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CLEARWATER <br /> G R O U P, I N C. <br /> Fn Bi rnn meita! Serairrs <br /> Clearwater agrees that a complete understanding of contamination distribution and <br /> mass is an integral element of remedial system design; however, continued debate <br /> over the exact mass of contaminants is not beneficial. It is not disputed that <br /> significant concentrations of residual petroleum hydrocarbons remain in the <br /> subsurface. However, pilot test results provide the most reliable data for design of <br /> an operational remedial system, as groundwater/soil vapor flows rates, influent <br /> hydrocarbon concentrations, and resulting zones of influence are empirically <br /> derived. Once the system is installed, it will likely operate until contaminant <br /> recovery rates are reduced to low levels regardless of what exact contaminant mass <br /> was estimatedduring the assessment phase. Suffice it to say that the actual mass of <br /> contamination is likely somewhere between the Clearwater estimate and PHS/EHD <br /> estimate, and that the remedial recommendation is appropriate for such site <br /> conditions. <br />` Remedial Action Plan <br /> Clearwater conducted a dual-phase vapor extraction test on RW-1 and soil vapor <br /> extraction tests on VW-1, VW-2, and VW-3. The tests conducted using these four <br /> wells provided empirical. data concerning achievable vapor flow and radii of <br /> influence. Based on these data, Clearwater predicted that an additional dual-phase <br /> i extraction well, located near MW-1, used in conjunction with those wells noted <br /> above, would be sufficient to exert vapor recovery influence across the lateral extent <br /> of soil contamination beneath the site (Figure 12 of Remedial Action Plan). The <br /> PHS/EHD noted that systems do not always perform according to theory and <br /> suggested that an additional vapor extraction well be incorporated into the <br /> conceptual design. It should be noted that empirical data is available for 80% of the <br /> proposed extraction points (RW-1, VW-1, VW-2, and VW-3). Although flow rate <br /> and radius of influence for proposed RW-2 are estimates, they are based on <br /> sufficient site specific data. If data collected during operation of the system as <br /> designed indicate an additional well appears necessary in the future, it would not be <br /> difficult to plumb it to remedial trench hardware. This sequential approach ensures <br /> against inefficient system overdesign. <br /> The PHS/EHD also expressed; concern [regarding "smearing" of separate-phase <br /> hydrocarbons (SPH) in the cone of depression resulting from groundwater <br /> extraction. It should be noted that this smeared interval will be aggressively targeted <br /> by coeval soil vapor extraction, and that Clearwater has proposed no sole <br /> groundwater extraction wells. All groundwater extraction points will also serve as <br /> vapor extraction points. Concern was also expressed regarding smearing of soluble- <br /> phase contamination as the water table is lowered within the pumping well. It <br /> should be noted that maximum drawdown within each pumping well is anticipated <br /> to be approximately 10 to 11 feet. It should be noted that groundwater beneath the <br /> site naturally fluctuates up to 7 feet annually, from 10 to 17 feet below grade. <br /> Considering that the vertical extent of groundwater contamination is probably at <br /> Ruiz.4491.W.DurhaniFerry.Tracy.CA 3 September 17,1996 <br /> r <br />