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Project No 014-95262 <br /> Appendix D <br /> Page No 2 <br /> pH, chloride, phosphate, nitrate, ammonia-N, and oil and grease Soil samples <br /> from hand auger borings near sumps, separators, etc were analyzed for one or <br /> more of the following chloride, electrical conductivity, pH, oil and grease Soil <br /> samples from adjacent to the former boiler diesel supply pipeline, and from areas <br /> previously or currently overlain with spoils from excavation of the former diesel <br /> tanks, were analyzed for Total Petroleum Hydrocarbons as diesel (TPH-D), and <br /> BTEX/TPH-G <br /> 13 Drill cuttings were drummed and stockpiled within the fenced area west of the <br /> main plant building Drill cuttings were segregated based upon field observations <br /> Rinsate generated during decontamination procedures was drummed and left on- <br /> site near the wastewater treatment facility pending analytical results Following <br /> favorable analytical results the drum contents may be metered into the normal <br /> process waste stream for biologic treatment <br /> 14 Equipment used for the advancing of soil borings and the sampling of soils was <br /> decontaminated (steam-cleaned, TSP, lab-grade detergents, etc ) before arriving <br /> on-site, between each boring and/or sampling, before leaving the site, or as <br />' necessary to minimize the chances of cross-contammation The rinsates from the <br /> cleaning were contained and drummed The water was stored on-site pending the <br /> results of the chemical analysis and proper disposal by the client with the <br /> assistance of Krazan& Associates, within 90 days following generation <br /> 15 Nine Hydropunch* II sampling points were placed at various locations at the <br /> subject site to assess the distribution of constituents of concern in groundwater <br /> Please refer to the attached map for the Hydropunch'II sampling points <br /> 9 ' <br /> 16 Prior to driving the Hydropunch'II probe with a cone penetration testing (CPT) <br /> rig, an existing monitoring well was sounded to determine the current depth to <br /> l groundwater beneath the subject site area <br /> 17 A groundwater sample from location HP-6 collected using the Hydropunch' II <br /> sampling tool When positioned below the groundwater surface and locked in <br /> place, the sleeve is retracted exposing a section of PVC well screen Groundwater <br /> enters the well screen with no aeration Once the well screen is filled, <br /> accumulated groundwater was collected using a Teflon bailer <br /> 18 Due to difficulties in obtaining a water sample, caused by clogging of the screen <br /> of the Hydropunch 11 sampling tool, all remaiung water samples were collected <br /> 1 by pushmg rod without the Hydropunch B tool attached Only a sacrificial tip was <br />' placed at the end of the rod The drill rod was pushed to the target depth and then <br /> extracted a few feet separating the tip from the rod and creating a cavity into <br /> which groundwater flowed A Teflon bailer was lowered down the center of the <br /> rods to collect accumulated water,just as if using the Hydropunch R tool <br /> 19 The collected samples were transferred from the bailer to appropriate sample <br /> containers using a bottom emptying device (Teflon check valve and nipple) <br /> minimizing loss of volatile constituents The samples collected were preserved in <br /> 1 I, <br />' KRAZAN& ASSOCIATES, INC <br /> Offices Serving the Western Untied States <br /> 95262 APD <br />