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' 20 December 2002 <br /> AGE-NC Project No 95-0185 <br /> ' Page 4 of 7 <br /> ' The soil was then visually described in accordance with the Unified Soil Classification System(see <br /> Appendix C) <br /> ' 2 3 3 Laboratory Analysis of Soil Samples <br /> ' Selected soil samples were logged on a chain-of-custody form, placed in a chilled container and <br /> transported to McCampbell Analytical Laboratory Inc (MAI), a State of California Department of <br /> Health Services (DHS)-certified laboratory, for the following analysis <br /> ' a Total petroleum hydrocarbons quantified as stoddard solvents (TPH-ss), total petroleum <br /> hydrocarbons quantified as motor oil(TPH-mo),TPH-g and TPH-d in accordance with EPA <br /> ' Method 8015 Modified, <br /> • BTEX and the oxygenated fuel additives MTBE,DIPE,ETBE, TAME,TBA,methanol and <br /> ethanol in accordance with EPA methods 8260B, <br /> • The fuel scavengers ethylene dibromide (EDB) and 1,2-dichloroethane (1,2-DCA) in <br /> ' accordance with EPA Method 8260B <br /> ' 2 3 4 Well Completion <br /> Monitoring well MW-5 was completed utilizing a 2-inch diameter casing with 0 020-inch slotted <br />' screen from 10 to 30 feet bsg and blank, 2-mch diameter PVC well casing extending to the surface <br /> The ozone sparge wells were completed with a pre-fabricated 2-inch diameter, polyvinylchloride <br /> (PVC) mess diffuser and blank, 314-inch diameter PVC well casing extending to the surface The <br /> depth of the mess diffusers were from 48 to 50 feet bsg for wells OPS 1B through OSP3B, from 28 <br />' to 30 feet bsg for well OSP1A, from 33 to 35 feet bsg for well OSP2A, and from 38 to 40 feet bsg <br /> for well OSP3A <br />' Each well was installed by placing a PVC well casing assembly through the hollow stem of the <br /> augers to the total depth of the boring The augers were incrementally raised as No 3 Lonestar Lapis <br /> Luster sand(filter pack)was slowly poured down the annulus between the well casing and the inner <br />' wall of the hollow stem auger to approximately two feet above the screened interval <br /> A nominal two-foot bentonite seal was placed above the filter pack to minimize the potential for <br />' grout penetration into the screened section of the well The bentonite seal was formed by pouring <br /> bentonite pellets into the annulus and allowing them to settle on the filter pack Bentonite pellets <br /> were hydrated using five gallons of water and the pellets were allowed to hydrate for a minimum of <br />' one-half hour prior to installation of cement grout <br />' Advanced GeoEnvironmental,Inc <br />