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the contaminants were carried to the site by ground water flow. These aze the areas proposed to be <br />mined. <br />Given the known historical contaminant plume in this area, excavation activities associated with <br />removal of aggregate materials within the zone of water table fluctuation would produce mechanical <br />mixing that will remobilize (desportion) contaminants that had adsorbed on the subsurface alluvial <br />materials. This remobilization can produce an immediate threat to human health by ingestion of <br />contaminated drinking water supplies. The potential concentrations of desorbed contaminants are <br />dependent upon the original historical concentrations in the aquifer, the geomorphology of the <br />aquifer, and the grain size of particles in the aquifer, among other hydrogeologic characteristics. <br />The historical concentration of contaminants in the shallow, alluvial aquifer is unknown as the <br />ground water plume was not investigated until 1974. Chemical production and waste disposal at the <br />RMA had continued for 30 years prior. Recent mapping by the U.S. Geological Survey (USGS), <br />Hydrologic Investigations Atlas HA-736 has identified a number of paleo-channels associated with <br />the South Platte River system. These channels of thicker deposits of alluvial materials would <br />represent preferential flow paths through the alluvial aquifer, where contaminants might be expected <br />to "concentrate" in their absorbed phase. Figure 2 in HA-736 identifies a channel of thicker alluvial <br />material that trends southwest-northeast through the center of section 16, the section containing the <br />applicant's Jeronimus property and my property. Alluvial thickness of 85 and 60 feet aze <br />documented on the driller's logs of my two alluvial wells. A copy of the appropriate portion of that <br />figure is reproduced and enclosed as Attachment 6. Lastly, the grain size of the alluvial material will <br />influence the amount of adsorption. Smaller grains such as silts and clays have a greater tendency to <br />absorb contaminants. According to the USGS, the youngest alluvium in the area consists of Piney <br />Creek and post-Piney Creek Alluvium composed of gravel, sand, silt, and clay. Due to the unknown <br />distribution of these materials in the subsurface, the potential concentrations of desorbed <br />contaminants may vary greatly. <br />Upon the recommendation of the Water Quality Control Division, I request that the Division <br />of Minerals and Geology request asste-specific review of the applicant's discharge permit from <br />the Division for consideration of past, current, and potential future ground-water <br />contamination from organic chemicals attributed to historical waste disposal practices at the <br />Rocky Mountain Arsenal. Water quality monitoring, on a minimum quarterly basis, of semi- <br />volatile and volatile organic compounds including DIMP sbould be required from mine <br />perimeter monitoring wells, all ouNalls, and process water effluent. Ezceedance of regulatory <br />ground or surface water standards should require implementation of mitigation measures. <br />3. Injury to Decreed Water Rights <br />The residence structure and outbuilding on my property are located approximately 40-feet east of the <br />Amendment No.l Area boundary. The storage barn is directly adjacent to the property boundary. <br />One bedrock aquifer well (permit no. 2455), permitted for domestic water supply, and one alluvial <br />aquifer well (permit no. 2456), permitted for lawn irrigation, are housed within the same vault <br />structure and located approximately 30-feet east of the property boundary. Our field irrigation well, <br />permit no. 32883, is an alluvial aquifer well that was adjudicated December 31, 1972 and is located <br />approximately 25 feet east of the property line. <br />