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AN <br /> &MA <br /> W- 1 all <br /> �c i <br /> , S <br /> 4':S <br /> PROJECT 02510.01 January :31, 1991 <br /> sampled through a 1/4-inch Teflon sample line that was connectea to a <br /> stainless steel , air tight, well head fitting. Use of Teflon tubing <br /> minimizes sample loss through adsorption and the possibility of distorted <br /> results from a sample line contaminated by a previous analysis. <br /> Leak checks were performed on the sample line before the analysis. <br /> Filters were used extensively throughout the system to remove foreign <br /> material from the sample pathway. The sample line was connected to a <br /> diaphragm pump located in a mobile laboratory. The extracted soil gas <br /> was analyzed using a Beckman Model 400 Total hydrocarbon Analyzer <br /> equipped with a Flame Ionization Detector (FID). The Beckman Model 400 <br /> was calibrated using certified standards of propane in nitrogen. The <br /> instrument was recalibrated periodically throughout the day using <br /> certified standards. <br /> Depth to groundwater was measured at monitoring wells tested during the <br /> Soil Gas Survey using an electronic water level indicator, <br /> Performance Test <br /> The Performance Test was conducted January 30, 1991. A portable skid <br /> containing a vacuum pump, flow meters, and vacuum gauges was used on <br /> site. A vacuum line was connected to an existing ground water monitoring <br /> well to create an extraction point. Five monitoring wells (MW-5, MW-7, <br /> MW-io, MW-13, and MW-19) were used as extraction points (Figure 1). <br /> Each <br /> extraction point was tested for a period of 20 minutes. <br /> The information from the Performance Test was used to determine the <br /> capture radius, the distance at which the pressure differential created <br /> by a vacuum pump is measured, in the lateral and vertical planes. The <br /> capture radius was noted by recording the vacuum gradient in neighboring <br /> wells in inches of water ("H20). This procedure was performed at various <br /> flow rates at several of the wells. The detection limit for the vacuum <br /> gradient was 0.005" H0. The effluent from the extraction points was <br /> routed through two cyOinders in series, each containing 200 pounds of <br /> vapor phase activated carbon. The carbon adsorbs organic vapors from the <br /> extraction air stream, preventing discharge of contaminants into the <br /> atmosphere. <br /> RESULTS <br /> Soil Gas Survey <br /> TVH concentrations recorded at the wells tested are given in Tab .e- <br /> The highest TVH concentration, 11,550 parts per million (ppm), was <br /> recorded at monitoring well MW-2 located east of the existing underground <br /> fuel storage tanks and south of the station building. The next highest <br /> „r <br />