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3.1 FIELD PREPARATION <br /> Prior to beginning the field program, ETIC will arrange for access with the current Site owner, <br /> Mr. Overton. Once site access has been arranged, the proposed boring locations will be marked <br /> and checked for the presence of underground utilities by Underground Service Alert. A private <br /> utility-locating contractor will also be hired to identify the presence of underground utilities. <br /> Drilling permits will be obtained from San Joaquin County Environmental Health Department <br /> (SJCEHD). A health and safety plan will be prepared and implemented during drilling and <br /> sampling activities. Each soil boring on the Site will be hand augured to a minimum depth of 4 <br /> feet BGS to identify utilities prior to drilling. <br /> 3.2 DRILLING AND SOIL SAMPLING <br /> Based upon hydrogeologic information obtained from other sites in the vicinity, groundwater in <br /> the shallowest aquifer flows to the southeast. The results of previous soil and groundwater <br /> investigations performed at the Site indicate that additional characterization of the extent of <br /> contamination is needed within the area of, east, and south of the former UST excavation, in the <br /> vicinity of the former dispenser, and in the area of a sump located inside the existing <br /> warehouse. Soil and shallow groundwater samples will be collected from I I borings to further <br /> characterize petroleum hydrocarbon contamination in these areas. The proposed boring <br /> locations are shown on Figure 4. <br /> Drilling will be performed by a C57-licensed contractor, using a direct-push drilling rig. All <br /> drilling equipment and sampling tools will be decontaminated prior to beginning the field <br /> program. Reusable sampling equipment will be thoroughly washed with a Liqui-Nox solution, <br /> rinsed with tap water, and then rinsed with distilled water prior to each use. An ETIC geologist <br /> will supervise all drilling and sampling activities. Soil samples will be examined for lithologic <br /> identification and visible signs of contamination in accordance with the Unified Soil <br /> Classification System and the Standard Practice for Description and Identification of Soils <br /> (Visual-Manual Procedure), American Society for Testing and Materials (ASTM) Designation <br /> D2488 (ASTM 2000), and the observations will be recorded in the field logs. Technical <br /> guidance for the program will be provided by a California Professional Geologist. <br /> A photo-ionization detector (PID) will be used to monitor for organic vapors. Measurements of <br /> headspace vapors from soil samples will be recorded on the boring logs. If any unusual stains <br /> or odors are evident in the soil, additional samples will be collected for laboratory analyses. <br /> Each soil boring will be drilled to a total depth of approximately 55 feet BGS. Soil samples <br /> will be collected from the I I borings at approximate 5-foot intervals, at changes in lithology, at <br /> the soil-water interface, and where contamination is evident. The samples will be submitted for <br /> laboratory analyses. Additional soil samples may be collected and held for subsequent analysis, <br /> 7 <br />