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C <br /> be collected from the bottom of borings B-4 and B-5(i.e., at approximately 15 feet bgs). Borings B-4 and <br /> B-5 will then be advanced to approximately 40 feet bgs, and a groundwater sample will be collected from <br /> the deep zone (approximately 40 feet bgs) using Hydropunch techniques. <br /> Boring B-6 will be continuously cored from the surface tort40 feet bgs to fuher characterize site soils for E <br /> the SCM. One soil sample will be collected from B-6 at the capillary fringe(approximately 10 feet bgs)or l <br /> where elevated PID readings indicate the presence of impact. Depth discrete groundwater samples will be <br /> collected from the shallow zone (approximately 15 feet bgs), and from the deep zone_(appro(imately <br /> 40 feet bgs) at boring B-6 using Hyrdropunch techniq s If unsaturated soils are encountered between <br /> the shallow and deep groundwater zones, additional soil sam' 1pes maybe collected from the intervening j <br /> unsaturated zone for chemical analysis. <br /> Soil samples will be collected from each boring for lithologic logging and field screening. The samples will <br /> be collected in a 5-foot by 1.5-inch O.D. core samplerequipped with an acetate liner. Soil samples will be <br /> collected at approximate five-foot intervals and at intervals where staining or color or texture changes are <br /> noted. The field staff will examine representative portions of the soil samples and prepare soil boring logs <br /> that describe the encountered soil in general accordance with the American Standards for Testing <br /> Materials (ASTM) 2488-06 and the Unified Soil Classification System (USCS). The soil boring logs will <br /> indicate the depth of the various strata, and record other pertinent information regarding the advancement <br /> and sampling of each borehole. <br /> Each soil sample will be field screened for volatile organic vapors with_a photoionization detector(PID)or <br /> similar instrument. The field screening readings will be recorded on the soil boring log. A portion of each <br /> soil sample will be retained for potential laboratory analysis.. The samples will be collected in an acetate <br /> liner and the liners will be cut at the desired sample interval and sealed with Teflon®tape and plastic caps <br /> at each end. All samples will be stored in an ice chest cooled to approximately 4 degrees Celsius(°C)with <br /> ice. ___- <br /> r <br /> Groundwater samples will be collected using disposable polyethylene tubing. Each sample will be <br /> collected in laboratory-provided containers preserved as appropriate for the specific analytical testing <br /> method. Sampling containers for volatile organic compound (VOC)analysis will be filled completely with F <br /> sample and preservatives to eliminate headspace and create a positive meniscus. The vial will be capped <br /> with convex Teflon es pta. Each vial will be observed to ensure that no air bubbles are present within the <br /> vial. Samples will be marked for identification, placed on ice, and transported to a California certified <br /> laboratory for analysis. Chain-of-custody records will be maintained and accompany all samples to the <br /> analytical laboratory. <br /> e • <br /> Soil and groundwater samples will be analyzed fortotal petroleum hydrocarbons characterized as gasoline ° <br /> (TPHg), benzene, ethylbenzene, toluene, totals xylenes (BTEX), five fuel oxygenates (methyl tert butyl <br /> ether, tertiary butyl alcohol, tertiary-amyl metFij l ether, ethyl tert butyl ether, and di-isopropyl ether), and <br /> lead scavengers (ethylene dibromide and 1,2-dichlo_ roethane) in accordance with EPA Test Method <br /> 8260B. <br /> All cuttings and groundwater removed from the borings will be temporarily stored on-site in Department of <br /> Transportation (D.O.T.)-rated 55-gallon drums pending characterization and proper disposal. <br /> Additional investigation St Workplan <br /> Quik Stop No.132,Stockton,CA <br /> ... May 18,2009 <br /> It <br /> 1 <br />