Laserfiche WebLink
Z M1 <br /> S + i <br /> 05 April 1996 <br /> AGE-NC Project No 95-0111 <br /> Page 2 of 6 <br /> Prior to March 1996, ground water samples had been collected on three occasions from each well <br /> at the site The depth to ground water at the site is approximately 6 feet, with-a prevailing flow <br />' direction toward the north to northeast <br />' 3.0. PROCEDURES <br /> 3 1 DRILLING AND SAMPLING <br />' On 26 February 1996, two borings were drilled at the site to a depth of 15 feet below surface grade <br /> (bsg) and completed as ground water monitoring wells MW-5 and MW-6 Well MW-4 was over- <br /> drilled, then the casing, filter, pack, bentornte`plug and grout seal were replaced <br /> All drilling was performed using a truck-mounted CME 75-HT drill rig equipped with 8 25-inch <br />' diameter hollow-stem augers The drill rig and two-man crew were supplied by Soil Exploration <br /> Services (SES) of Benicia, California The locations of the borings are shown on Figure 2 <br /> Samples were collected at five-foot intervals in each boring using a split tube sampler loaded with <br /> three clean, 2 by 6-inch brass sleeves A 140-pound hammer was used to advance the sampler 18 <br /> inches, the number of blows required to advance the sampler in 6-inch increments was recorded on <br />' the boring logs All sampling equipment was washed in an Alconox solufion and rinsed twice with <br /> water prior to each sampling run <br />' For each sample, both ends of the leading sleeve were covered with Teflon sheets, capped and sealed <br /> with tape The samples were stored in a chilled container and transported under chain-of-custody to <br />' McCampbell Analytical, Inc (MAI) in Pacheco, California Each sample was analyzed for total <br /> petroleum hydrocarbons quantified as gasoline and diesel (TPH-g and TPH-d) and volatile aromatics <br /> (benzene, toluene, ethyl benzene and xylenes BTE&X) in accordance with EPA methods <br />' 5030/8015m and 602, respectively <br /> During drilling, auger returns were monitored for the presence of organic vapors using a photo- <br /> ionization detector (FID Thermo Environmental 580A, 10 0 eV, calibrated to isobutylene) Auger <br /> returns were then placed on plastic sheeting and stored on-site pending laboratory analysis <br /> I3 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 Unified Soil Classification System (see Boring Logs, Appendix A) <br />