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Five (5) confirmatory soil samples (SB11), S132G, SB3E, SB4F and SB15) were collected from <br /> the bottom of the north south, east and west corners of the elevator shaft, and the center <br /> excavation borings, respectively, at the request of SJCPHS The four (4) corner samples <br /> represent sidewall samples <br /> The soil samples were taken with a Modified California Split Spoon Sampler lined with brass <br /> sampling sleeves 2 inches in diameter by 6 inches long driven into the soil with a 70-pound slide <br /> hammer After each sample was collected, it was presented to Inspector Sasson for review prior <br /> to capping The ends of the sample sleeves were covered with teflon tape, capped with plastic <br /> caps, sealed in plastic bags, stored on ice and delivered to the laboratory for analysis The soil <br /> samples were described by a field geologist under the supervision of a California Registered <br /> Geologist, in accordance with the Unified Soil Classification System (USCS) <br /> The confirmatory samples were transported to Curtis & Tompkins, Ltd (DHS ELAP Certificate <br /> #1459) located in Berkeley, Califorma with standard chain of custody documentation Analysis <br /> was requested on a 24-hour turnaround basis for the bottom samples and standard turn-around <br /> on the shallow samples <br /> Two (2) separate mobile field labs were used to field screen samples during the boring <br /> operations These were Calscience Environmental Laboratories, Inc of Stanton, Califorma and <br /> Sequoia Analytical of Sacramento, California Samples were submitted to these labs under the <br /> same handling and documentary protocol as those sent to Curtis & Tompkins, Ltd Laboratory <br /> analytical results for the soil excavation are provided in Appendix V <br /> The analytical results on the confirmatory samples revealed concentrations of TPH in SB11) at <br /> 250 ppm and non-detected in the other four (4) samples Boring SB1 was extended only to 10 <br /> feet 6 inches based on a mobile lab screening result of non-detected in sample SB 1 C at 10 feet <br /> The other four borings were between 15 feet 6 inches and 20 feet 6 inches deep <br /> In addition to the confirmatory borings, four (4) additional 18-inch borings and six (6) 14-inch <br /> in-fill borings were drilled to remove as much contaminated soil from beneath the elevator shaft <br /> as possible These borings were advanced until mobile lab field screening results were less than <br /> 100 ppm TPH as hydraulic fluid by EPA Method 8015M <br /> The results of the bottom samples from the remaining 18-inch borings were 770 ppm for SBSC, <br /> 89 ppm for SB6E, 1,600 ppm for SB7F and non-detected for SBBE The results for the 14-inch <br /> borings were all non-detected for samples SB9B, SB10A, SB11B, SB12B and SB14B No <br /> samples were taken in boring SB13 The bottom depths for these borings ranged from 15 feet <br /> 6 inches to 19 feet 6 inches <br /> When mobile lab field screening data indicated sample results of less than 100 ppm TPH as <br /> hydraulic fluid by EPA Method 8015M, the groundwater in the borings was pumped out with a <br /> submersible pump in an effort to remove as much floating hydraulic fluid as possible from the <br /> excavation Over 2,000 gallons of hydraulic fluid-contaminated groundwater was pumped out <br /> CRC Environmental Risk Management Inc Project#3620-001- <br /> i <br /> George Bravante,Receiver 2233 Grand Canal Boulevard <br /> January 19 1995 4 Stockton California <br />