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V, Hazardous Waste Tank Closure Certification, and Sims Metal Management weight receipt and <br /> Certificate of Destruction are in Appendix C. <br /> 6, Non-impacted soil generated during the tank removal activities were placed back into the excavation <br /> up to the level of the Comcast fiber optic line conduit (Photo No. 4). The remainder of the tank <br /> excavation was backfilled with two-sack concrete sand slurry per Comcast's requirements. The <br /> L excavation backfill was completed with asphalt concrete cold patch (Photo No. 5). A copy of the <br /> completed SJCEHD Backfill Excavation Certificate is in Appendix D. <br /> Soil Conditions, Sampling and Analysis <br /> Soil conditions exposed in the tank excavation consisted of slightly moist, firm to stiff, silty clay with a <br /> petroleum odor. No soil staining or other field indicators of potential contamination were noted. A <br /> photoionization detector (PID) reading of the excavation bottom soil was 342arts <br /> Groundwater was not encountered in the tank excavation. P per million. <br /> �- Soil sample UST-7.25 was obtained approximately 2 feet beneath the bottom of the UST excavation <br /> using the backhoe bucket. Soil sample PIPE-3 was obtained beneath the suspected location of the interior <br /> former fuel dispenser location using a hand-auger. The soil samples were collected in new stainless steel <br /> tubes, sealed at both ends with Teflon, capped, labeled, and placed in a chilled cooler pending transport <br /> under chain-of-custody protocols to the laboratory. The approximate soil sample locations are depicted <br /> on Figure 2. <br /> r. <br /> The soil samples were delivered to ATL for analysis of gasoline-and diesel-range organics (GRO and <br /> DRO) following Environmental Protection Agency (EPA) Test Method 8015B, benzene, toluene, <br /> ` ethylbenzene and total xylenes (BTEX) by EPA Test Method 8021, fuel oxygenate compounds (FOCs) <br /> by EPA Test Method 8260B, and total lead by EPA Test Method 7420 in accordance with SJCEHD <br /> requirements for leaded gasoline fuel. <br /> ANALYTICAL RESULTS <br /> Petroleum hydrocarbon constituents were reported in UST removal soil sample UST-7.25 including <br /> GRO and DRO at 1,300 and 610 milligrams per kilogram(mg/kg), respectively. Toluene,ethylbenzene <br /> and total xylenes were detected in sample UST-7.25 at concentrations ranging from 6,900 to 66,000 <br /> micrograms per kilogram. Benzene and FOCs were not detected above the laboratory reporting limits <br /> for sample UST-7.25. <br /> The only petroleum hydrocarbon constituent reported in product piping soil sample PIPE-3 was DRO <br /> at a concentration of 3.3 mg/kg. This DRO concentration is consistent with naturally occurring <br /> organics as opposed to fuel contamination. <br /> Total lead was detected in soil samples UST-7.25 and PIPE-3 at respective concentrations of 34 and 88 <br /> mg/kg. <br /> ` A summary of the soil analytical data is presented on Table 1. Copies of the laboratory report and <br /> chain-of-custody documentation are in Appendix E. <br /> 6. <br /> Linden UST Removal Report,TO No.34 Caltrans Contract 06A1895,EA No. 10-0Y3600 <br /> Geocon Project No.59800-01-34 -3 - December 22,2014 <br /> b. <br />