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<br /> <br /> 7 <br /> <br />These general water quality relationships are not as pronounced for the baseline Colorado River <br />surface water monitoring data, due to the many influences from the extremely large Colorado <br />River drainage basin. <br /> <br />Ground Water <br /> <br />The occurrence of ground water in the permit area and adjacent area is controlled mostly by <br />irrigation water and the Colorado River. Alluvial groundwater in the permit area occurs in river <br />alluvium that lies over Mancos shale. The river alluvium is well-graded sandy gravel that was <br />deposited in terraces. These terraces are areas of relatively flat land (located on either side of the <br />flood plain) which are above the flood plain because of river erosion over the years down cutting <br />below the level of the terraces. <br /> <br />Along the banks of the Colorado River, the alluvium is directly impacted by flows in the river. <br />The alluvial water within the permit boundary appears to be a result of flow from upland irrigation. <br />The three proposed sediment ponds will be lined to prevent seepage of water, seepage of dissolved <br />constituents, and mobilization of contaminants in pond substrates. The pond linings are required <br />by USFWS conservation measures. Underlying the alluvium is the Mancos Shale, a shallow <br />marine deposit comprised predominantly of marine shale, mudstone and claystone, with <br />interbedded sandstone, siltstone, and limestone. Overall, the Mancos Shale restricts the <br />movement of groundwater and generally acts as an aquitard and confining unit in the regional <br />groundwater flow system. <br /> <br />Rule 2.04.7(1)(a) requires investigation and description of each aquifer above, within and, if <br />potentially impacted, below the lowest coal seam to be mined. Since the permit application is <br />solely for a unit train loadout, no mining will occur and therefore no potential exists to impact <br />bedrock groundwater. No investigation of bedrock groundwater was performed for the loadout. <br />Groundwater that may occur in isolated interbedded sandstones within the underlying Mancos <br />will not be required to be monitored as a result of Loadout operations. <br /> <br />The land east of Reed Wash is a remnant of the former petroleum refinery operations. The site <br />and adjacent lands were part of refinery operations that were conducted by the American <br />Gilsonite Company beginning in 1957. Monitoring wells were installed in 1981 by Gary <br />Refining Company. The wells encountered 15 to 23 feet of material that was described as silty <br />clay "slope wash.” Underlying the silty clay is between 19 and 25 feet of the river alluvium , <br />which consists of poorly- to well-sorted sand and sandy gravel. The Mancos Shale was <br />encountered in all boreholes, ranging in depth from 34 to 48 feet. <br /> <br />Three of the Gary Refining Company monitoring wells were selected for use by CAM for its <br />baseline ground water monitoring (RW-1, RW-3 and RW-4). A monitoring well installed for a <br />nearby acid sludge landfill was selected as a fourth monitoring well. This monitoring well, RW- <br />2, is located northeast of the acid sludge landfill. See Map 8, Hydrologic Monitoring Location <br />Map, in the PAP for the location of these monitoring wells. <br /> <br />Alluvial monitoring wells RW-1 and RW-2 are located within the permit boundary. RW-2 is