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*4010, *-8104 <br /> Mr. Howard Hold <br /> October 6, 2004 <br /> Page 2 <br /> pressure,resistivity, and ultra violet induced fluorescence)to interpret the stratigraphic profile of <br /> each boring. When target sample depths are reached (based on the interpretation of the <br /> stratigraphic profile)below the depth of the water table, a push-type ground-water sampler with <br /> a sealed stainless steel screen section is pushed to the desired sampling interval. The sampler <br /> push rod is then retracted to expose the screen, allowing ground water to hydrostatically flow <br /> from the formation into the sampler(Gregg In-Situ, Inc.). When sampling is completed,the <br /> sampler is retrieved and the borehole continues to be advanced. The CPT technology encounters <br /> difficultly in advancing when gravel and cementation or hardpan are encountered. These <br /> conditions can bend and damage the CPT system. Water may be used to assist in the <br /> advancement of the borehole. Any fluids generated from the borehole advancement will be <br /> spread on the ground away from the drill site. <br /> Proposed CPT Locations <br /> Based on the historical record for ground-water flow directions and the estimated extent of <br /> ground-water quality impacts in the shallow and deep zones (LSCE, 2003), areas were identified <br /> for CPT locations in both the shallow and deep zones to characterize the lateral and vertical <br /> extent of chloride-impacted ground water. Each CPT boring will be advanced until field <br /> measurements of total dissolved solids (TDS) (field measurement of electrical conductivity (EC) <br /> will be multiplied by 0.66 to convert to an equivalent total dissolved solids concentration) <br /> approach the water quality protection standards(WQPS) for TDS. The WQPS for the shallow <br /> zone is 600 mg/L, and the WQPS for the deep zone is 460 mg/L. Historical plume boundary <br /> comparisons between TDS and chloride have been similar, therefore, field calculations of TDS <br /> concentrations which approach TDS WQPS will also be representative of chloride <br /> concentrations approaching WQPS. The proposed locations along with estimated depths for the <br /> CPT borings are presented below. <br /> While the CPT boring is being advanced, water quality samples will begin to be collected once <br /> the water table (approximately 110 to 115 feet below ground surface) is encountered. As the <br /> CPT boring is advanced to greater depths, ground water will be monitored for EC to estimate the <br /> extent of contamination. The target depths associated with each proposed boring below are only <br /> estimates and may change depending on the water quality measurements collected during the <br /> field investigation. <br /> Shallow CPT Locations <br /> • A minimum of two CPT borings located approximately 500 to 1,000 feet north to <br /> northwest of the north pond to depths of up to approximately 160 to 180 feet; <br /> • A minimum of two CPT borings located approximately 400 to 800 feet east to northeast <br /> of the northeastern corner of the north pond to depths of up to approximately 160 to 180 <br /> feet; <br />