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URS <br /> Ms Vickie McCartney, REHS Page 3 <br /> . San Joaquin County Environmental Health Department <br /> ARCO 2186 <br /> Drilling and Monitoring Well Installation <br /> On April 13 through April 16 and April 19 and 20, 2004, Gregg Drilling, of Martinez, California, drilled <br /> four soil borings (BH-1 through BH-4) and installed one 2-inch diameter groundwater monitoring well <br /> (MW-8), one 4-inch SVE well (VW-4), and one 2-inch AS well (AW-1) at the site Prior to drilling, <br /> utility clearance was obtained from Underground Service Alert (USA) Cruz Brothers Locators, a <br /> private utility location contractor, cleared proposed boring locations to ensure that private utilities <br /> would not be damaged during drilling Boring locations were cleared to a depth of 5 feet below ground <br /> surface (bgs) with an air knife device prior to drilling Boring/well locations are shown on Figure 2 <br /> The borings were drilled using a drill rig equipped with 8- and 10-inch-outside-diameter (OD) hollow- <br /> stem augers (HSAs) to accommodate the installation of 2- and 4-inch diameter groundwater monitoring <br /> and remediation wells The total depth of the borings ranged from approximately 40 to 135 feet bgs <br /> First groundwater was encountered at approximately 48 feet bgs in the borings During the drilling of <br /> the boring for MW-8 (BH-3), the driller's sample hammer cable broke off at approximately 112 feet bgs <br /> In an attempt to recover his sample hammer, the driller had to over drill to 116 feet bgs Based on driller <br /> observations, the lithology in the depth interval from 112 to 116 feet bgs was thought to be saturated <br /> sand However, because the interval was not sampled, the lithology could not be confirmed Since the <br /> lithology could not be confirmed to the depth interval from 112 to 116 feet bgs in boring 1314-3 <br /> (Itthology data were needed for well-screen placement), the boring was backfilled with neat cement <br /> grout from the bottom to the ground surface Boring BH-4 was drilled approximately 5 feet to the east- <br /> northeast of BH-3 to install well MW-8 Boring BH-4 was cored continuously from 108 feet bgs to 135 <br /> feet bgs for lithologic characterization ' <br /> Soil samples were collected at 5-foot intervals using a modified California split-spoon sampler from 5 <br /> feet bgs to the total depth in the borings drilled for wells VW-4 and AW-1 Soil samples were collected <br /> at 5-foot intervals using a modified California split-spoon sampler from 5 feet bgs to 75 feet bgs in the <br /> boring for well MW-8, most of the depth interval from 75 feet bgs to 135 feet bgs was cored -- <br /> continuously Soils were logged by a URS geologist according to the Unified Soil Classification System <br /> No hydrocarbon staining or odor were noted for any of the soil samples A maximum photoionization <br /> detector (PID) reading of 22 6 parts per million (ppm) was noted near the capillary fringe during the <br /> drilling of well AW-1 During the drilling of well MW-8, a maximum PID reading of 8 9 ppm was noted <br /> at a depth of 54 5 feet bgs During the drilling of well VW-4, all PID readings were noted as 0 0 ppm <br /> Soil samples were submitted for laboratory analysts from each soil boring Soil samples pgre analyzed V-11- <br /> for depths of approximately 50 and 97 feet bgs for MW-8,40 feet bgs for VW-4,and, 'feet bgs for /I Sas <br /> AW-1 Soil samples were sealed in 2-inch-diameter brass sleeves with Teflon® squares and plastic end <br /> caps Samples were then labeled and placed on ice in a cooler, pending delivery to Sequoia Analytical <br /> Laboratories in Petaluma, California Soil samples were analyzed for gasoline range organics (GRO), <br /> benzene, toluene, ethylbenzene, and total xylenes (BTEX), and for fuel oxygenates/additives (including <br /> MtBE) by U S EPA Method 8260B <br /> K IWproeessU5 BP ARC010218612004 Assessmentleeport 04 doe <br />