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Mr. Michael T. Goldstein <br /> October 14 , 1985 <br /> Page 2 <br /> Monitoring Well Installation <br /> As recommended in our letter of August 14 and agreed upon by Georgia- <br /> Pacific and the RWQCB, two additional monitoring wells (BC12 and <br /> BC13 ) were installed north of the Georgia-Pacific plant to further <br /> define the downgradient extent of chloroform in the shallow <br /> groundwater. One of the wells ( BC12 ) was constructed to monitor the <br /> "shallow" and "deep" saturated zones monitored by . the existing wells <br /> (BC2 through BC11 ) . The other well (BC13 ) was installed in the next <br /> deeper sandy to gravelly zone beneath a depth of 80 feet (below the <br /> "deep" zone ) . Both wells were sampled to determine if chloroform was <br /> present in the groundwater and if its concentration was above 50 <br /> micrograms per liter (ug/1) . <br /> Water samples from the wells contained chloroform concentrations of <br /> approximately 150 and less than 2 ug/l from BC12 and BC13 , <br /> respectively. These results indicated that an additional <br /> downgradient well, screened above the 80-fcoot depth, would be <br /> required to define the downgradient extent of chloroform migration. <br /> This well, BC14 , was subsequently installed and its chloroform <br /> concentration wsas less than 10 ug/1. Because of the low chloroform <br /> concentration in BC14 , we believe that the downgradient extent of the <br /> chloroform plume has ben established. <br /> Monitoring wells BC12, BC13 , and BC14 were installed in Units 2 and 3 <br /> of the Sycamore Village subdivision north of the Georgia-Pacific ' s <br /> plant on August 28 , August 29 , and September 4 , 1985, respectively. <br /> The wells were installed under the direction of Brown and Caldwell <br /> geohydrologists by PC Exploration of Roseville, California. A truck- <br /> mounted Mobile B-53 drilling rig equipped with nominal 6-inch <br /> diameter hollow-stem augers was used to advance the boreholes. Soil <br /> samples were obtained through the augers for classification purposes <br /> using a 5-foot continuous tube soil sampler and a standard <br /> penetration test (SPT) sampler. All down-hole equipment was steam- <br /> cleaned or washed with laboratory-grade detergent and rinsed with <br /> distilled water prior to drilling each borehole or obtaining each <br /> soil sample. <br /> Monitoring wells were subsequently installed in each borehole. Wells <br /> were constructed of 2-inch diameter flush-threaded Schedule 40 PVC <br /> blank pipe and 0. 020-inch machine-slotted pipe. Bottom caps and top <br /> plugs were installed on each well. The screened section of each well <br /> was sand packed with Number 2 or 3 Lapis Luster sand produced by Lone <br /> Star Sand of Monterey, California. Well BC12 was completed with two <br /> screened intervals to monitor the groundwater zones which are <br /> monitored by Wells BC2 through BC11 . During completion of the well , <br /> an attempt was made to separate the upper and lower screened <br /> intervals of the well, using a bentonite pellet seal. Seal placement <br /> was not successful, as a thin bentonite layer was placed in the upper <br /> screened interval. This layer does not interfere with the proper <br /> functioning of the well . Concrete or a neat cement grout was placed <br /> BROWN AND CALDWELL <br /> 110 BOX 604S WA(NUT CHL FK.CA 94596-Q. O•(415)937-9010 TELEX 33-6490•OFFICE AT 3480 BUSKIRK AVENUE PLEASANT HILL 94523 <br />