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Subsurface Investigation Report <br /> Installation of Wells MWS,MW6, and MW7 <br /> 640 N El Dorado Street, Stockton, CA <br /> I <br /> 2.0 PROCEDURES FOR ADDITIONAL INVESTIGATION <br /> 21 Permitting and Protocols <br /> I Prior to initiating fieldwork, well installation permits were obtained from E14D All fieldwork was <br /> performed in accordance with Ground Zero's Site Safety Plan and Quality Assurance/Quality Control <br /> Plan <br />' 2.2 Drilling, Soil and Groundwater Sampling <br /> Between May 6 and May 23, 2003, Ground Zero personnel supervised the drilling and sampling of three <br />' soil borings and the installation of three groundwater monitoring wells Fisch Environmental (C57- <br /> 683865) conducted the drilling and well installation Three continuous-core pilot borings (SB9, SB10 <br /> and SBI I) were advanced using a "direct-push" drilling rig for lithologic logging and subjective <br />' evaluation of soil and groundwater contamination Three groundwater monitoring wells (MWS, MW6 <br /> and MW7) were subsequently installed at the same locations as the pilot borings All fieldwork <br /> conducted at the site was performed under the supervision of field geologist Sean Garvey and project <br />' manager John Lane, a California Registered Geologist Ms Lori Duncan of EHD conducted grout <br /> inspections and observed field activities Figure 3 shows the locations of the pilot borings and <br /> monitoring wells <br /> Borings SB9, SB 10, and SB 11 were advanced to approximately 50 feet below surface grade (bsg) <br /> Where possible, soil samples were collected continuously using a 4-foot long core sampler lined with <br />' new 2 inch diameter polyethylene sleeves A phototonization detector (PID) was used to monitor the <br /> presence of VOCs in the soil Discrete groundwater samples were also collected from each boring by <br /> driving a groundwater sampling device to the desired depth, then retracting the probe rods to expose the <br />' screen to the formation A 0 17-inch diameter PTFE tube equipped with a stainless steel check valve was <br /> then inserted into the rods to the bottom of the of the sampler Water was extracted from the boring by <br /> creating a positive displacement effect within the tubing, forcing the water sample to the surface where it <br />' was collected directly into the appropriate sample containers <br /> Soil_and-groundwater samples selected_for laboratory analyses,_based on field observations and field <br /> screening results, were sealed, labeled, and immediately placed in an ice chest cooled to a temperature of <br />' approximately 4° Centigrade The-samples were submitted under chain of custody protocol to Argon <br /> Laboratory(FLAP 2359)or possible analysis <br />' Each completed direct push boring was backfilled to the ground surface with neat cement grout All <br /> drilling and sampling equipment was decontaminated prior to use and between sample collection by <br /> washing with a laboratory grade detergent and rinsing with water to minimize the possibility of cross <br />' contamination Waste soil and water generated during drilling and well installation activities were placed <br /> into properly labeled DOT approved storage containers, and were subsequently transported off-site for <br /> disposal at licensed facilities The soil was transported to Forward Landfill in Manteca and the water <br /> t was transported to the Riverbank Oil Transfer Station Copies of the non-hazardous waste manifests are <br /> included in Appendix 1 <br /> 1 <br /> -2- <br /> 1 <br />