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Donna Gardner 2 <br />29 September 2006 <br />26056 Thornton Rd., Thorn. , <br />143 to 150 Sand it II <br />150 to 155 Clay LI <br />155 to 164 , Sand 160 to 185 LI <br />- <br />164 to 231 - clay and Shale 225 to 235 tt <br />231 to 245 Sand 2 <br />245 to 350 Clay <br />350 to 360 Sand <br />360 to 371 Clay and Shale <br />371 to 376 Sand <br />376 to 380 Shale <br />380 to 395 Sand <br />395 to 4203 Shale <br />1 — depths in feet bgs 2 — Total Depth of Well Casing, 245 feet bgs 3 — Total Depth of 28-inch Diameter Boring, 420 feet bgs <br />While Well #2 is screened below 135 feet bgs and has a 70-foot cement sanitary seal, the <br />drilling log shows sand pack from 0 (surface) to 245 feet bgs. If the drilling log is correct, then <br />the construction of Well #2 could present a preferential pathway for groundwater pollution <br />deeper than 70 feet into the deeper water zones. However, monitoring of Well #2 has shown <br />no impact from petroleum hydrocarbons to date. <br />In November 1990, WaterWork (A.K.A. RESNA), a consultant for Wilson, Hoslett and <br />Whitridge installed monitoring wells MW-1 through MW-3 to 28 feet bgs (Figure 2). The depth <br />to shallow groundwater was 12 feet bgs. Soil samples were not analyzed since sample <br />holding times were exceeded. Maximum 1990 groundwater groundwater concentrations were: <br />TPHg, 45,000 pg/L; benzene, 270 pg/L; toluene, 15 pg/L; ethylbenzene, 63 pg/L; and xylenes, <br />110 pg/L. <br />Three additional monitoring wells (MW-4 through MW-6, Figure 2) were installed in October <br />1991 and screened from 5 to 15 feet bgs. The downgradient groundwater direction was <br />towards the west. Two areas of soil contamination (near MW-3 and MW-4) were noted in the <br />January 1992 Interim Problem Assessment Report, Soil and Groundwater Contamination. <br />MW-3 is located immediately northwest of the former USTs, while MW-4 is approximately <br />20 feet south of Well #2. The maximum groundwater results (MW-4) in October 1991 were: <br />TPHg, 19,000 pg/L; benzene, 110 pg/L; toluene, 79 pg/L; ethylbenzene, 640 pg/L; and <br />xylenes, 1,700 pg/L. <br />The service station buildings were removed in November 1994, and eight soil borings were <br />advanced from 20 to 45 feet bgs to assess the vertical and lateral extent of the soil <br />contamination. The maximum vertical extent of soil contamination was reported as 30 feet <br />bgs. Approximately 1,400 cubic yards of soil and 10,000 gallons of excavation water were <br />removed in February 1995. The excavated soil was stockpiled onsite and aerated In <br />November 1996. No petroleum hydrocarbons were detected in the analyses of the stored <br />excavation water, and the water was discharged to land at the Site in May 1995 without a <br />Regional Board permit. The October 1997 Problem Assessment Report recommended a pilot <br />study for soil vapor extraction and air sparging, which was approved by SJCEHD but was not <br />implemented. In March 2001, a groundwater pumping test was proposed by consultant ATC