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f �y <br /> 15 November 2005 <br /> AGE-NC Project No 04-1239 <br /> Page 4 of 5 <br /> s <br /> will be collected from each soil boring at 5-foot intervals using a California modified split-spoon <br /> sampler fitted with 2-inch diameter, 6-inch long brass sleeves Upon removal from the sampler,the <br /> sample sleeves will be separated with a knife The exposed ends of the second sleeve will be covered <br /> with Teflon sheets, capped, and sealed with tape Soils sampled in the borings will be visually <br /> classified by an AGE geologist in accordance with the Unified Soil Classification System (USCS) <br /> Additionally, soil samples will be field screened for the presence of volatile organic compounds <br /> using an organic vapor meter(OVM),equipped with a photo-ionization detector(PID) Soil sample <br /> descriptions and OVM readings will be recorded on a log for each boring <br /> Following sample collection, each preserved sample sleeve will be labeled with the boring location, <br /> depth,time, date,and sampler's initials Appropriately sealed and labeled samples will be placed in <br /> a chilled container and transported under chain of custody to a DHS-certified laboratory for analysis <br /> for the constituents listed in Section 2 2 <br /> 3 2 WELL COMPLETION AND ELEVATION SURVEY <br /> The pilot soil borings will be completed as ground water monitoring wells utilizing 2-inch diameter, <br /> Schedule 40 PVC blank well casing and 0 010-inch slotted well screen installed from 20 feet to <br /> 40 feet bsg in the two shallow wells and from approximately 55 feet to 65 feet bsg or from 60 feet <br /> to 60 feet bsg if required to isolate a coarse grained stratigraphy, in the two deep wells Proposed <br /> monitoring well construction diagrams are depicted on Figures 3 and 4 <br /> After installing the well casing in each pilot boring, a filter pack material consisting of pre-washed <br /> #2112 Lonestar sand will be added through the augers from total depth to approximately 2 feet above <br /> the screened interval Following placement of the filter pack, the well will be surged to assist in <br /> settling the filter pack Additional sand will be added if settling occurs <br /> A nominal 2-foot bentonite chip seal will be placed above the filter pack to minimize the potential <br /> for grout penetration into the screened section of the wells The bentonite seal will be formed by <br /> pouring bentonite chips into the annulus and allowing them to settle on the filter pack The bentonite <br /> -pellets will be allowed to hydrate for a minimum of one-half hour prior to grouting <br /> The remaining annular space will be filled to within 1 foot of the ground surface with a cement <br /> grout The grout mixture will consist of Type I/II portland neat cement and not more than 6 gallons <br /> of water per 94-pound sack of cement The grout will be placed by pumping through a tremie pipe <br /> A grouting inspection will be scheduled with EHD personnel <br /> Following completion of the monitoring wells, well elevations and locations will be surveyed by a <br /> ipCalifornia-licensed surveyor relative to a City of Stockton elevation benchmark <br /> Advanced GeoEnvironmental,Inc <br />