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� v <br /> A S S O C I A T E S I N C <br /> 4 <br /> soil types encountered and sample collection intervals are presented on the boring logs contained <br /> in Appendix A Each soil sample was field screened with a Flame Ionization Detector (FID) for <br /> the presence of volatile organic compounds Sample tubes were then sealed at each end using <br /> Teflon tape and plastic end caps, labeled, and placed on ice <br /> 1 2.1.2 Soil Sample Analysis <br /> Selected soil samples were kept on ice and delivered under chain-of-custody documentation to <br /> State-certified Argon Laboratories Inc (FLAP Cert No 2359) in Ceres, California for chemical <br /> analysis Selected samples were analyzed for total petroleum hydrocarbons as gasoline (TPHg) <br /> by EPA method 8015, BTEX by EPA method 8020, and methyl tertiary butyl ether (MTBE), <br /> tertiary amyl ether (TAME), ethyl tertiary butyl ether (ETBE), tertiary butyl alcohol (TBA), di- <br /> isopropyl ether (DIPS), 1,2-dichloroethane (1,2-DCA), and ethyl dibromide (EDB) by EPA <br /> method 8260 The analytical results for soil samples are summarized in Table 1 Laboratory <br /> data sheets and chain-of-custody documentation are included in Appendix B <br /> 2.13 Groundwater Sampling and Analysis <br /> Groundwater samples were collected from borings SBI through S134 at the depth groundwater <br /> was first encountered, approximately 61 feet bgs A Geoprobe® Screen Point 15 Groundwater <br /> Sampler was threaded onto the leading end of the Geoprobe after groundwater had been <br /> encountered When the sampler was advanced, O-nng seals and an expendable drive point <br /> ' provided a watertight system to ensure sample integrity <br /> When the tool was advanced to the desired depth, extension rods were sent downhole to brace the <br /> ' bottom of the sample screen as the tool casing was retracted When the casing was retracted, <br /> approximately 41-inches of screen with slot sizes of 0 004 inches was exposed Teflon tubing <br /> with a check valve attached to one end was inserted down the casing until it was immersed in <br /> ' groundwater Water was then pumped through the tubing and to the ground surface by <br /> oscillating the tubing up and down Following soil and groundwater sample collection, the <br /> borings were backfilled with neat cement grout to the ground surface <br /> Groundwater samples were kept on ice and delivered under chain-of-custody documentation to <br /> State-certified Argon Laboratories in Ceres, California for chemical analysis Groundwater <br /> samples were analyzed for TPHg by EPA method 8015, BTEX by EPA method 8020, and <br /> MTBE, TAME, ETBE, DIPS, TBA, 1,2-DCA, and EDB by EPA method 8260 The analytical <br /> results for groundwater samples are summarized in Table 2 Laboratory data sheets and chain- <br /> of-custody documentation are included in Appendix C Gat w, } fCSUA�s <br /> 2 1.4 Hollow Stem Auger Drilling Activities <br /> Hollow stem auger drilling was conducted on September 17 through September 21, 2001, by <br /> Woodward Drilling (State C57 license no 710079) Soil boring ASI was advanced to <br /> approximately 85 feet bgs, soil borings PZia and PZlb were advanced to approximately 80 feet <br /> w 1163931reportslnfs doe 3 <br />