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Cla%-ton <br /> Grant Trigger Pam, <br /> Honigman Miller Schwartz and Cohn Clayton Proposal No. 975FOEMR43 i <br /> October 7, 1997 <br /> of any of the borings, drilling may be advanced an additional 4 to 8 feet to determine if <br /> the vertical impact varies with depth. Clayton will advise the client prior to incurring <br /> any additional costs. The GeoProbe technique typically penetrates the subsurface in four- <br /> foot intervals and collects a continuous core inside a plastic liner. The recovered soil <br /> cores will be observed for odor, staining, and presence of volatile organic compound <br /> (VOCs) based on photoionization device (PID) readings (one reading per sample liner). <br /> Soil intervals selected for laboratory analysis will be cut from the main core, sealed with <br /> teflon tape and plastic end caps, labeled, and placed in cold storage for transportation to <br /> the analytical laboratory under formal chain-of-custody. <br /> Clayton will retain one sample from each four-foot probe interval in the event additional <br /> testing becomes necessary. Based on field screening results, one soil sample per boring <br /> will be selected for laboratory analysis. Soil cuttings will be field screened by a PID. If <br /> no indication of potential contaminants are detected by observation or PID readings, a <br /> soil sample from about the 3.5 to 4 foot range will then be submitted for testing to <br /> confirm the limited depth of TRPH impact in the-areas of concern. If elevated PID <br /> readings are detected or observations indicate contamina ion during field screening, the <br /> number of soil samples submitted for laborafory analysis may vary and the boring may <br /> be extended. The samples in the vicinity of the oil/water separator will be collected at <br /> depths greater than the base of the separator and associated piping to evaluate the <br /> potential for releases to have occurred from this device. <br /> Clayton does not anticipate that this sampling plan will penetrate the groundwater table. <br /> Should groundwater be encountered, a grab groundwater sample will be collected from <br /> each boring, if possible, and the water sample may be submitted in place of the soil <br /> sample. The depth to groundwater at the subject property is believed to be <br /> approximately 60 feet below the ground surface. Groundwater samples will be collected <br /> using a stainless steel bailer. The samples will be decanted from the bailer into an <br /> appropriate container for the analytical method proposed. The containers will be capped, <br /> labeled and placed into an ice filled chest. <br /> After sampling is completed, the boreholes will be backfilled with neat cement. Soil <br /> cuttings will be placed in a five gallon bucket. The bucket will be labeled and <br /> temporarily stored onsite pending appropriate disposal. Since the quality of the soil and <br /> groundwater is unknown, Clayton has not provided an estimate for disposal costs of the <br /> drilling wastes. <br /> Task 3: Laboratory Analysis <br /> Clayton proposes to submit up to 7 soil samples for chemical analysis by the following <br /> methods on a five-day turn-around-time at Clayton's State-certified laboratory in <br /> Pleasanton, California. All samples will be tested for TRPH: however, only the samples <br /> collected in the vicinity of the oil/water separator will be tested for TRPH, VOCs, and <br /> metals <br /> USEPA Method 418.1/Silica Gel Extraction: Total Recoverable Petroleum <br /> Hydrocarbons (TRPH) <br /> K:IEMRTROPOSALUI ASEl\97. 31.WPD <br />