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U i <br /> l <br /> impact. - <br /> Soil samples will be collected from the boring for lithologic logging and field screening. The samples will <br /> be collected in a 5-footer-1�5--inch O.D._core sampler equipped with an acetate liner. Soil samples will be <br /> collected at approximate five-foot intervals ani a f fervais where staining or color or texture changes are <br /> noted.The field staff will examine representative portions of the soil samples and prepare soil boring logs <br /> that describe the encountered soil in general accordance with the American Standards for Testing <br /> Materials(ASTM) 2488-06 and the Unified Soil Classification System (USCS). The soil boring logs will <br /> indicate the depth of the various strata, and record other pertinent information regarding the advancement <br /> and sampling of each borehole. <br /> Each soil sample will be field screened for volatile.organic vapor's with a photoionization detector(PID)or <br /> similar instrument. The field screening readings will be recorded on the soil boring log. A portion of each <br /> soil sample will be.retained for.potential laboratory analysis. The samples will be collected in an acetate <br /> liner and the liners will be cut at the desiredm <br /> saple interval and sealed with Teflon®tape and plastic caps 4 <br /> at each end. All samples will be stored in an ice chest cooled to approximately 4 degrees Celsius(°C)with <br /> ice. <br /> Upon completion of the soil boring,the monitoring well (proposed well,MW-11)will be constructed with no <br /> more than 5 feet of 0,_010 inch slotted Schedule 40(Sch-40)2-inch diameter polyvinyl chloride(PVC). The <br /> well screen will be located from approximately 20 to 25 feet bgs. Approximately 20 feet of blank Sch-40, <br /> 2-inch diameter-P_VC.casing will be located from 20 feet bgs to approximately 6-inches below grade. The <br /> north side of the casing will be notched to facilitate consistent groundwater monitoring data acquisition. <br /> The boring annular space will be filled with appropriate filter sand extending from the maximum explored da <br /> th t <br /> depo approximately four feet bgs. The annular space will e i led with bentonite pellets or chip frs om <br /> approximately four to three feet bgs. Above the bentonite seal the annular space will be filled with <br /> Portland type II ceme gro)or grout/bentonite slurry to approximately 6-inches below grade. The <br /> surface completion will consist of a traffic rated well box set in concrete with a 2-inch diameter locking well <br /> cap. Drill cuttings will be stored on-site in 55-gallon drums pending laboratory results. Soil cuttings will be <br /> profiled and disposed of at an appropriate facility within 90 days: <br /> At least 72 hours after the installation of the monitoring well, the newly installed monitoring well will be <br /> surged with a 2-inch nominal diameter surge block-to_remove fines from the filter pack. Subsequent to <br /> surging, the well will be developed using centrifugal pump until`the produced water is relatively sediment <br /> free or until a volume equivalent to at least 10 well casings of water have been removed, which ever <br /> occurs first. All purge water will be stored in 55-gallon drums and staged on-site pending laboratory <br /> analysis for disposal. The development of the well will be performed a minimum of 72 hours after <br /> installation. <br /> F <br /> At least 72 hours after completion of the monitoring well surging and development,ATC will return to the <br /> Site to collect groundwater samples. The newly installed well will be sampled along with the other <br /> mandated wells as part of the semi-annual monitoring program. Prior to collection of groundwater I <br /> samples, dedicated polyethylene sample tubing will be inserted to the depth equivalent to midway down ` <br /> the screened interval so as not to disturb the standing water column above the screened interval and not ll! <br /> to stir up colloidal particles or sediment. The tubing will then be connectedlo a peristaltic pump and a <br /> Horiba Water Quality Monitor Model U-22XD meter(or equivalent) with a flow-through cell. <br /> Groundwaterwill be slowly pumped while simultaneously monitoring the DTW and adjusting the pump rate <br /> until no or minimal drawdown is observed. Drawdown greater than 0.33 ft results in a reduction of <br /> pumping rate or a temporary shut down. Once the pumping rate is stabilized at a rate not exceeding 0.54'=A' f J� <br /> L/min, temperature, pH, specific conductance;dissolved oxygen, and turbidity will be measured. When <br /> U � Additional Investigation Workplan Addendum <br /> Quik Stop No. 132,Stockton,CA I <br /> ...<. ..<. ,.<. July 28,2009 <br /> t <br />