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<br /> <br /> 22 <br /> <br />CAM prepared SEDCAD hydrology demonstrations that show that the silt fence <br />protecting the stream buffer zones can treat runoff to NPDES standards for settleable <br />solids. The SEDCAD demonstrations can be found in Exhibit 9 of the permit <br />application. <br /> <br /> K. Probable Hydrologic Consequences <br /> <br />The operator's discussion of the Probable Hydrologic Consequences (PHC) is <br />presented in Section 2.05.6(3)(b)(iii) of the permit application. Concerning surface <br />water, CAM presents their assessment that the waters of the Colorado River, Reed <br />Wash and the Loma Drain will not be adversely affected by operations at the Loadout. <br /> <br />Since the three sediment ponds are total containment ponds and the pond water will <br />be removed from the ponds and disposed of at an approved disposal facility, CAM <br />concluded that Loadout’s operations will not adversely affect the surface water regime <br />and may even improve the water quality in Reed Wash. <br /> <br />CAM concluded that sediment ponds will improve the quality of the surface water <br />flowing through and out of the proposed permit area and adjacent area because <br />sediment and water removed from the ponds will be disposed of at an approved <br />disposal facility. This will reduce the amount of suspended solids and reduce the <br />possibility of flood hazards by retaining runoff during storm events. <br /> <br />With regard to groundwater, CAM provided a PHC analysis for the alluvial <br />groundwater only. Bedrock groundwater will not be affected by the Loadout’s <br />operations. Alluvial groundwater in the permit area occurs in river alluvium that lies <br />over Mancos shale. It is unlikely that the groundwater within the permit area is <br />directly related to the Colorado River. It is possible that groundwater beneath the <br />property may in part be the result of irrigation in the upland areas, using water from <br />up river diversions. The water quality of the alluvial groundwater is relatively poor. <br />The alluvial groundwater is predominantly a calcium-sodium-sulfate water, with <br />elevated iron and manganese. Total dissolved solids range from 5,800 to 8,800 mg/L, <br />and there are no domestic or irrigation wells located immediately downgradient of the <br />permit and adjacent areas. Soils at the surface are described as silty-clay with low <br />permeability. <br /> <br />CAM analyzed infiltration from surface water runoff to shallow alluvial groundwater. <br />CAM concluded that in clayey soils, percolation is slow and most water is held at <br />shallow depths, where it can be lost to evapotranspiration. Intense precipitation <br />produces rapid surface runoff and low percolation. Combining this with the semi-arid <br />climate of the Grand Valley that possesses very high evapotranspiration rates should <br />allow runoff from the loadout to occur without impacting alluvial groundwater, as <br />most runoff water will be lost to evapotranspiration before it can infiltrate the alluvial <br />groundwater. <br />