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Groundwater investigation Report <br /> 1 • Country Club Drain System Project City of Stockton Municipal Utilities Department <br /> October 2 2003 <br /> Page 6 <br /> ' The investigation included the advancement of 15 borings (GP-1 through GP-15) with direct push <br /> technology (Geoprobeo) along portions of the MUD storm drain located along Country Club Blvd and <br /> Plymouth Road Four borings were advanced downgradient of the Exxon Mobil site, eight borings were <br /> advanced crossgradient and downgradient of the Shell Oil site, one boring was advanced upgradient of <br /> the Shell Oil site, and two of the borings were advanced at the south end of Plymouth Road None of the <br /> borings advanced in the area of the Exxon Mobil site were placed next to existing monitoring wells <br /> ' Three of the borings advanced in the area of the Shell Oil site were placed near existing monitoring <br /> wells Boring GP-12 was advanced near MW-9, GP-10 was advanced near MWA, and GP-9 was <br /> advanced near MW-08 <br /> ' The soil borings were hydraulically advanced using a 1 75-inch diameter bit Before advancing each <br /> boring, the bit and associated push rods were thoroughly cleaned using laboratory-grade, non-phosphate <br /> detergent and delonized water and double-rinsed with deioriized water Upon completion of the dnlling <br /> ' and sampling, the borings were grouted with neat cement to within 18 inches of the ground surface The <br /> remainder of the boring was filled to the surface with soil from the borings and capped off with an <br /> asphalt hole patch The locations of the borings are shown on Figure 2,Appendix A <br /> ' 3 31 Groundwater Sampling <br /> Groundwater samples were collected from all borings The samples were collected using a push-type <br /> ' groundwater sampler The sampler has a sealed, retrievable stainless steel screen The sampler was <br /> pushed in a closed position in the borings to groundwater The sampler push rod was then retracted <br /> exposing approximately four feet of intake screen Groundwater flowed hydrostatically from the <br /> formation into the intake screen A groundwater sample was retrieved from within the screen with a <br /> length of clean, 3/8-inch diameter polytygon tubing equipped with a check valve at the bottom The <br /> tubing was moved up and down by hand to draw groundwater up inside the tubing The groundwater <br /> 1 samples were discharged directly from the tubing into laboratory supplied sample containers The sample <br /> containers were labeled, stored in a cooler chilled with Blue Ice, and delivered, under chain-of-custody <br /> procedures, to Argon Laboratories for analysis <br /> ' 3 4 LABORATORY ANALYSES <br /> Groundwater samples were analyzed for BTEX, and selected gasoline oxygenates/additives (TBA, <br /> MTBE, di-isopropyl ether [DIPE], ethyl tertiary-butyl ether [ETBE], TAME, 1,2-dichloroethane [1,2- <br /> DCA],and ethylene dibromide [EDB]) by EPA Method 8260B <br /> 4 0 INVESTIGATION RESULTS <br /> ' 4 1 FIELD OBSERVATIONS <br /> Condor observed the advancement of 15 direct push borings at various locations along the MUD storm <br /> ' drain Borings were advanced to depths ranging from 14 to 20 feet bgs, with the majority of the borings <br /> advanced to 14 or 16 feet bgs GP-7 was advanced to 20 feet bgs and GP-12 was advanced to 18 feet bgs <br /> Water samples were collected from approximately five feet below the first encountered groundwater <br /> First groundwater was encountered at an average depth of approximately 9 2 feet bgs Boring locations <br /> are shown on Figure 2, Appendix A <br /> 4 2 LABORATORY ANALYTICAL RESULTS <br /> ILaboratory analytical results indicate TBA was detected in groundwater samples collected from two <br /> . borings (GP-10 and GP-11) at concentrations of 600 and 52 gg/L Both of these locations are in the <br /> V j <br /> �� CONDOR <br />