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The operator had originally developed an alluvial well field neaz the confluence of Scullion <br />Gulch and the White River to supply water for mine operations. In 1984, Kenney Reservoir was <br />completed above Rangely, Colorado. Kenney Reservoir impounds the White River through the <br />southern portion of the permit area, inundating much of the alluvial well field. Because the <br />alluvial surface is almost completely submerged by the reservoir, recharge to the alluvium is now <br />instantaneous. Due to inundation of the well field by the reservoir, and due to high salinity of the <br />alluvial well water, the operator now pumps water directly from the White River into an adjacent <br />lagoon, and from there, water is pumped to the mine's raw water storage tank.. Only one <br />alluvial well, Qal-5, located at the mouth of Scullion Gulch, remains in use as a monitoring well. <br />The Red Wash Syncline and major fracture zones located along Red Wash, Scullion Gulch, and <br />the White River control movement of the Mesaverde groundwater. Groundwater in the <br />northwest part of the permit azea moves down dip to the Red Wash Syncline. Within the central <br />and southern portion of the permit area, groundwater flows south to the White River. <br />Surface water drainage patterns in the area aze incised and dendritic. Scullion Gulch and Red <br />Wash flow primarily in response to direct precipitation. The White River is a perennial stream <br />receiving dischazge from the permit and adjacent azeas. The majority of flows in the White River <br />occur between May and July in response to snowmelt. <br />Soils in the azea include the Cushman, Forelle, Pinelli, Potts, Satanka and Wortka series, which <br />aze developed on ridge tops, ridge sideslopes, and in valley fans. Underdeveloped soils such as <br />Colorado, Haverson alkali phase, Kinnear, Moyerson, Redcreek, Rentsac, and Turley variant <br />occur on low floodplains, extreme ridge tops, and upper ridge sideslopes. <br />Eight plant communities have been identified in the permit area to be affected by surface <br />operations and facilities. Vegetation communities consist of juniper woodland, juniper <br />woodland-big sagebrush, big sagebrush, big sagebrush-wheatgrass, western wheatgrass, <br />Colorado wildrye, cheatgrass-annual forb, and big sagebrush-greasewood. These communities <br />comprise a mosaic controlled by soil type, topography, and past and present land uses. Historic <br />grazing practices may have contributed to the extent of the cheatgrass-annual forb vegetation <br />type throughout the permit azea. The permit azea is currently used aswinter/spring range for <br />domestic sheep. <br />Wildlife species found within the permit azea include mule deer (Odocoileus hemionus), <br />pronghorn antelope (Antilocapra americana), and sage grouse (Centrocercus urophasianus). <br />Numerous raptor species have been identified in the azea. Species include the ferruginous hawk <br />(Buteo regalis), turkey vulture (Cathortes aura), mazsh hawk (Cireus cyaneus), American kestrel <br />(Falco sparverius), sharp-shinned hawk (Accipter shiatus), burrowing owl (Spestyto <br />cunieulaira), red-tailed hawk (Buteo jamaicaensus), and golden eagle (Aquila chrysauetos). <br />Bald eagles (Hliaeetus leucocephalus) and peregrine falcons (Falco seregrinus) aze known to <br />migrate through the area. Lazge white-tailed prairie dog (Cynomys leucurus) towns exist in the <br />azea of the refuse disposal sites. <br />1R <br />