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%t/ %Wok <br /> y <br /> Ms. Lori Duncan <br /> October 3, 2003 <br /> Page 5 of 7 <br /> vertical extent of the dissolved plume has been defined, Ground Zerp proposes to advance one soil <br /> boring (Figure 6) to a depth of up to 75 feet bgs in the vicinity of the former UST using a direct <br /> push drilling rig equipped with a dual-tube system. After pushing the outer rods to a depth of <br /> approximately 25 feet to seal off the uppermost water-bearing unit, a CPT probe will be pushed to a <br /> depth of up to 75 feet bgs to characterize lithology beneath the site. After lithology has been <br /> characterized through CPT, a second hole will be advanced for the purpose of collecting discrete <br /> groundwater samples. Groundwater samples will collected using a hydropunch-style sampler from <br /> any potential aquifers (high-permeability zones) identified through soil classification. <br /> If preliminary hydropunch samples are positive for gasoline constituents, we will re-mobilize to the <br /> site at a later date to install a deep monitoring well, the screened interval to be determined from <br /> preliminary results. This well will not be installed if the discrete sampling data indicate that deeper <br /> zones are not impacted. <br /> Well Development,Surveying and Groundwater Sampling <br /> The elevation of the top of the casing in each well will be surveyed to an accuracy of 0.01 feet. A <br /> minimum of 24 hrs after completion, an experienced field technician will measure static depth to <br /> water and then develop the wells by pumping and surging until turbidity is minimized. A minimum <br /> of five casing volumes will be purged from each well. <br /> Groundwater samples will be collected after pH, temperature, and electrical conductivity have <br /> stabilized and the wells have recharged to minimum of 80% of static levels. Groundwater samples <br /> will be immediately placed in an iced cooler and submitted to a State-certified laboratory under <br /> chain of custody protocol for analysis of TPHg (EPA 8015B), BTEX (EPA 8021B), and <br /> oxygenated gasoline additives (EPA 8260B). The EPA 8260B scan will be expanded to include <br /> ethylene dibromide (EDB) and 1,2-dichloroethane (1,2-DCA) pursuant to Regional Board <br /> requirements. <br /> Water generated from well development and sampling will be contained in labeled DOT approved <br /> drums. The drums will be stored on site pending laboratory results and the development of disposal <br /> options. <br /> Investigation of Pumping Influence of Nearby Production Wells <br /> Evaluation of Analytical Results <br /> Groundwater samples were collected from the facility and the two nearest domestic wells on <br /> September 29, 2003. Samples were collected at the spigot nearest the well after opening the spigot <br /> for approximately 15 minutes at each location. Samples were collected into 40-m1 glass vials <br /> supplied by the laboratory. The samples were transported under chain of custody protocol to Argon <br /> Laboratories (FLAP 2359) for analysis of TPHg, BTEX, and oxygenated gasoline additives using <br /> EPA methods 8015B, 802113, and 8260B,respectively. <br /> woo 1 se y.chYr epo r t sl w o rk p I a n.m w s <br />