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2-7 <br /> were identified with the same designation as the monitoring wells Monitoring Wells MW-4, <br /> MW-5, and MW-6 were installed during the supplemental Phase H Investigation <br /> Monitoring wells were constructed using flush-threaded, 2-inch diameter, Schedule 40 poly- <br /> vinyl chloride {PVC} riser and 10 feet of PVC, 0 010-mch mill-slotted screen fitted with a <br /> flush-threaded end cap The PVC casing was inserted into the boring with the hollow-stem <br /> augers left in place to the total depth of the boring The screen interval was placed with the <br /> top of the screen approximately 2 feet above the static water level at the tune of installation <br /> PVC riser was added so the top of the casing was approximately 1 5 to 2 feet above the <br /> ground surface Clean silica sand was placed in the annular space between the screen and <br /> the borehole wall to a depth approximately 1 to 2 feet above the top of the screen Hollow- <br /> stem augers were incrementally removed from the boring as the sand pack was being placed <br /> A bentomte pellet seal, with a thickness of approximately 1 to 2 feet, was placed on top of <br /> the sand pack and hydrated with potable water The bentonite pellets were permitted to set <br /> up for a minimum of 1 hour A bentonite/cement grout mix was placed on top of the ben- <br /> tonite seal in the annular space until it reached the ground surface The PVC casing was <br /> capped with a locking watertight hd A locking protective steel casing was placed over the <br /> ' PVC casing Detailed as-built drawings of each monitoring well are contained with the bor- <br /> ing logs in Appendix B Monitoring well construction data are provided in Table 2 <br /> Development of the monitoring wells was completed approximately 24 hours after mstalla- <br /> ' tion Water was bailed from each well for a penod of up to 60 minutes to remove fine <br /> cuttings that were produced during drilling Approximately 10 to 20 well volumes were <br /> removed from each well and pH, specific conductance, and temperature were measured after <br /> each successive 5 gallons of water removed. Monitoring well development was not consid- <br /> ered completed until successive pH, specific conductance, and temperature measurements <br /> were within 10 percent Summary sheets of each monitoring well development are presented <br /> in Appendix D Water removed was placed in 55-gallon drums and staged at the site for <br /> disposal <br /> 29025 <br /> I <br /> ' "REALISTIC SOLUTIONS FOR HAZARDOUS WASTE PROBLEMS" <br />