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Atlantic Richfield Company <br /> ARCO 4932 16 E Harding Way,Stockton,CA June 7 2002 <br /> • - were monitored in wells EW-1, MW-1, MW-4, MW-6, and MW-7 Groundwater levels <br /> were recorded for approximately 24 hours, until the data loggers were removed from the <br /> wells on April 4, 2002 Water level data compiled throughout aquifer testing was <br /> downloaded from the data-loggers onto a computer, and was later used to determine <br /> ' hydraulic properties of the aquifer beneath the site <br /> Data Analysis <br /> ' Drawdown data from observation wells MW-1 MW-4, MW-6, and MW-7 were <br /> analyzed using the Cooper and Jacob (1946) method applied using the AQTESOLV <br /> ' software groundwater modeling program The analyzed data were selected after <br /> borehole storage effects were considered negligible approximately 115 minutes after <br /> pumping began (Hargis, 1979) Groundwater recovery data from extraction well EW-1 <br /> ' and observation wells MW-1,MW-4, and MW-7 were also analyzed using the Theis <br /> (1935) method of plotting the recovery water levels versus the time that pumping <br /> commenced/time that pumping was ceased (tit') on semi-log paper Results of the <br /> ' analysis of drawdown data from wells MW-1, MW-4, MW-6,and MW-7 indicated a <br /> transmissivity (T) ranging from 1,200 to 5,400 gallons per day per foot (gpd/ft) The Ts <br /> ' from extraction well EW-1 and observation wells MW-1, MW-4, and MW-7 were also <br /> calculated using the straight-line method described by Theis (1935), which analyzes the <br /> late-time recovery water The results of the groundwater recovery data analysis <br /> indicated Ts ranging from 1,400 to 11,000 gpd/ft The geometric mean of the T from 7, <br /> analysis of the drawdown and recovery data is 3,600 gpd/ft The hydraulic conductivity <br /> (K) was calculated by dividing the T at each well by its respective aquifer thickness, <br /> ' which ranged from 16 7 feet in well EW-1 to 10 95 feet in well MW-7 The calculated <br /> Ks ranged from 0 005 centimeter per second (cm/sec) in EW-1 to 0 046 cm/sec in MW- <br /> 7 The geometric mean for K was calculated at 0 014 cm/sec This is consistent with <br /> the silts and sands described in the saturated zone on the boring logs (Attachment B) <br /> Storativity (S) of the aquifer can be calculated from analysis of the observation well <br /> ' data only S ranged from 0 02 to 0 03, with a geometric mean calculated at 0 03 The S <br /> values are typical of a semi-confined aquifer system A summary of hydraulic <br /> properties determined from aquifer testing is presented in Table 7 <br /> Assuming that semi-confined or confined conditions may exist across the site at depths <br /> beyond 90 feet bgs, based on soils encountered in deep soil borings SB-1 and SB-2, and <br /> ' the boring for deep well DMW-1, a capture zone for pumping well EW-1 was calculated <br /> using the Javandel and Tsang(1986) method According to Gorelick et a] (1993), the <br /> Javandel and Tsang (9186) method may be applied at sites with semi-confined <br /> rconditions based on the following " semi-confined conditions seem to indicate that <br /> the delayed yield effects from gravity drainage are insignificant Confined-aquifer <br /> ' hydraulics can be applied with reasonable confidence in such cases " Using a discharge <br /> rate of 0 59 ft/min (weighted average of pumping rates recorded during the constant- <br /> rate pumping test), an average hydraulic gradient of 0 009 ft/ft calculated from all <br /> ' I 1ARCO149321ReportslAsmt&Aq&TstRpt doe <br />