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I� <br /> v , <br /> A S S O C I A T E S I NC . <br /> probe capable of measuring with an accuracy of 11100 of a foot. Groundwater elevation data are <br /> presented in Table 3. <br /> =' 2.5 Groundwater Sampling and Analysis <br /> t="! On March 11, 1999, groundwater samples were collected from wells MW-1 through MW-6. The <br /> } samples were collected after purging a minimum of three well volumes and stabilization of electric <br /> conductivity, pH, and temperature. Field development/purge logs are presented in Appendix C. <br /> G <br /> Subsequent to purging, groundwater was sampled and transferred to appropriate sample <br /> containers, using clean, disposable bailers with bottom emptying devices to reduce volatilization. <br /> Sample containers were then labeled with sample identification, placed on ice, and shipped under <br /> chain-of-custody to Sequoia Analytical. <br /> The groundwater samples from wells MW-1 through MW-6 were analyzed by Sequoia Analytical <br /> for TPHg, BTEX, and methyl tertiary butyl ether (MTBE) by EPA methods 801518020. Samples <br /> from wells MW-4, MW-5, and MW-6 were also analyzed for oxygenate fuel additives by EPA <br /> <: method 8260. Groundwater analytical results are summarized in Table 2, and laboratory data <br /> sheets are presented in Appendix D. <br /> 3.0 SUBSURFACE CONDITIONS <br /> 3.1 GeoloQy <br /> == Soil in borings MW-4, MW-5, and MW-6 generally consisted of lean clay from the ground <br /> surface to depths between 26 to 28 feet bgs, the maximum depth explored. Each boring had sand <br /> with varying amount of silt and/or gravel from depths between 11.5 to 15 feet bgs and 16.5 to 20 <br /> k ' feet bgs. Boring MW-5 also had poorly graded sand from 10.5 to 11 feet bgs and sandy clay from <br /> between 21.5 to 25 feet bgs and 26 feet bgs, the maximum depth explored. <br /> 3.2 Hydro-geology <br /> Water level measurements were collected from wells MW1 through MW6 on March 11, 1999. <br /> Water levels ranged from 6.93 to 8.55 feet below the tops of the well casing elevations. Water <br /> eet since January 1999. The water level data were used <br /> levels have increased an average of 0.28 f <br /> r`. to develop the groundwater elevation contour map (Figure 3). Assuming that horizontal isotropic <br /> conditions prevail, groundwater in the uppermost aquifer beneath the site flowed towards the <br /> ;==3 north-northeast. The average hydraulic gradient on March 11, 1999 was calculated to be 0.002 <br /> ft/ft or approximately 11 ft/mile. These results are consistent with results of previous monitoring <br /> events. A summary of groundwater monitoring data is presented in Table 3. <br /> w:113099\reports%sumwel.doc 4 <br /> F:.'f <br />