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A soil vapor extraction (SVE) system along with two air sparging wells (SWI and SW2) was <br /> installed in May 1994. The SVE system recovered petroleum hydrocarbon vapors using four <br /> vadose zone wells screened from 10 to 30 feet below ground surface (bgs). Due to an increase in <br /> groundwater elevation at the site, petroleum hydrocarbons trapped in soil below the water table <br /> have not been effectively remediated with the SVE system. <br /> In November 1996, a vacuum vaporizer well system, known as UVB (Underdruck Verdampfer <br /> ` Brunnen), was installed for groundwater remediation at the site. The installation of the UVB <br /> system consisted of overdrilling existing groundwater recovery well RW3 to install the dual- <br /> screen UVB well for groundwater extraction-injection, and the installation of adjacent <br /> ` monitoring wells UVB-MWI and UVB-MW2 to monitor system performance. The operational <br /> measurements of the UVB system show that it has reached the asymptotic stage of operation and <br /> has not achieved a significant migration control. The UVB system will therefore be shut down <br /> ` as referenced in ETIC's letter dated 29 October 2000. <br /> ` Groundwater monitoring and sampling was initially conducted in January 1987, and has been <br /> conducted on a quarterly basis since February 1989. The samples are submitted to a state <br /> certified laboratory and analyzed for benzene, toluene, ethylbenzene, and total xylenes (BTEX), <br /> ` and for Total Petroleum Hydrocarbons as gasoline (TPH-g). Groundwater samples have also <br /> been analyzed for methyl t-butyl ether(MTBE) since 1995. <br /> PLANNED ENVIRONMENTAL ACTIVITIES <br /> Risk Assessment <br /> ETIC will conduct a risk evaluation following ASTM RBCA methodology to assess <br /> environmental risks due to the presence of petroleum hydrocarbons at the site. The RBCA <br /> analysis will be based on ASTM E 1739-95 and San Francisco Regional Water Quality Control <br /> Board (SFRWQCB) vapor pathway guidelines, accounting for complete direct and/or indirect <br /> soil exposure pathways associated with future site residents and construction workers. <br /> r <br /> Additional data for the risk evaluation will be collected during a shallow soil and soil gas <br /> investigation. Eight soil borings will be installed to collect shallow soil and soil gas samples. <br /> One soil sample will be collected from each boring at approximately 2 feet bgs, and soil gas <br /> samples will be collected from each boring at approximately 3 and 6 feet bgs. Each soil sample <br /> will be analyzed for Total Organic Carbon (TOC) by SW9060, moisture content by D2216, and <br /> porosity by ASTM D854. Each soil vapor sample will be analyzed for TPH-g, BTEX, and <br /> oxygenates by EPA Method TO-14. The proposed depths and analyses for soil and soil gas <br /> samples are presented in Table 1. The borings will be driven by the direct push method, and the <br /> vapor samples will be collected in 6-liter Summa canisters or 1-liter Tediar bags. The proposed <br /> locations of the shallow soil borings are shown on Figure 1. The locations of the soil borings <br /> were chosen to assess the presence of hydrocabons in the vadose zone onsite. The results of this <br /> sampling and analysis will be used in the RBCA risk evaluation. <br /> F\Pmje u\73992\M STERMWP p1000\.ttd 2 <br /> V <br />