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analyzed for the presence VOCs in accordance with EPA Method 8260B and TPH-cc in accordance <br /> with EPA Method 8015M. <br /> Up to nine soil samples (three per boring) will be collected from borings B12, B13 and 1314. One <br /> soil sample from each boring will be selected for laboratory analysis based on field observations <br /> and at areas where photoionization detection (PID) readings are elevated above background.The <br /> selected soil samples will be analyzed for the presence VOCs in accordance with EPA Method <br /> 826013, TPH-cc in accordance with EPA Method 8015M, polychlorinated biphenyls (PCBs) in <br /> accordance with EPA Method 8082, Title 22 Metals in accordance with EPA Method 6010/200.7, <br /> and semi-volatile organic compounds (SVOCs) and polycyclic aromatic hydrocarbons (PAHs) by <br /> Selective Ion Monitoring (SIM) in accordance with EPA Method 8270C. <br /> 5.4 Proposed Monitoring Well Installation Methods <br /> Groundwater monitoring well borings MW-1, MW-2 and MW-3 will be advanced to a total depth <br /> of 35 feet bgs using a truck-mounted HSA drill rig. A groundwater monitoring well will be <br /> constructed within the auger column of borings MW-1, MW-2 and MW-3 to a depth of 10 feet <br /> below depth to groundwater, which is anticipated to be at 25 feet bgs, for a total well depth of <br /> approximately 35 feet bgs. The monitoring wells will consist of a 15 foot section of 2-inch <br /> diameter, 0.020-inch slotted schedule 40 polyvinyl chloride (PVC) screen at the terminal end, <br /> extending approximately 10 feet below depth to groundwater and five feet above depth to <br /> groundwater;and 2-inch diameter schedule 40 PVC blank riserto the ground surface.The terminal <br /> end of each monitoring well will be fitted with a PVC end cap and the PVC screen and riser <br /> segments will be attached with threaded connections. The well casing will be suspended <br /> approximately 6-inches above the terminal depth and the boring annulus will be backfilled from <br /> the terminal depth upwards with sand to approximately 2 feet above the well screen, followed by <br /> a 3-foot bentonite seal and cement grout from the top of the seal to the ground surface. During <br /> well construction the wells will be periodically surged to settle the well screen filter pack. A flush- <br /> mounted, traffic-rated well vault will be emplaced to provide access to the wellhead. <br /> Details of the monitoring well construction are provided in Figure 3. <br /> Additional Site Assessment Work Plan <br /> Heliostockton Property <br /> 434 Dr.Martin Luther King Jr. Boulevard <br /> Stockton,California <br /> Partner Project Number SM17-191672 <br /> RWQCB Case#:392004 <br /> January 9,2018 <br /> Page 11 <br />