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kn KLEINFELDER <br /> Ten of the push probe borings were pneumatically advanced using a 4 foot steel core barrel. Soil <br /> samples were continuously collected by inserting a new four foot acetate liner into the core <br /> barrel prior to each drive. Soil samples obtained for potential chemical analyses were collected <br /> at desired intervals by removing the acetate liner and cutting out the desired 6-inch interval. <br /> Probe location PP-8 was advanced using a stainless steel hand auger. Soil samples were obtained <br /> by slide hammering a 2-inch diameter by 6-inch long stainless steel tube into the soil at the <br /> desired sampling depths at this location. The stainless steel tubes and acetate soil sample <br /> containers were then removed from the boring and sealed with Teflon° sheeting and tight-fitting <br /> plastic end caps. <br /> The stainless steel hand auger and down-hole pushprobe equipment was decontaminated <br /> between sample and probe locations with a Liquinox® (laboratory-grade detergent) and potable <br /> water wash and a distilled water rinse. New stainless steel tubes used in the hand auger location <br /> were used for sample collection were also decontaminated using the same methodology. <br /> Groundwater samples were obtained from eight of the eleven push probe borings (PPs-1, 3, 5, 6, <br /> 7, 8, 9, and 10). The groundwater samples were collected using a positive displacement check <br /> valve attached to new polypropylene tubing. The positive displacement was generated manually <br /> using a piston-like motion. New tubing was used at each sampling location. Slotted PVC was <br /> placed within each of the eight push probe boreholes to help decrease turbidity and facilitate <br /> collection of the groundwater sample. The groundwater samples were transferred into pre- <br /> cleaned laboratory grade bottles. <br /> 4.3 SAMPLE HANDLING AND CHEMICAL ANALYSES <br /> After collection, the soil and water samples were immediately stored in an iced cooler. The <br /> samples were transported under chain-of-custody control to Kleinfelder's office and then <br /> transported by courier in a sealed container to Sequoia Analytical Laboratories of Sacramento, <br /> California. Sequoia is certified by the California Department of Health Services to perform the <br /> requested analyses. <br /> A total of 22 soil samples and 8 groundwater samples were submitted for chemical analyses. <br /> One soil sample from boring PP-9, three from PP-11, and two soil samples from the remaining <br /> probe locations were submitted for analysis. One groundwater sample from each pushprobe boring, <br /> with the exception of PPs- 2, 4, and 11, were also submitted for analyses. The twenty-two soil <br /> samples and eight groundwater samples were analyzed for the following: <br /> • Ammonia as N by EPA Method 350.3 <br /> • Nitrate as N by EPA Method 300.0 <br /> • Total Kjeldahl Nitrogen by EPA Method 351.2 <br /> A illustration of the sampling locations is shown on Plate 2 and a summary of the soil'and <br /> groundwater sampling results is located in the attached Table 1. <br /> 43851.E01/ST05R158/DH:Iv Page 6 of 12 <br /> ©2005,Kleinfelder,Inc. February 9,2005 <br />