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Nail.E4 m tial} urd Gruvudu rrLr III tir,hF it <br /> ( mc-p r,C it N N. <br />' (13'UI'rufu tir NIOLklon CA <br /> I aur v) 21 1991 <br /> I'rbc 7 <br />' laboratory) the soil samples %ill be anahzed using U 5 CPA Methods and California-approved <br /> method~ folloN%i ng quality as5urancc inLa,,ures Laborator\ analyses are dlscusud 1n SLLtIOfi 1 S <br /> 3 4 SINIULPROBE SANIFUNG <br />' The 5 foot long, split spoon simpler Evill be used iii the saturated zone from the water table to a total <br /> depth of approvrniat(.ly 70 feet bgs to investigate the lithologic profile of the site The vertical <br /> distribution of contaminants (if present) within the saturated zone will bi- Investigated b\ using a <br />' Simulprobe sampling, device The Simulprobe sampling dc\ice «ill be dtployed nn plate of the spht- <br /> spoon sampler to collect soil arid vround%%ater simples at signifrcantl\ different litholotgacal zones in the <br /> saturated zone It is anticipated that no more than three Simulprobe soil and ground tater samples \%III <br /> be colleLtcd from the saturated zone The sampler \N ill be cleaned before collecting each Sample u-ing <br />' the procedure described in Section 3 3 above <br /> Once the borehole has been drilled to the planned depth the Simulprobe sampler will be fitted xi Ith three <br />' brass tube- much like a California split-spoon and then hammered into the formation to retrieve a soil <br /> sample Tlne Simulprobe also has an integrated groundwater sampling systenn that through a filter <br /> screen N\ill allo\% groundNNater to enter the sampler at the same depth the soil N%ill be collected from A <br /> polyprop)leve sheath placed around the sampler prior to deployment N\it l pre\ent the entrance of <br /> I grouiid\�ater from above the desired sampling depth The sheath Ni ill break NN hen the sampler iti <br /> hammered into the formation The filter screen will be exposed to the formation b\ Pulling tine samplLr <br /> up apprommately three inches The water \\ill be routed throu�_h the sampler and past the soil Samples <br /> «ith Teflon tubine into a (,roundwater collection chamber The sampler iN ill then be raised to the surface <br /> on drill stem dissassembled and the soil and groundwater samples removed Each ground,,Nater sannplc <br /> «ill b( gravith drained from the device into the sample containers Samples N%ill be handled in <br /> accordance N\ith the -tandard procedures described above In Section > ; of this report <br /> 35 LABORATORY ANALYSIS <br /> The Soil samples collected from the horin<g- will be ana]Nzed for TPH-G bN Method 5030/1-UfT for <br /> Benzene Folii(.ne Cth}1 Buizcne arid Xylene (BTEX) EPA Method 8020 and for gasoline <br /> oyygenates/additive,, by 1 PA Method 8260 The gasoline o\vgcnafes/additne- include tifetiivl teitiarv- <br /> Butyl Ether (M FBE) Ethanol tertiary-Butanol D1-isoprop\l ether (DIPC) EthN I tertlarN-Butyl Ether <br /> (ETBE) and tertiar\-amyl Methyl Ether (TAMEI fhe �(aroundwatcr sampler collected from the <br /> Simulprobe. will be anal}zed for TPl l-G by Method 50 ti0/LUC'F for BTEX b. EPA Method 602 and for <br /> gasoline oxygenates/additives by EPA Method 8260 The, anaMical methods acid analy tical detection <br /> limits are presented in Table 1 <br /> CONDOR <br /> I <br />