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SECTION 4.0 SITE INVESTIGATION ACTIVITIES <br /> feet below the top of the water table Samples were collected using the KabisTM II sampler for <br /> 4-inch wells, as described in Appendix B The discrete samples at each depth were collected in <br /> three 40-milliliter vials (40 mil VOAs) The 40 nil vials are screwed into the bottom of the <br />' stainless-steel lid on top of the KabisTM sampler Groundwater fills into each vial via stainless- <br /> steel sample ports located on top of the KabIsTM sampler lid As long as the KabisTM sampler <br /> remains stationary in the well, groundwater will continue to fill the vials and then cascade from <br /> the vials into the KabisTM sampler reservoir The vials and reservoir fill in approximately 10 <br /> minutes <br /> The discrete groundwater samples were analyzed at the Stockton Yard site using a mobile <br /> laboratory operated by Environmental Laboratories (ONSITE) for the following analyses <br /> TPH-g in accordance with EPA Method 8015 modified <br /> • BTEX and MTBE in accordance with EPA Method 8260B <br /> Nitrogen as nitrate and sulfate analyses in accordance with EPA Method 300 0 were conducted <br /> by a subcontractor to ONSITE (Curtis and Tompkins) During collection of the discrete samples, <br /> URSGWC monitored for the following groundwater quality parameters pH, conductivity, <br /> temperature, dissolved oxygen, and turbidity The field monitoring data are recorded on well <br /> sampling logs included in Appendix A <br /> Quarterly groundwater monitoring at Stockton Yard was conducted during April 1 and 2, 1999 <br /> by PSI under contract to Caltrans The routine periodic groundwater monitoring at the site <br /> included measunng depth to groundwater in the 12 onsite groundwater monitoring wells and two <br /> vapor monitoring wells, purging of each well, and collecting groundwater samples for analytical <br /> testing The depth-to-groundwater measurements were used by PSI to evaluate groundwater <br /> surface elevations, and horizontal gradients Depth to groundwater measurements and analytical <br /> data for the April 1999 monrtonng event are included in Table 3-3 The results for the quarterly <br /> monitoring event are discussed along with the discrete vertical sampling in Section 5 0 <br /> 4.3 SLUG TEST PROCEDURES <br /> Single-well hydraulic tests (slug tests) were conducted at three wells at the Stockton Yard site <br /> Slug tests consisted of lowenng a mandrel into each of the three wells to cause an instantaneous <br /> rise in water level The fall in water level to static water level conditions was measured using a <br /> water level meter to the nearest 0 01-foot Once static water level conditions existed, the mandrel <br /> was removed from the water column to cause an instantaneous fail to water The subsequent <br /> recovery of the water level to static conditions was measured with a water level meter The data <br /> were down loaded in the AgtesolvTM groundwater modeling program to the estimate hydraulic <br /> conductivity for each slug test The data were analyzed using the Bouer and Rice Method for <br /> S 1PROJ141040100044SYYARD4MAINTYAROSIIDOC 4-3 URS Greiner Woodward Clyde <br />