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City of Stockton Draft Amended Report of Waste Discharge(AROWD) <br /> Austin Road Landfill Work Plan <br /> The rig and the hollow stem augers will be decontaminated following the procedures in Section 2.2.2 <br /> prior to drilling the first boring and after each boring is completed. The washdown will be performed <br /> at the on-site decontamination facility. <br /> Groundwater Sampling <br /> Depth discrete groundwater samples will be collected at the specified aquifers in the borings of each <br /> transect using a Hydropunch®sampler. The Hydropunch®is a stainless steel sampling device which <br /> is hydraulically driven ahead of the hollow-stem augers into undisturbed soil at a sufficient distance <br /> to perform groundwater collection(11h-2 feet). <br /> For sample collection,the Hydropunch®is fitted with a dedicated stainless steel tip which seals the <br /> bottom opening of the sampler during advancement and then releases as the sampler is retracted to <br /> expose a screened opening. After the sampler is retracted about one foot,groundwater enters an <br /> internal chamber through a synthetic,reed-type check valve. After a waiting period sufficient to <br /> allow the internal chamber to fill(field judgment will be used to expedite this process),the sampler is <br /> retrieved. <br /> At the ground surface,sampled groundwater will be transferred from the internal chamber to volatile <br /> organic compound (VOA)sample vials as described in Section 2.2.1.5. Results from VOC sampling <br /> will have a 24-hour turnaround. QA samples will be taken as prescribed by EPA guidance. The <br /> Hydropunch®sampler will be decontaminated prior to its next use as described in Section 2.2.2. <br /> Aquifer Soils by Split-Barrel Core Samplers <br /> Soil samples will be collected using 5-foot long,split-barrel core samplers on the initial borings of each <br /> transect. The split-barrel samples will be collected continuously from approximately 10 feet above the <br /> water table(at depths starting approximately 90 to 100 feet below ground surface) and extending <br /> down to approximately the total depth of 180 feet. The field geologist will open the sampler,log the <br /> lithology,and retain the samples in heavy-duty,zip lock baggies. The samples will contain soil of <br /> similar lithology over approximately 1-ft depth intervals. These samples will then be labeled with the <br /> sample location and depth interval. <br /> The split-barrel samplers will be advanced at the same time as the drill hole to collect relatively <br /> undisturbed samples(except for the first 1-2 feet which will be advanced through the material <br /> previously disturbed by the Hydropunch®groundwater sampler). Lithologic observations will be <br /> recorded on boring logs by the onsite geologist. The Unified Soil Classification System (USCS)will be <br /> used to describe lithologies,and symbols will be consistent with those used previously by CDM at the <br /> French Camp Landfill. <br /> 2.2.1.3 Monitoring Well Installation <br /> After completion of the Hydropunch®program delineating the edge of the contaminant plume,two <br /> monitor well clusters will be installed at the approximate locations depicted in Figure 2. These wells <br /> will be completed in the shallow and deep aquifer zones,installed utilizing the air rotary/casing <br /> hammer drilling technique. The drilling will be performed as described below and in accordance <br /> with procedures described in Section 8.1.6.1.8,Air Rotary Method,of EPA(1987). <br /> W:\REPORTS\STOCKTON\AUSTIN\WORKPLAN.DOC Page 6 <br />