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tidal influences (clock-times and heights) at Stockton were converted monthly from available <br /> f`f' tidal table information on the dates of soundings of the three wells. The Project Status Report <br /> `j of Ground-Water Monitoring (W.W. Irwin, Inc., January 30, 1995) contained data which, until <br /> the Problem Assessment Report was issued on August 8, 1995, were the most recent regarding <br /> site conditions at Village West Marina. <br /> 1 <br /> Problem Assessment and Completions of MW-7 and MW-8 <br /> On July 3, 1995, W.W. Irwin, Inc. directed the drilling, logging, and sampling of <br /> Hydropunches'''"°HP-7, HP-8, HP-9, and HP-10. HP-7 and HP-8 were completed as monitoring <br /> wells MW-7 and MW-8 after ground-water samples collected for "rushed" analyses of gasoline <br /> and diesel analytes at Sherwood Labs in Hilmar were found nondetectable. The new monitoring <br /> wells were drilled, sampled, and completed in order to determine the horizontal and vertical <br /> extent of soil and ground-water contamination. The new monitoring well locations are initially <br /> depicted on the Site Plan, Figure 2. <br /> Each sample collected from HP-7, HP-8, HP-9, and HP-10 was analyzed for the presence of <br /> Total Petroleum Hydrocarbons asgasoline (TPH-g) by modified EPA Method 801515030, Total <br /> Recoverable Petroleum Hydrocarbons as diesel (TRPH-d), and the volatile aromatics benzene, <br /> toluene, ethylbenzene, and total xylenes (BTEX) by EPA Method 8020. All soil analytical <br /> results are listed in Table 1. <br /> Detectable, primarily fractional BTEX analytes were detected only in soil samples collected from <br /> HP-7 at 15 feet, and from HP-9 at 15 feet. The highest TPH-g result was 3 mg/Kg, revealed <br /> in the sample collected from HP-9. TRPH-d results were wholly nondetectable. <br /> 1 <br /> HydropunchTm ground-water samples were collected from HP-7 at 19 feet; from HP-8 at 21.5 <br /> feet; from HP-9 at 23.5 feet; and from HP-10 at 21.5 feet bsg. HP-9 yielded the only sample <br /> impacted with elevated concentrations of TPH-g and benzene. Table IA lists the analytical <br /> results of the HydropunchT'ground-water samples submitted to Sherwood Labs Corporation of <br /> Hilmar, California. <br /> ' New monitoring wells MW-7 and MW-8 were developed on July 7, 1995 using sterile, <br /> polyethylene bailers. Bailing removed turbid water from the wells until clear water appeared. <br /> The monitoring wells were sampled after a minimum of 40 gallons were bailed and the ground- <br /> water levels had recovered to at least 90% of their static levels. <br /> ;I'_ Following completion of all tasks, the Problem Assessment Report and Project Status Report of <br /> Ground-Water Monitoring were issued by W.W. Irwin, Inc. on August 8, 1995. Monitoring <br /> activities conducted on October 18, 1995 were documented in the Project Status Report dated <br /> October 31, 1995. The Remedial Action Plan with feasibility study were issued on December <br /> 28, 1995; W.W. Irwin, Inc. has recommended bioventing with continued ground-water <br /> monitoring as the best, cost-effective technologies for cleanup of affected soil and ground water. <br /> W.W. Irwin, Inc. <br /> 1 Project No. 33016.06 <br /> �. <br /> April 1996 6 <br />