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Work Plan:Environmental Sampling of Soil Export Materials <br /> 1506 N.California St. <br /> Page 2 <br /> plan is included in Appendix B. Personnel working at the Site will have completed 40 hours of classroom <br /> training (OSHA 29 CFR 1920.120, HAZWOPER) and 24 hours of supervised field training concerning <br /> hazards that may be encountered at hazardous waste sites. Additionally, field personnel working at the <br /> Site will participate in a medical monitoring program. <br /> 3.3 DIRECT PUSH BORING PROCEDURES <br /> Twenty direct push borings will be advanced on the Site. The proposed boring locations are shown on <br /> Figure 3 in Appendix A. All of the borings will be advanced to approximately 16 feet below ground <br /> surface (bgs): groundwater is anticipated to be between 40 and 50 feet bgs. <br /> Continuous core soil samples will be collected from the boring with a 1.75-inch O.D., 4-foot long core <br /> barrel fitted with a clean, single use, polyethylene liner. The soil sampling equipment will be cleaned <br /> prior to collecting the sample using laboratory-grade, non-phosphate detergent and deionized water and <br /> double rinsed with deionized water. During the sampling, the core barrel will be driven in 4-foot <br /> intervals. The sample liner will be extracted from the core barrel and used for geological logging and <br /> field observations. The soil samples will be logged according to the Unified Soil Classification System <br /> (USCS). Portions of the soil samples will be placed in polyethylene bags and checked with a <br /> photoionization detector (PID) for the presence of volatile hydrocarbons. Geological logs will be <br /> prepared containing field observations including soil type, estimated moisture content, PID <br /> measurements, and the presence of staining or odor. Soil samples will be collected from the borings for <br /> laboratory analyses at 3.5, 10, and 16 feet bgs, or wherever contaminated soil is identified, for a total of <br /> three soil samples per boring. Any soil cuttings with identified contamination using field methods will be <br /> placed in a 55-gallon drum, sealed, labeled, and left on-site to await disposal pending results of the <br /> laboratory analyses. Following the collection of the soil samples, the borings will either be abandoned <br /> with drill cuttings and remaining void space will be grouted to surface with neat cement, or the borings <br /> will be completely grouted to the surface. <br /> Each soil sample collected for laboratory analyses will be cut from the liners. The liners will be sealed at <br /> the ends with Teflon® sheeting, capped, and labeled. The samples will be placed in a cooler chilled with <br /> Blue Ice® and delivered under chain-of-custody procedures to a California certified laboratory for <br /> analyses. <br /> 3.4 LABORATORY ANALYSES <br /> Upon completion of the fieldwork, the soil samples will be delivered under chain-of-custody procedures <br /> to a state certified laboratory for analyses. The soil samples will be composited by the laboratory at a 4- <br /> to-1 ratio based on depth and location for a total of 15 composite soil samples (5 composite soil samples <br /> per depth). The composite soil samples will be analyzed for total petroleum hydrocarbons (TPH) <br /> quantified as gasoline, diesel, kerosene, and motor oil by EPA Method 8015M, volatile organic <br /> compounds (VOCs) by EPA Method 8260B, organochlorine pesticides by EPA Method 8081B, <br /> polychlorinated biphenyls (PCBs) by EPA Method 8082, and CAM 17 Metals by EPA Methods 6010B <br /> and 7417A. <br /> lkkii�6 <br /> �.a CONDOR <br />