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West Elk Mine <br />supplied with subsurface water through interconnection with fractures or springs. Some <br />groundwater seepage may occur from the wetland to the river via groundwater. However, the site <br />of the highway embankment and the compaction that should have occurred during its construction, <br />probably restrict groundwater flow to the river. The only drainage exit from the wetland area is a <br />road culvert that has been blocked by animal activity; therefore, the only avenues of -exit are <br />evapotranspiration-and seepage. <br />Vegetation of the wetland community is characteristic of swamps or marshes with relatively <br />stagnant hydrologic conditions, and is dominated by olcl and senescent Populus angustifoZia <br />(narrowleaf cottonwood) individuals along the edges of the wetland, numerous Salix sp. (willow) <br />clumps along the edges extending to the center, and a dense mixture of Typha latifolia (cattail), <br />Carex sp. (sedges), and Agrostis alba (redtop). Approximately the west third of the wetland had <br />standing water present in September 1995, while the remainder of the azea was subirtigated (no <br />standing water on the surface, but saturated conditions below the ground surface). <br />Total vegetation cover of this community was estimated between 50 and 65 percent. Herbaceous <br />production was approximated to be between 200 and 300 g/m2 (1780-26751bs/acre). Woody plant <br />density was estimated at 1000 stems/acre, dominated by the willow thickets. <br />The small size and relative inaccessibility of this area and vegetation community significantly limit <br />its potential uses. Size of this community, as well as unpredictable subirrigation and/or surface flow <br />effectively limits its usefulness as pasture or hayfield. While the community serves as wildlife <br />habitat for residents of the RPE area, the adjacent North Fork of the Gunnison .provides a more <br />diverse and high quality wildlife habitat. <br />A small side slope area {<0.01 acre) on'the main slope of the RPE area was identified during the <br />vegetation sampling as differing in visually dominant tree species (Figure 2). This area represents a <br />seep from a bedrock outcrop or saturated surficial soil on the slope of the RPE azea. With a <br />generally reliable moisture source, this small azea supports plant species with high .moisture <br />requirements. At this area, mature Populus angustifolia (natmwleaf cottonwood) individuals are . <br />present.along:with Agrostis alba (redtop) and Salix sp. (willow). Vegetative characteristics and <br />parameter values aze similar to those of the relict oxbow wetland described above. Due to its small <br />size, this minor. community serves mainly as a source of cover and water for wildlife species <br />utilizing the immediate RPE azea. <br />A small inclusion {Q acres) of the Douglas fir-Utah juniper vegetation community is present on the <br />easternmost flank of the RPE azea. Within the 1tPE area this community is an association of mature <br />Pseudotsuga menziesii (Douglas fir) and Juniperus osteosperma. The topography of the area is <br />characterized by rocky terrain and moderate slopes. The vegetation. cotmunity is open and park- <br />like between the mature trees. It is hypothesized that this area, having shallower soils and more <br />surficia] sandstone fragments has allowed the shade intolerant Douglas fir to become established. <br />As the area has a more easterly aspect, the moisture regime may be slightly more xeric, explaining <br />the presence of Juniperus osteosperma. In any event, this vegetation community is not <br />chazacteristic of the RPE azea. <br />2.04-153 Revised Apri120P¢ PRlO <br />