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1 <br /> 23 April 1999 <br /> AGE-NC Project No. 95-0100 <br />' Page 2 of 6 <br />' Probe boring CB 1 and CB2 were advanced at the northern and southern ends of the former dispenser <br /> island,respectively. Borings CB 1 was advanced to a depth of 60 feet below surface grade(bsg). Soil <br /> boring CB2 was advanced to a depth of 35 feet bsg. Soil samples were collected at 5-foot intervals, <br />' beginning at a depth of 5 feet bsg to a depth of 55 feet bsg in boring CB 1 and to a depth of 35 feet <br /> in CB2. <br /> The soil borings were advanced at the site using a van-mounted Geoprobe 5400 probing unit <br /> equipped with 1.25-inch diameter probe rods with a 2.15-inch diameter soil sampling assembly,pre- <br /> loaded with four six-inch by 1.125-inch brass sleeves. After soil samples collection all soil sleeves <br />' were removed from the soil sampler and the ends of the second 6-inch brass soil sleeve were covered <br /> with Teflon sheets,capped and sealed with tape.The sample containers were labeled with the sample <br /> identification(boring location, time and date). The sleeves were placed in a chilled container. <br /> Following collection of soil samples from boring CBI, ground water was encountered at <br /> approximately 55 feet, as inferred from saturated soil samples collected at 55 feet bsg, at which point <br /> a Geoprobe water sampling assembly, equipped with a slotted PVC screen, was advanced into the <br /> boring to a depth of 60 feet bsg. The PVC screen was then exposed to the saturated soil. Ground <br /> lie <br /> water was allowed to enter the casing and a water sample was retrieved using a modified PVC tubing <br /> bailer. A sample was then drawn to the surface. The grab ground water sample was transferred into <br /> a laboratory 40-m1 EPA-approved volatile organic analysis (VOA) vials containing 0.5 ml 18% <br />' hydrochloric acid as a sample preservative. The sample containers were labeled with the sampling <br /> identification (boring location,time and date). The samples were placed in a chilled container. <br />' 2.2. EQUIPMENT DECONTAMINATION <br />' All sampling tools and brass sleeves used for sample collection were thoroughly rinsed with clean <br /> water after washing with a solution of Alconox. All Geoprobe rods were cleaned prior to <br /> advancement of each,probe boring. <br />' 2.3. SAMPLE ANALYSIS <br /> The soil samples and the `grab' ground water sample were logged on a chain-of-custody form, stored <br /> in a chilled container and transported under chain-of-custody.to McCampbell Analytical_Inc. <br /> a California Department of Health Services (DHS)-certified laboratory. The soil samples and the <br /> grab water sample were analyzed in accordance with: <br /> • EPA Method 8015 Modified for total <br /> petroleum hydrocarbons uantified as gasoline TPH <br /> g) and - <br /> Advanced GeoEnvironmental,Inc. <br />