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xlps =average reference azea all hit herbaceous covet-improved <br />• pasture-subirrigated <br />Ta =total of relative community types used in comparison, premise area <br />Average vegetation cover will be used for reclaimed azeas because successional development will have <br />established a predominantly herbaceous community even with shrubs present. <br />The cover success standazd for all permanently reclaimed areas in the haul road corridor will be 35 <br />percent. This value represents the weighted mean herbaceous vegetation cover for the sagebrush, <br />western wheatgrass/alkali sagebrush, alkali sagebrush/greasewood, and alkali meadow types as <br />derived from baseline data. The latter two types encompass only 3.2 and 1.4 acres, respectively. In <br />addition, the alkali meadow type has been variously disturbed Neither type is extensive or unique <br />enough to warrant a separate success standard. The weighted mean cover value was detemvned from <br />cover data for the four types as determnied during 1992 supplemental baseline vegetation studies (see <br />Appendix B to Attachment 10.1, Tab 10, Vegetation). Foz vegetative cover, the revegetated azea shall <br />be considered acceptable if it is not less than 90 percent of the standazd (35) with 90 percent statistical <br />confidence. <br />• The value of 35 percent herbaceous vegetation cover is a reasonable value when combined with the <br />anticipated litter values of 15 percent (see previous discussion) and the more retie site conditions <br />along the cosidor. Also, the value of 35 percent herbaceous cover for the standard is nearly identical <br />to the herbaceous cover for the upland improved pasture type sampled during the 1992 supplemental <br />baseline studies. This premise type represents reseeded lands previously occupied by the sagebrush <br />and western wheatgrass/ alkali sagebrush types prior to disturbance. The sagebrush and western <br />wheatgrass/alkali sagebrush types represent the dominant native vegetation types along the corridor, <br />which will be affected. Undisturbed areas of the above vegetation types may be used to verify the <br />above cover standard; however, at this time it is uncleaz as to how much azea of these two types will <br />remain undisturbed in the haul road corridor portion of the permit area. <br />Conservation Reserve Program (CRP) lands were occupied by the sagebrush and western <br />wheatgrass/alkali sagebmsh types prior to being cropped CRP lands will be seeded with the <br />permanent mix used in the haul road corridor unless the landowner specifically requests the <br />postmining land use be cropland In this case, cropland success standards will apply. As discussed in <br />• Tab 4, baud Use and Tab 10, Vegetation, CRP lands aze former cropland areas seeded to a permanent <br />vegetative cover for a period of ten years. At the end of the ten-yeaz period, these lands may be <br />PR-02 37 Revised 01/06 <br />