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7 <br /> . were subsequently downloaded to a portable field computer Water levels were measured <br /> periodically in all of the other monitoring wells during the pumping test <br /> The test consisted of three pumping steps plus recovery Figure 4 showy the drawdown <br /> versus time in the pumping well. TEX-1 Each pumping step lasted for 2 hours During the first <br /> step, the average pumping rate was about 7 5 gallons per minute (gpm) The flow rate was <br /> increased to 10 7 gpm for the second step, and subsequently increased again to 16 7 gpm for the <br /> third step At the end of the 6-hour test. approximately 5 feet of drawdown was measured in <br /> TEX-1 Drawdowns, as measured in the observation wells, were insignificant Specifically, a <br /> drawdown of approximately 0 1 foot was measured in ATR-4 and 0 03 feet was measured in <br /> ATR-2 There was no measurable drawdown in the other monitoring wells <br /> In order to determine the horizontal conductivity of the saturated zone around TEX-1, the <br /> data collected from TEX-1 were analyzed by the generalized straight-line method of Cooper and <br /> Jacob modified for step-type variation of the discharge rate (1983)1 The aquifer is thought to <br /> be anisotropic and heterogeneous and hydraulic conductivity values will vary within the aquifer <br /> Analysis of these data are shown on Figure 5 The two parallel lines drawn through the data <br /> have the same slope from which the transmissivity was calculated The average transmissivity <br /> was calculated to be about 1,300 square feet per day (sq ft/day), assuming the saturated thickness <br /> of the aquifer to be about 23 feet The average horizontal hydraulic conductivity is about <br /> 60 ft/day Due to the heterogeneity of the aquifer and the presence of low permeable layers of <br />. silt, this hydraulic conductivity is probably accurate to an order of magnitude and represents the <br /> higher end Thus, the aquifer around TEX-1 is thought to have a hydraulic conductivity <br /> between 6 and 60 ft/day <br /> Groundwater Extraction (Optional) <br /> The decision as to whether or not groundwater extraction is needed to remediate the site will <br /> be based on data collected during the fust 6 months to 1 year of sparging and vapor extraction <br /> If required, groundwater may be extracted from TEX-1 and from monitoring wells ATR-2, <br /> ATR-4, and ATR-5 The purposes of pumping from these wells will be to <br /> 1 Keep the water table from rising as a result of vapor extraction so that vapors can be <br /> withdrawn from the hydrocarbon-affected soil 1 to 2 feet above the current water table <br /> 2 Lower the water table in order to expose more vadose zone. <br /> 3 Recover and treat hydrocarbon-affected groundwater from these wells <br /> Pumping rates at wells ATR-2, ATR-4, and ATR-5 are expected to be on the order of 0 to <br /> 2 gpm, and at TEX-1, 10 to 15 gpm The actual pumping rates will vary depending on water <br /> elevations in specific wells and the actual performance of TEX-1 <br /> 1Kruseman, G P , DeRidder, N A , 1983, Analysis and Evaluation of Pumping Test Data, <br /> pg 38, International Institute for Land Reclamation and Improvement ILRI, Wageningen, The <br /> Netherlands, 200 p <br /> 7403,1ZU0RT9\2EMEDATN PLN <br />