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Work Plan for Groundwater Monitoring Well Installation, <br /> Soil Gas and Groundwater Investigation, <br /> and Groundwater Monitoring <br /> Army Aviation Support Facility, Stockton, California <br /> 2.4 MARCH 2008 SITE INVESTIGATION <br /> The site investigation conducted by URS in March 2008 included the collection of soil and grab <br /> groundwater samples from twelve hollow-stem auger (HSA) borings (B-3 through B-14). These <br /> samples were analyzed by both on-site and off-site laboratories. Sampling locations for the <br /> March 2008 investigation are indicated in Figure 3. Soil and grab groundwater samples were <br /> analyzed for TPH-g, TPH-d, VOCs, and BTEX compounds by USEPA Method 8260B, and lead <br /> by USEPA Method 6010B. Lead was detected in soil samples from all 12 borings, but below its <br /> PRG of 150 mg/kg. No VOC or BTEX compounds were reported in any soil samples. The only <br /> boring reporting petroleum hydrocarbon detection above action levels (Tri-Regional <br /> Board, 1990) was B-9, which is located at the southern portion of the 20,000-gallon USTs <br /> excavation (Figure 3). Reported diesel concentrations in B-9 were 1,840 mg/kg and 156 mg/kg <br /> at depths of 30 and 35 feet bgs, respectively. Diesel was not detected in any other borings <br /> (north, northeast, or southeast), and the URS report concluded that diesel in soil had been <br /> delineated. <br /> Grab groundwater samples were collected from each boring between approximately 38.5 feet <br /> and 40 feet bgs, corresponding to first groundwater encountered. Contaminants in groundwater <br /> exceeding respective MCLs were benzene in borings B-5 (6.0 pg/L) and B-9 (1.5 pg/L), carbon <br /> tetrachloride (CT) in boring B-9 (16 pg/L), TCE in boring B-13 (8.3 pg/L), and cis-1,2- <br /> dichloroethene (cis-1,2-DCE) in boring B-9 (18 pg/L). TPH-g was detected in borings B-4 and <br /> B-5, adjacent to the former 5,000-gallon USTs, at concentrations of 740 pg/L and 410 pg/L, <br /> respectively. TPH-d was only detected in boring B-9, at a concentration of 11,000 pg/L. <br /> Petroleum-related contaminants in groundwater were found generally only in areas in the <br /> immediate vicinity of the former USTs. Likewise, contaminants commonly found in solvents and <br /> degreasers (tetrachloroethylene [PCE], CT, TCE, and cis-1,2-DCE) were detected in <br /> groundwater samples in the southern portion of the site, generally upgradient from the former <br /> USTs. Groundwater contamination was defined laterally to the north (downgradient), east, and <br /> west (cross-gradient), but not to the south (upgradient). <br /> 3.0 PROPOSED ACTIVITIES <br /> This section describes the specific activities associated with the implementation of the scope of <br /> work described in Section 1.1, Project Objectives and Scope. <br /> All proposed field activities will be conducted in accordance with the APP/SSHP (Appendix B). <br /> 3.1 PERMITTING <br /> The SJCEHD is the lead agency that oversees the installation of groundwater wells within San <br /> Joaquin County. In accordance with SJCEHD requirements, one well permit application will be <br /> filed for the four proposed groundwater monitoring wells and the 30 proposed soil gas/grab <br /> groundwater sample borings. Once all appropriate SJCEHD permits have been received, field <br /> activities will be scheduled. <br /> 3.2 SITE PREPARATION <br /> All proposed field activities will be coordinated in advance with the CVRWQCB and appropriate <br /> CA ARNG personnel. Site preparation activities will be coordinated by OTIE's Field Manager, <br /> and will be initiated by a site visit to mark out proposed invasive drilling locations (i.e. well and <br /> boring locations). The Field Manager will further ensure that those locations are cleared for <br /> underground utilities or other obstructions. This clearance will include: <br /> OTIE 7 <br />