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11 February 2003 <br /> AGE_NC Project No. 98-0520 <br /> ' Page 5 of 21 <br /> ' Since initiation of groundwater monitoring in December 1999,groundwater elevations have ranged <br /> from approximately 13 to 19 feet above mean sea level. The ground water table underlying the site <br /> is generally in the form of a trough-like depression,with the base of the trough plunging northwest <br /> ' a low gradient of less than 0.01 ft/ft(Figure 7). <br /> Releases of petroleum hydrocarbons occurred from the on-site USTs. Once released to the <br /> ' subsurface, the contaminants migrated through the sandy Layer I to a vertical depth of <br /> approximately 20 feet bsg, at which point the contaminants encountered the less porous clayey silt <br /> of Layer 2 and began to migrate laterally as well as vertically;the direction of lateral migration Was <br /> ' dominantly towards the northwest, in the preferred ground water flow direction. <br /> Significant petroleum-hydrocarbon impact to soil in the vadose zone is present in borings B-2-20.25, <br /> ' B-4-20, MW-2-25 and MW-4-20, in the area.of the former USTs, and off-site well MW-9-20 <br /> (Table 2).TPH-g, TPH-d and TPH-rno are-present at maximum concentrations of 670 mg/kg(B-2- <br /> 20.25), 150 mg/kg(MW-9-20)and 120 mg/kg(B-2-20.25),respectively.Most of the contamination <br /> appeared to reside at the top of the clay layer, at approkimately 20 feet bsg. <br /> • 5.0. POTENTIAL IMPACT ONNEARBY SURTACE AND GROUND WATER <br /> Typically,'ground water would represent the migration medium for contaminants over significant <br /> ' horizontal distances. However, sites located in up-gradient or cross-gradient directions from the <br /> subject property are not likely to be negatively impacted by the subject property. In addition, first <br /> encountered ground water is not used for drinking or irrigation,,although all ground water in the <br /> ' State of California is considered to be of potential beneficial'use. <br /> 1 Drinking water at and near the site is supplied by the City of Manteca. The nearest city wells are <br /> located approximately 2,000 feet northeast of the site; based on the distance and cross-gradient <br /> ground water flow direction at the site,.it is unlikely for these wells to be contaminated by impacted <br /> ground water from the site. <br /> The nearest surface water features to the site are the San Joaquin River and Little John Creek.- <br /> located <br /> reek.located approximately 5 miles southwest and north, respectively, of the site. It is unlikely that <br /> impacted ground water at the site would represent a significant pollution threat to water in the San <br /> Joaquin River and Little John Creek, based upon their distances from the site. <br /> 6.0. SOIL REMEDIATION ALTERNATIVES <br /> ' Based on the distribution and concentrations of petroleum hydrocarbons in soil and ground water <br /> . on the subject site, and on site-specific conditions, AGE believes excavation and in-situ soil <br /> • <br /> Advanced CeoEnvironmental,Inc. <br />