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i GETTLER-RYAN INC. <br /> FIELD METHODS AND PROCEDURES <br /> WELL INSTALLATION <br /> Site Safety Pian <br /> Field work performed by Gettler-Ryan Inc (GR) is conducted in accordance with GR's Health and Safety <br /> Plan and the Site Safety Plan GR personnel and subcontractors who perform work at the site are beefed <br /> on the contents of these plans prior to initiating site work The GR geologist or engineer at the site when <br /> the work is performed acts as the Site Safety Officer GR utilizes a photoionization detector (PID) to <br /> monitor ambient conditions as part of the Health and Safety Plan <br /> Collection of Soil Samples <br /> Collection, preservation, and analysis of samples is performed in accordance with the California Code of <br /> Regulations Title 23, Division 3, Chapter 16, Underground Tank Regulations (June 2001), the Central <br /> Valley Regional Water Quality Control Board's Tri-Regional Board Staff Recommendations for <br /> Preliminary Investigation And Evaluation Of Underground Tank Sites (August 1990), Environmental <br /> Protection Agency SW-846 Methods(November 2000), and local agency guidelines <br /> Well borings are drilled by a California-licensed well driller A GR geologist is present to observe the <br /> drilling, collect soil samples for description, physical testing, and chemical analysis, and prepare a log of <br /> the exploratory soil boring under the supervision of a California Registered Geologist Soil samples are <br /> collected from the soil boring with a split-barrel sampling device fitted with 2-inch-diameter, clean brass <br /> tubes or stainless steel liners The sampling device is driven approximately 18 inches with a 140-pound <br /> hammer falling 30 inches The number of blows required to advance the sampler each successive 6 <br /> inches is recorded on the boring log The encountered soils are described using the Unified Soil <br /> Classification System (ASTM 2488-93) and the Munsell Soil Color Chart or GSA Rock Color Chart <br /> After removal from the sampling device, soil samples for chemical analysis are covered on both ends with <br /> teflon sheeting, capped, labeled, and placed in a cooler with blue ice for preservation to 4°C±2°C A <br /> chain-of-custody form is initiated in the field and accompanies the selected soil samples to a California <br /> state-certified hazardous material testing laboratory Samples are selected for chemical analysis based in <br /> part on <br /> a depth relative to underground storage tanks and existing ground surface <br /> b depth relative to known or suspected groundwater <br /> c depth relative to areas of known hydrocarbon impact at the site <br /> d presence or absence of contaminant migration pathways <br /> e presence or absence of discoloration or staining <br /> f presence or absence of obvious gasoline hydrocarbon odors <br /> g presence or absence of organic vapors detected by headspace analysis <br /> Field Screening of Soil Samples <br /> A PID is used to perform headspace analysis in the field for the presence of organic vapors from the soil <br /> sample This test procedure involves removing some soil from one of the sample tubes not retained for <br /> chemical analysis and immediately covering the end of the tube with a plastic cap, or by placing a small <br /> amount of the soil to be screened in a sealable plastic bag The soil is warmed in the sun to allow organic <br /> compounds in the sample to volatilize The PID probe is inserted into the headspace inside the tube <br />