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r Work Plan-Soil and Groundwater Investigation <br /> New Jernsaletn School <br /> October 2G,1998 <br /> Page-3- <br /> The soil cuttings from the borings and steam cleaning effluent will be placed in 55-gallon druJns, sealed, <br /> labeled, and left on site pending laboratory analyses. Disposal of hazardous materials, if any, will be the <br /> responsibility of the property owner. <br /> V <br /> One groundwater sample will be collected from each borehole using a Hydropunch groundwater sampler. <br /> The Hydropunch groundwater sampler is designed to be hydraulically pushed into the aquifer at the <br /> bottom of a borehole to collect a groundwater sample from a discrete zone. The sampler utilizes a <br /> sealed, watertight, stainless steel sample chamber and PVC screen that is isolated from the surrounding <br /> environment as the sampler is advanced. When the desired depth for collection of a groundwater sample <br /> r is reached, the sample chamber is opened by pulling back on the body of the sampler, exposing the <br /> screen. When the screen is full, a small diameter stainless steel bailer is lowered into the push rod and a <br /> groundwater sample is retrieved from the sample chamber. The bailer sample will be inspected for free <br /> �.. product, odor, and sheen. The sample will subsequently be poured into laboratory-supplied containers. <br /> The soil and groundwater samples will be stored in a cooler chilled with Blue Ice and delivered within 24 <br /> hours of collection, under chair-of-custody procedures, to GeoAnalytical Laboratories, in Modesto, <br /> California (a California State Certified laboratory). The soil samples will be analyzed using U.S. EPA <br /> 4 Methods and California-approved methods following quality assurance measures. Laboratory analyses <br /> are discussed in Section 3.7. <br /> Upon completion of the drilling and sampling, the boreholes will be grouted to the ground surface with <br /> cement slurry containing approximately three to five percent bentonite. The slurry will be tremied into <br /> the borehole to avoid bridging. All decontamination rinsate produced during the fieldwork will be <br /> `r placed in a 55-gallon drum, sealed, labeled, and left on site pending laboratory analyses. <br /> 3.4 MONITOR WELL INSTALLATION <br /> V <br /> The monitor wells (MW1, MW2, and MW3) will be drilled by Spectrum Exploration. Tine proposed <br /> monitor well locations are shown on Figure 2, Appendix A. The monitor well boreholes will be drilled <br /> and sampled using the same procedures as for the soil borings. The boreholes will be drilled to a depth <br /> of approximately 23 feet bgs. <br /> 3.5 MONITOR WELL CONSTRUCTION <br /> The monitor wells will be constructed with 2-inch O.D., Schedule 40, flush-threaded, machine-slotted <br /> PVC screen (slot size 0.020) extending from a depth of approximately 8 feet to 23 feet bgs. A flush- <br /> threaded PVC bottom cap will be placed at the bottom of the screen. Blank PVC casing will be installed <br /> above the screen to the ground surface. The well casing will be stearin-cleaned on site prior to use. No <br /> glue or solvents will be used in the construction of the wells. <br /> y A sand pact: of 43 Monterey sand will be placed in the annular space to approximately one foot above <br /> the screen- Approximately two feet of bentonite pellets will be placed above the sand to form a <br /> protective seal. The bentonite will be hydrated using potable water. A seal of neat cement will be <br /> ' poured in the annulus from the bentonite seal to the ground surface and a locking, traffic box will be <br /> installed at the ground surface. The proposed well design is shown in Figure 3,Appendix A <br /> r <br /> h <br /> L� <br /> CONDOR <br /> it <br />