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ERI 205503 Rol Unocal Service Station 5886 Stockton California lune 3 1997 <br /> FIELD PROTOCOL <br /> Site Safety_ Plan <br /> Field work is performed by ERI personnel in accordance with a site safety plan developed for the <br /> site This plan describes the basic safety requirements for the subsurface investigation and the drilling <br /> of soil borings at the work site The site safety plan is applicable to personnel and subcontractors of <br /> ERI Personnel at the site are informed of the contents of the site safety plan before work begins A <br /> copy of the site safety plan is kept at the work site and is available for reference by appropriate <br /> parties during the work The ERI geologist acts as the Site Safety Officer <br /> Soil Borings and Sampling <br /> Prior to drilling of borings and construction of wells, ERI acquires necessary permits from the <br /> appropriate agency(ies) ERI also contacts Underground Service Alert (USA) before drilling to help <br /> locate public utility lines at the site ERI hand-probes and hand-augers boring locations to a depth of <br /> approximately 5 feet bgs and a diameter greater than the soil boring diameter before drilling to reduce <br /> the risk of damaging underground structures <br /> Soil borings are drilled with a CME-55 (or similar) drill rig equipped with 10-inch diameter, hollow- <br /> stem augers Auger flights and sampling equipment are steam-cleaned before use to minimize the <br /> possibility of crosshole contamination The rinseate is containerized and stored on site ERI will <br /> coordinate with Tosca for appropriate disposal of the rinseate <br /> . Drilling is performed under the observation of a field geologist, and the earth materials in the borings <br /> are identified using visual and manual methods, and classified as drilling progresses using the Unified <br /> Soil Classification System Soil borings are drilled to approximately 10 feet below the uppermost <br /> zone of saturation or 5 feet into any competent clay layer (aquitard) encountered beneath the water- <br /> bearing zone If an aquitard is encountered, the boring is terminated and backfilled with bentonite <br /> before installing a groundwater monitoring well <br /> During drilling, soil samples are collected at 5-foot intervals, obvious changes in lithology, and dust <br /> above the groundwater surface Samples are collected with a California-modified, split-spoon sampler <br /> equipped with laboratory-cleaned brass sleeves Samples are collected by advancing the auger to a <br /> point,lust above the sampling depth and driving the sampler into the soil The sampler is driven 18 <br /> inches with a standard 140-pound hammer repeatedly dropped 30 inches The number of blows <br /> required to drive the sampler each successive 6-inch interval is counted and recorded to give an <br /> indication of soil consistency <br /> Soil samples are monitored with a photoionization detector (PID), which measures hydrocarbon <br /> concentrations in the ambient air or headspace above the soil sample Field instruments such as the <br /> PID are useful for indicating relative levels of hydrocarbon vapors, but do not detect concentrations <br /> of hydrocarbons with the same precision as laboratory analyses Soil samples selected for possible <br /> chemical analysis are sealed promptly with TeflonB tape and plastic caps The samples are labeled <br /> and placed in iced storage for transport to the laboratory Cham of Custody Records are initiated by <br /> the geologist in the field, updated throughout handling of the samples, and sent with the samples to <br /> the laboratory Copies of these records are in our report Cuttings generated during drilling are <br /> placed on plastic sheeting and covered and left at the site ERI coordinates with Tosco for the soil to <br />