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. SITE CONCEPTUAL MODEL <br /> Former Texaco Service Station/ARCO <br /> 440 West Charter Way, Stockton, California <br /> 2 7 MTBE Plume Stability and MTBE concentration trends are stable or declining in the wells associated <br /> Concentration Trends with this site The only exception to this is well MW-14 located offsite to the <br /> southwest It appears that MTBE levels in this well are likely due to an offsite <br /> source <br /> 2 8 Groundwater Flow Direction, Since 1992, depth to water beneath the subject site has ranged from 17 to 43 <br /> Depth Trends and Gradient fbg in the monitoring wells The groundwater flow direction is typically toward <br /> Trends the east/southeast with the groundwater gradient varying around 0 001 to <br /> 0 007 Since 1992 the groundwater elevation beneath the site has risen <br /> approximately 20 feet This groundwater rise peaked in 1999 and is now <br /> slowly declining The groundwater elevation has decreased approximately 5 <br /> feet since 1999 A graph of historical (1992 to 2003) water levels in well MW- <br /> 1 is included in Attachment 2 <br /> 2 9 Stratigraphy and Hydrogeology The site is underlain by layers of clay (CL), silt (ML), clayey sand (SC), silty <br /> sand (SM), and sand (SP & SW) The predominant soil type beneath the site <br /> is fine grained sods (silt and clay) There are several coarse grained layers <br /> (sand) beneath the site that appear to be laterally continuous These coarse <br /> grained layers occur at approximate depths of 80 and 120 fbg and vary in <br /> thickness across the site Boring logs are included in Attachment 3 and site <br /> cross sections are included in Attachment 4 <br /> I <br /> 2 10 Preferential Pathways Analysis Since the depth to groundwater is deeper (>= 17 fbg) underground utilities <br /> are buried, it is highly unlikely there are preferential pathways in the <br /> subsurface as a result of underground utilities No natural preferential <br /> pathways (buried stream channels, etc) have been identified in the <br /> subsurface It appears contaminant transport is occurring through the <br /> naturally deposited sediments beneath the site <br /> 2 11 Other Pertinent Issues None <br /> 3 Remediation Status <br /> 31 Remedial Actions Taken Interim remediation, in the form of sod vapor extraction (SVE) using a thermo <br /> oxider, was performed in wells VEW-1 through VEW-4 from January 1996 to <br /> March 1998 Approximately 6,256 pounds of TPHg were removed from <br /> VEW-1 through VEW-4 <br /> 3 2 Area Remediated The vicinity of VEW-1 through VEW-4 <br /> 3 3 Remediation Effectiveness Influent concentrations were reduced from a high of 9,700 mg/m3 (February <br /> 1996) to <10 mg/m3 March 1998 <br /> 4 Well and Sensitive Receptor <br /> Surve <br /> 41 Designated Beneficial Water Existing and potential beneficial uses include municipal and domestic water <br /> Use supply, agricultural supply, industrial service supply, and industrial process <br /> supply(CVRWQCB Basin Plan) <br /> 4 21 Shallow Groundwater Use INone identified in the vicinity of the site <br /> 4 31 Deep Groundwater Use I None identified in the vicinity of the site <br /> 1399 Page 2 of 3 Date Modified 11/2/2004 <br />