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Ce0k9icdTecFinics Inc. <br /> Gubwy Page 2 <br /> Project No. 775.2 <br /> July 13, 1999 <br /> the former center UST. See Figure 2: Sketch.map for boring location. A hydropunch type <br /> groundwater sample will be collected from the boring. <br /> The soil boring will be drilled using an 8-inch outside diameter, continuous flight, hollow <br /> stem auger owned and operated by V&W Drilling (C57# 720904). The expected depth to <br /> groundwater is approximately 60 feet below ground surface, based on data from San Joaquin <br /> County Flood Control and Water Conservation District. <br /> The soil boring will be drilled to the,capillary .fringe. After the collection of the hydropunch <br /> sample,the borings will be closed by a neat cement grout trernied into the borehole. <br /> Soil boring permits will be secured as necessary and the local regulatory agency will be <br /> notified 48 hours prior to commencing work. The subsurface will be cleared of underground <br /> utilities by notifying Underground Service Alert. <br /> 2.1 Soil Sampling Procedure <br /> Soil samples will be collected for geological and analytical evaluation at 5-foot intervals. A <br /> boring log providing sediment description using the USCS and field observations will be <br /> maintained by a professional geologist working under the supervision of a registered <br /> geologist. Soil samples wi1l be collected in 6:0-inch brass liners using a 2.0 inch modified <br /> California split spoon sampler. All soil samples will 'be sealed with Teflon, capped with <br /> Teflon end caps, labeled and placed in a cooler at 4° Celsius for transport to the laboratory <br /> following Chain of Custody protocol. <br /> Since only selected soil samples will be submitted for laboratory analysis, a screening <br /> process will be used to gather additional information through field observation including: <br /> a sediment type, especially grain size and clay content <br /> moisture content <br /> • visible evidence of contamination, i.e., color change due to reduction of iron or <br /> discoloration from hydrocarbons and other pollutants <br /> a readings above background on a organic vapor meter (OVM) <br /> The OVM is a portable photo ionization detector that uses a 10.0 eV lamp to detect <br /> compounds with ionization potential below 10.0 eV (hydrocarbon range). <br /> 2.2 Hydropunch Sampling Procedure <br /> After the capillary fringe soil sample is collected from borehole, a hydropunch type <br /> groundwater sampling tool will be advanced into the saturated zone. The tool will then be <br /> retracted to expose the screen. A narrow diameter stainless steel bailer will be used to <br /> recover representative groundwater samples. Care will be taken to .minimize sample <br /> agitation from the initial filling of the bailer to the transfer of the sample to the VOA vial. <br /> Once the sample container is filled and capped, the bottle will be inverted, tapped, and <br /> checked for headspace bubbles. The sample container is identified and labeled with a unique <br /> designation, inserted into foam holders and placed in an ice chest cooled to 4°C for transport <br /> to the laboratory. <br /> All non-disposable sampling equipment is decontaminated using a steam cleaner before and <br /> between uses. Disposable gloves will be used while collecting all samples and will be <br /> changed with each sampling event. A bailer blank for each borehole will be collected prior to <br />