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. the source The auger and bit will be advanced to 3 feet above the desired sampling <br /> depth at which point a hydropunch tip and screen will be inserted through the hollow <br /> stem auger at the end of a hollow rod and driven three feet into the formation at the base <br /> of the test hole A groundwater sample will be collected from the screened tip with a <br /> mini bailer through the hollow rod The water sample will be decanted into 4 VOA vials <br /> with no airspace and preserved with 0 5 ml of HCL The water samples will be labeled <br /> and preserved as described below for the soil samples <br /> The hydropunch water samples will be analyzed by a certified laboratory for <br /> concentrations of TPH-G, BTEX, and MTBE using EPA method 8260B The results will <br /> be used to determine if future wells, if necessary, will need to be multiple depth-screened <br /> wells to define the groundwater contamination plume at distance from the source Once <br /> all samples have been obtained from the exploratory borings, the borings will be <br /> destroyed with neat cement containing 5% bentonite using tremae method for placement <br /> of the cement from bottom of boring to surface During placement of cement, all <br /> displaced fluids exiting the borings will be collected and pumped into 55-gallon drums <br /> that will be stored onsite for later disposal <br /> COMPLETION OF MONITOR WELLS MW6 AND MW7 <br /> Once the exploratory borings have been destroyed, the boreholes for MW6 and MW7 <br /> will be drilled to the 30-foot depth using 8-inch hollow stem augers No samples will be <br /> obtained because of the close proximity of each set of holes <br /> The boreholes will then be completed as monitor wells with and estimated 15 feet of <br /> machine slotted SCH 40 TriLock 2 inch diameter PVC screen (0 01) from estimated 15 <br /> feet bgs to the total depth of the well at 30 feet bgs Core examination from the <br /> exploratory boring nearest the well will determine the top of sand/clay interface <br /> placement of the top of screen The wells will be completed to surface with blank SCH <br /> 40 TriLock 2" diameter PVC The sand envelope will consist of 92/16 Lapis Lustre sand <br /> and will be positioned from the base of the well to 2 feet above the top of the slotted <br /> casing The sand envelope will be sealed on top with a 1-foot layer of hydrated bentonite <br /> pellets Cement (with less than 5% bentonite) will be used to seal the annular space from <br /> the top of the bentonite seal to surface A locking thermos cap will be used to seal the <br /> casing orifice A steel traffic box fitted with a well ID tag will be set in concrete to <br /> protect the exposed well casing <br /> COMPLETION OF RECOVERY WELL R1 <br /> The borehole will be completed as a monitor well with and estimated 23 feet of machine <br /> slotted SCH 40 TnLock 4 inch diameter PVC screen (0 02) from estimated 7 feet bgs to <br /> the total depth of the well at 30 feet bgs Core examination will determine the top of <br /> sand/clay interface placement of the top of screen The wells will be completed to <br /> surface with blank SCH 40 TriLock 4" diameter PVC The sand envelope will consist of <br /> #3 Lapis Lustre sand and will be positioned from the base of the well to 2 feet above the <br /> top of the slotted casing The sand envelope will be sealed on top with a 1-foot layer of <br /> hydrated bentonite pellets Cement (with less than 5% bentonite) will be used to seal the <br /> 6 <br />