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19 January 2012 <br /> AGE-NC Project No. 11-2006 <br /> Page 2 of 7 <br /> ends of a separated, 6-inch portion of the acetate liner were covered with Teflon sheets, <br /> capped and sealed with tape. The cut portion of the liner was labeled with soil boring <br /> location, depth, time, date and sampler's initials and then placed in a chilled container. Soil <br /> samples were transported under chain-of-custody to Cal Tech Environmental Laboratories <br /> (CTEL), a California Department of Public Health-Certified laboratory and analyzed for the <br /> following chemical constituents: <br /> • Total petroleum hydrocarbons (TPH-all) in accordance with EPA-method 8015- <br /> modified; <br /> • Volatile organic compounds (VOCs) in accordance with EPA method 826013; <br /> • Semi-volatile organic compound (SVOC's) in accordance with EPA method 8270; <br /> and <br /> • California Assessment Metals (CAM) 17 by EPA method 6010B and 7471. <br /> The remaining portion of each sample was extruded into a plastic bag and field-screened <br /> for the presence of organic vapors using an organic vapor meter (OVM), equipped with a <br /> photo-ionization detector(PID). Additionally, the soil was visually classified in accordance <br /> with the Unified Soil Classification System (USCS). PID readings and soil classifications <br /> were recorded on boring logs, which have been included in Appendix B. <br /> In addition to the soil samples collected from borings B7 and B8, selected samples <br /> collected from borings B1, B2 and B6 on 10 November 2011 were also analyzed for CAM <br /> 17 metals. <br /> GRAB GROUND WATER SAMPLE COLLECTION <br /> Grab ground water samples were collected from borings 137 and B8 at a depth of <br /> approximately 30 feet bsg. Ground water samples were collected by placing 1-inch PVC <br /> pipe equipped with a 4-foot section of temporary screen down the advanced borehole to <br /> a depth of 30 feet bsg. Each ground water sample was extracted using inertial action by <br /> lowering Teflon tubing through the hollow center of the PVC pipe. A sufficient sample was <br /> collected to fill three 40-ml EPA-approved volatile organic analysis (VOA) vials and one <br /> 1-liter amber bottle, each without preservative. The ground water sample containers were <br /> labeled with soil boring designation, date, time, and samplers initials and then placed in a <br /> chilled container. Grab ground water samples were transported under chain-of-custody to <br /> CTEL and analyzed for the following chemical constituents: <br /> • TPH-all in accordance with EPA-method 8015-modified; <br /> Advanced CcoEnvironmrntal,Inc. <br />