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I20 July 1995 <br /> • AGE-NC-95-0113 <br />' Page 2 of 5 <br />' 3.0. PROCEDURES <br /> 3 1 DRILLING AND SAMPLING <br />' On 16, 17 and 19 May 1995 five sod borings were drilled at the site Two borings (B 1 and 132) were <br /> drilled at an angle of 25* from vertical Each boring was drilled using a truck-mounted HT-55 drill <br /> Irig equipped with hollow-stem augers The drill ng and two-man crew were supplied by Soils <br /> Exploration Service, Inc (SES) of Benicia, California Boring MW-1 was advanced to a depth of <br /> 40 feet, boring B3 was advanced to a depth of 15 feet, boring B-4 was advanced to a depth of 20 <br />' feet Borings B 1 and B2 were advanced to vertical depths of 15 feet, requiring approximately 20 feet <br /> of auger <br />' Soil samples were collected ahead of the drill bit using a split-tube sampler loaded with three pre- <br /> cleaned 2-inch by 6-inch brass sleeves Samples were collected at five-foot intervals, using a 140- <br /> pound hammer to advance the sampler 18 inches The number of blows required to advance the <br /> samples in 6-inch increments was recorded on the boring logs To avoid cross-contamination, the <br /> sampling equipment was washed in an alconox solution and rinsed twice with water prior to each <br /> sample run The augers were steam-cleaned between borings <br /> For each sample, troth ends of the lead sleeve were covered with aluminum or Teflon sheets, capped <br /> and sealed with tape The samples were stored on ice and transported under chain-of-custody to <br /> McCampbell Analytical Inc (MAI) in Pacheco, California Selected soil samples were analyzed for <br /> total petroleum hydrocarbons quantified as gasoline (TPH-g), volatile aromatics (benzene, toluene, <br /> rethyl benzene and xylenes BTE&X) and total lead in accordance with EPA methods 5030/8015m, <br /> 8020 and 6010, respectively Based on the analytical results for total lead in the soil sample from B 1- <br /> 10, it was also analyzed for soluble lead in accordance with California Title 22 method <br /> During drilling, auger,returns and soil sample duplicates were monitored for the presence of organic <br /> vapors using a photo-ionization detector (PID Thermo Environmental 580A, 10 OeV, calibrated <br /> using Isobutylene) <br /> 3 2 LOGGING <br /> Soil was extruded from the second brass sleeve and screened for the presence of organic vapors, <br /> using a PID, and the readings were recorded on the boring logs The soil was then described in <br /> accordance with the United Soil Classification System Boring logs are included in Appendix A <br /> I <br />