Laserfiche WebLink
t i <br /> 12 December 1995 <br /> AGE-NC Project No. 95-0140 <br /> Page 3 of 5 <br /> Figure 2. <br /> Probing B 1 was located in the approximate location of stakes 14 and 15; probing B2 was located <br /> between stakes 6 and 12 ; probing B3 was placed between stakes 26 and 30; probing B4 was placed <br /> between stakes 31 and 32; and probing B5 was placed between stakes 50, 51 and 53. <br /> Discrete soil samples were collected at five foot intervals using a Geoprobe soil sampler assembly <br /> loaded with pre-cleaned 1.125-inch by 6-inch brass sleeves. Soil samples were preserved by covering <br /> both ends of brass sleeve with Teflon tape, capping, and sealing with duct tape. The samples were <br /> immediately stored in a chilled container and transported to McCampbell Analytical Inc. (MAI). <br /> Selected soil samples were analyzed for total petroleum hydrocarbons, volatile aromatics (benzene, <br /> toluene, ethyl benzene and xylene: BTE&X), chlorinated pesticides and HVOCs in accordance with <br /> EPA methods 5030/8015, 602/8020 and 601/8010, respectively. <br /> 3.2. GROUND WATER SAMPLE COLLECTION AND ANALYSIS <br /> Water samples were collected each probing using a Geoprobe water sampler assembly. Water was <br /> encountered in each probing at a depth of approximately 12 feet. Upon collection, water samples <br /> were transferred to four 40-m1 EPA vials preserved with hydrochloric acid and two 1-liter amber <br /> bottles. Each sample was logged on a chain-of-custody form, placed in a chilled container and <br /> transported to MAI. Water samples were analyzed for TPH, BTE&X, chlorinated pesticides and <br /> HVOCs in accordance with EPA methods 5030/8015, 602/8020 and 601/8010, respectively. <br /> 3.3. EQUIPMENT DECONTAMINATION <br /> Prior to each sampling run, all sampling equipment, probe rods, and brass sleeves used for sample <br /> collection were thoroughly washed in an Alconox solution and rinsed twice with water to avoid cross- <br /> contamination. <br /> 3.4. LOGGING <br /> Soil was extruded from the second brass sleeve and screened for the presence of organic vapors using <br /> a photo-ionization detector(PID: Thermo Environmental 580A, 10.0 eV, calibrated to isobutylene), <br /> and the readings were recorded on the boring logs. The soil was then described in accordance with <br /> the Unified Soil Classification System (see Boring Logs, Appendix B). The probings were backfilled <br /> to grade with Portland cement. <br />