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,k <br /> S E C ® R <br /> t <br /> F <br /> Conceptual Site Model <br /> March 24, 2004 <br /> Page 21 <br /> logarithmic diffusion rate Because concentrations typically decrease exponentially with <br /> respect to distance, a linear relationship is likely conservative, <br /> To conservatively estimate the cross sectional area a saturated thickness of 20 feet and <br /> cross sectional width of 60 feet was assumed, <br /> • Based on historical records a hydraulic conductivity of 0 0411 cm/s was assumed, <br /> • A historical high groundwater gradient of 0 02 ft/ft was assumed (Figure 6), <br /> a <br /> • A conservative water supply well pumping rate of 35 gallons per minute was assumed <br /> Based on mass balance calculations and observed hydrocarbon concentrations in down gradient <br /> wells constituent concentrations migrating offsite would be reduced below secondary maximum <br /> contaminant levels (MCLs) for drinking water and are not likely to impact the five offsite water supply <br /> wells discussed in section 7 0 <br /> .x <br /> 9 0 SITE ASSESSMENT WORK PLAN <br /> The objective of this site assessment work plan is to determine the lateral and vertical extent of 4 <br /> impacts as stated during a regulatory meeting with SJEHD g� <br /> This work plan describes the field work and data collection process for these site assessment <br /> activities <br /> 9.1 Scope of Assessment <br /> This site assessment is framed by the existing facility property boundaries, bounded by commercial <br /> properties identified to have had a potential release to the environment to the west, north, and east <br /> A city of Stockton municipal yard is located to the southwest West Charter Way and South Lincoln <br /> Street are located immediately to the north and east, respectively <br /> b <br /> Based on historical data and current groundwater monitoring data the existing monitoring wells have <br /> been identified as having submerged screens Therefore, the existing three groundwater monitoring <br /> wells will be replaced and removed from the monitoring and sampling plan The locations of the s <br /> proposed monitoring wells are presented on Figure 2 An alternative use for MW-1, MW-2, and MW- <br /> 3 will be evaluated and presented in a future report -N^ 1Hwti -S a& 3�'fssI Sc Y-f.56, r^ a 5,.>e ' <br /> rw� s e k <br /> Results of previous assessment activities indicate petroleum hydrocarbons have not been vertically <br /> defined in groundwater beneath the Site and soil appears to be defined along the northwestern <br /> property boundary Determining the extent of impacted sod and groundwater laterally beneath the <br /> Site is problematic due to the following factors <br /> k <br /> • Additional primary sources of impacted sod and groundwater located immediately down <br /> and cross gradient, -u,l, F{,5 w ?JuS\t -1 <br /> r� <br /> 11Chevron%920331REPORTSICSMICSM 92033(REV B)doc <br />