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1. INTRODUCTION <br /> Exxon Retail Site (RS) 7-0137 is located at 1605 South El Dorado Street, Stockton, California, <br /> on the southwest corner of Second and South El Dorado streets The site is an active service <br /> station that has three double-walled fiberglass gasoline underground storage tanks (USTs) The <br /> site currently contains seven groundwater monitoring wells (MW I—MW7) and two vapor <br /> extraction wells (VEWI and VEW2) The seven groundwater monitoring wells (Figure 1) are <br />' sampled quarterly <br /> Groundwater sampling at Exxon RS 7-0137 has been conducted regularly since 1992 A soil <br /> e vapor extraction system operated at the site from November 1995 to March 1996, which <br /> extracted soil vapor through five wells (VEW 1, VEW2, MW2, MW3, and MW5) and abated the <br /> petroleum hydrocarbons with a catalytic oxidizer unit The catalytic oxidizer unit was removed <br /> in March 1996, following a decline in the concentrations of extracted hydrocarbon vapors <br /> /On21 January 1997, the seven groundwater monitoring wells were purged and sampled <br /> Samples were analyzed for Total Petroleum Hydrocarbons as gasoline (TPH-g) and for benzene, <br /> toluene, ethylbenzene, and total xylenes (BTEX) <br /> 2. SUMMARY OF RESULTS <br /> The depth to water in each well was measured prior to purging and sampling Liquid-phase <br /> hydrocarbons (LPH) were not detected in any of the wells Groundwater elevations at the site <br /> ranged from 23 56 to 20 49 feet below mean sea level Groundwater elevations have increased <br /> an average of 2 4 feet since the previous gauging on 16 October 1996 The monitoring wells at <br /> the site were constructed at a time when the water table was more than 10 feet lower than it is <br /> currently Monitoring wells MW1, MW2, MW3, and MW6 are screened from 35 to 55 feet <br /> below the surface, and MW4, MW5, and MW7 are screened from 40 to 60 feet below the <br /> surface Table 1 presents monitoring well construction details, and Appendix A presents well <br /> construction detail reports Table 2 shows that the depth to the water table on 21 January 1997 <br />' ranged from 32 10 to 34 36 feet Therefore, none of the wells were screened across the water <br /> table on that date In order to estimate the groundwater gradient and flow direction, we Eave <br />' prepared a water table contour map (Figure 1) using the following wells screened near the water <br /> table MW 1, MW2, and MW3 The flow direction based on data from these wells was toward <br /> the southeast at an approximate gradient of 0 004 Gauging data and calculated groundwater <br /> elevations from 21 January 1997 are presented in boldface type in Table 2, along with previous <br /> gauging data Field documents are included as Appendix B <br /> 1 After the depths to water were measured, each groundwater monitoring well was purged with a <br /> 2-inch PVC pipe attached to a vacuum pump until at least 3 casing volumes of groundwater were <br /> removed from it Samples were collected with factory-cleaned disposable polyethylene bailers <br /> The samples were poured into 40 ml glass VOA vials, which were then preserved in an ice-filled <br /> cooler A field-prepared sampling equipment rinse blank and a laboratory-prepared trip blank <br /> were stored and transported in the cooler with the groundwater samples The samples were <br /> handled and transported under chain of custody <br /> ' WP61 70137 Q197 TX 2 l <br />