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Hydraulic conductivity values calculated from the recovery testing are summarized below. <br /> Ff f_rr <br /> Well ID Hydraulic Conductivity Flow Velocity <br /> ft/yr <br /> cm/sec ft/sec <br /> MW-1 6.56 x 104 2.15 x 10-' 1.16 <br /> MW-2 7.17 x 10-3 2.35 x 10-4 12.72 <br /> MW-3 1.14 x 104 3.74 x 10-" 0.20 <br /> MW-4 7.94 x 104 2.61 x 10 1.41 <br /> MW-5 8.14 x 104 2.67 x 105 1.44 <br /> MW-6 7.18 x 10-' 2"36 x 10.5 1.27 <br /> MW-8 6.04 x 10' 1.98 x 10"S 1.07 <br /> MW-9 8.29 x 10-' 2.72 x 10 1.47 <br /> MW-10 2.03 x 10"3 6.66 x 10'' 3.60 <br /> MW-11 7.60 x 10"5 2.49 x 10-6 0.13 <br /> MW-12 3.32 x 10"3 1.09 x 10-4 5.89 <br /> { Geometric 7.79 x 10' 2.55 x 10" 1.38 <br /> Mean <br /> It is noted that the calculated hydraulic conductivity values reflect the aggregate permeability <br /> of the saturated screened interval of a particular well. <br /> 6.0 SITE GEOLOGY AND HYDROGEOLOGY <br /> Soils encountered while drilling during this and previous investigations generally consisted of <br /> sandy silt to silty sand to depths of 14 to 18 feet below grade, underlain by a 0.5- to 2-foot-thick <br /> silty clay to clayey silt layer. Below the clay and silt, sand with varying silt content was <br /> encountered to the total depth of the borings at 20 to 25 feet below grade. <br /> Nearly water-saturated soil was encountered during drilling and sampling at approximately 7 <br /> feet below grade,with the depth to groundwater measured in the monitoring wells at <br /> approximately 8 feet below grade. Groundwater elevations measured on September 3, 1998 <br /> were used to develop the groundwater potentiometric surface map shown on Figure 3. The <br /> groundwater gradient as calculated from these measurements is approximately 0.0006 foot per <br /> foot in a general southwesterly direction across the site. Seasonal fluctuation of the <br /> groundwater table in selected onsite wells is shown on Figure 5. <br /> 9 <br />