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CAMBR A <br /> Table 1 Site Conceptual Model,Shell-branded Service Station,2494 East Fremont Street,Stockton,California <br /> 2 5 BTEX Plume Stability and BTEX concentrations are showing a stable or decreasing trend in well S- <br /> Concentration Trends i Wells S-2, S-3, and S-4 typically do not contain BTEX and therefore <br /> cannot be used for trend analysis Deep wells S-2-82, S-3-84, and 5-4- <br /> 83 BTEX concentrations are typically near or below the detection limits <br /> Deep well 5-1-85 contains BTEX levels that fluctuate some, but generally <br /> show a declining trend <br /> 2 6 Groundwater Definition Status MTBE has been detected (by EPA Method 8260) in groundwater sample <br /> (oxygenates and lead from wells at this site at concentrations no higher than 8 5 ppb The only <br /> scavengers) exception to this is well S-6 which has contained MTBE as high as 100 <br /> ppb MTBE is sufficiently defined considering the low detections and the <br /> existing well network DIPE has been detected in groundwater samples <br /> from the wells at concentrations as high as 18 ppb The existing well <br /> network should be sufficient for delineation of DIPS in groundwater <br /> Ethanol,TBA, ETBE, and TAME have not been detected in groundwater <br /> samples collected from the site wells Methanol has been detected once <br /> in two wells at concentrations of 4,300 and 5,600 ppb Subsequent <br /> methanol sampling has shown that methanol delineation appears to be <br /> complete EDB has been detected only in well S-1 at concentrations as <br /> high as 350 ppb Grab groundwater samples collected from borings <br /> drilled at the site have not contained EDB, which demonstrates that EDB <br /> is not a widespread problem at this site <br /> 1,2-DCA has been detected in each site well at concentrations as high as <br /> 600 ppb CPT borings SB-20 through SB-25 provide some lateral <br /> delineation of 1,2-DCA at various depth intervals (Figure 2 of the main <br /> report) In general 1,2-DCA concentrations decline with distance away <br /> from the site and also decline with depth <br /> 2 7 Oxygenate and Lead MTBE concentrations appear to be stable, which would be expected as <br /> Scavenger Plume Stability and MTBE has been removed from the fuel that is sold at the site(since <br /> Concentration Trends January2003) DIPS concentrations appear to be stable or decreasing <br /> Ethanol,TBA, ETBE, and TAME have not been detected in groundwater <br /> samples collected from the site wells Methanol has been detected once <br /> in two wells at concentrations of 4,300 and 5,600 ppb EDB detections <br /> appear to be declining 1,2-DCA concentrations appear to be relatively <br /> stable or showing a declining trend <br /> 2 8 Groundwater Flow Direction, Shallow groundwater flow direction varies at the site, but is predominantly <br /> Depth Trends and Gradient toward south-southeast The gradient in the shallow zone ranges from <br /> Trends 0 0002 to 0 005 Depth to water (in the shallow groundwater zone), has <br /> ranged from 46 to 55 feet below grade The groundwater flow direction in <br /> the deep zone is typically toward the southeast Depth to water in the <br /> deep groundwater zone has ranged from approximately 51 to 55 feet <br /> below grade The vertical gradient between the shallow and deep <br /> groundwater zones appears to be neutral (i e , groundwater elevation in <br /> oil I the shallow zone is generally the same as it is in the deep zone) <br /> 0955 Page 2 0£5 Date Modified 12/1612004 <br />