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pe9e 6 <br /> Each boring was advanced with a hand auger. Discrete soil <br /> samples and a grab water sample were acquired from each <br /> borehole. Each soil sample was collected within a 1 . 9 inch <br /> diameter by 4 . 0 inch long clean brass sleeve fitted within <br /> a drive sampler lowered into the borehole to a point <br /> accessed by the hand auger . Upon being retrieved, the <br /> drive sampler was opened and the brass sleeve removed. The <br /> ends of each sleeve were then covered with teflon <br /> sheeting/aluminum foal , fatted with plastic caps , and <br /> sealed with duct tape. Each tube was then marked and <br /> placed in an iced, insulated container for trans-portation <br /> to Priority Environmental Labs of Milpitas , a California- <br /> state certified hazardous waste analytical laboratory, <br /> under chain of custody. Subsequent analyses were performed <br /> for Total Petroleum Hydrocarbons as Diesel (TPH-D) , Total <br /> Petroleum Hydrocarbons as Gasoline (TPH-G) , benzene, <br /> toluene, ethylbenzene , and total xylenes (BTEX) using EPA <br /> Methods 3550/8015 and 5030/8015-8020 , respectively. <br /> Grab water samples from each boring were acquired within a <br /> clean, disposable polyethylene bailer lowered into the <br /> borehole to a point just below the surface of the water . <br /> Upon being returned to grade, the contents of each bailer <br /> • were transferred into Volatile Organic Analysis (VOA) vials <br /> and one amber glass liter bottle. Each container was <br /> promptly covered with a teflon-lined screw cap, labeled, <br /> and placed in an aced, insulated container for trans- <br /> portation to Priority Environmental Labs under chain of <br /> custody. Subsequent analyses were performed for Total <br /> Petroleum Hydrocarbons as Diesel (TPH-D) , Total Petroleum <br /> Hydrocarbons as Gasoline (TPH-G) , benzene, toluene, ethyl- <br /> benzene, and total xylenes (BTEX) using EPA Methods 3510/ <br /> 8015 and 5030/8015-8020 (602 ) , respectively <br /> Boring EP--5 was located eight feet east of the eastern <br /> boundary fence of 2360 East Street near the southern <br /> boundary of the south sidewalk of Grant Line Road The <br /> first few inches of the soil profile consisted of asphalt <br /> pavement and gravel . The top 4 feet of soil beneath <br /> consisted of dark-brown silty clay followed by clay to 6 <br /> feet . Light-olive colored dense clay was present between 6 <br /> and 7 feet where an odor consistent with petroleum <br /> hydrocarbons was present . Groundwater was encountered <br /> beneath this dense clay layer in a dark-gray salty sand <br /> formation with intense petroleum hydrocarbon odor . A <br /> brown, oily sheen was present on the groundwater Later , <br /> when a groundwater sample was taken, the same oily material <br /> was observed coating the bailer . Discrete soil samples <br /> were acquired at 5 feet and 7 . 5 feet below ground surface <br /> .� (bgs) . <br />