <br />fencing was completed as part of an overall grazing management program to improve the rangeland <br />after several years of over - grazing. In 1991, Colowyo constructed a similar fence to provide a <br />boundary for the areas added to the Permit and to exclude grazing in this area. <br />Disturbed Areas <br />Disturbed acreage has been kept to a minimum in the permit area by proper planning for the location <br />of mine support facilities, haul roads, and pit advance. The mining methods, as discussed in Section <br />2.05.3, allow for a minimum amount of disturbance on an annual basis (less than 100 acres per pit), <br />when compared to strictly one or two seam mines with similar production levels which disturb <br />several hundred acres annually per pit. Topsoil and vegetation are removed during the summer and <br />fall months to allow for only enough disturbance to facilitate mining advance through June of the <br />following year. <br />Habitat Improvement Proeram <br />Prior to start-up of mining, Colowyo initiated a big game habitat improvement program in January <br />1976. The purpose of this on -going program was to increase range carrying capacity by increasing <br />available browse and increased access to herbaceous species. Another objective of the program was <br />to provide increased forage on selected undisturbed areas on and adjacent to the mine site to draw <br />wildlife away from newly reclaimed areas until the vegetation became established. A third benefit <br />was to improve enough habitat prior to and during mining in order to offset the temporary loss of <br />habitat from mining. <br />The technique for habitat improvement involved using a rubber tired or tracked dozer during the <br />winter months, preferably when there was minimal snow cover and the ground was frozen, to shear <br />off the dormant shrubs a few inches above ground level. <br />The shrubs tended to shear or break off easily when the ground was frozen leaving the root systems <br />undisturbed. During the following spring, vigorous new growth from root sprouting occurred, and <br />easy access was provided for deer and elk. This technique has had the additional effect of allowing <br />grasses and forbs to establish stands that will compete with the shrubs, thus prolonging heights <br />useable by wildlife. Approximately 30 acres of overmature decadent shrubs, i.e., serviceberry, oak, <br />and chokecherry was "brushed" on an annual basis through 1986. <br />Although no specific data has been collected on these areas, general observations have shown that <br />the areas are heavily utilized by both deer and elk. On all of the areas, any new shrub sprouting is <br />Rule 2 Permits 2.05 -43 Revision Date: 10/23/12 <br />Revision No.: RN -06 <br />