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• SNOW, d <br /> The borehole was logged under the supervision of a professional geologist using the Unified Soil <br /> Classification System together with lithologic information to describe the subsurface geology. <br /> The soil samples were collected at about five-foot intervals, and at stratigraphic features of <br /> interest. Soil samples were field screened for fuel hydrocarbons vapor and staining. Upon <br /> completion of the borehole drilling and collection of soil samples,the borehole was converted to <br /> a groundwater monitoring well using the procedures discussed below. Borehole drill cuttings, <br /> decontamination water, cement mixing and cleanup water were placed into closed top drums, <br /> labeled and left on-site at the City specified location onsite. <br /> 4.0 Groundwater Monitoring Well Installation and Sampling <br /> 4.1 Monitoring Well Design and Installation <br /> One (1) monitoring well MWWES-1 was constructed using threaded Sch. 40 PVC casing; glues <br /> were not used. Final well design was modified to the site-specific conditions encountered in the <br /> borehole during drilling. Once the aquifer strata are defined, the casing was lowered to the <br /> bottom of the borehole through the hollowstem auger, leaving a short sand pack interval above <br /> the occurrence of groundwater to observe for floating product. The slotted interval used a 0.020- <br /> inch machine sawn slot and the annular space around the slots was backfilled with 2/12-size <br /> sand. The sand pack was placed to a point about two (2) feet above the slots. The driller surged <br /> the sandpack during installation to create amore complete hydraulic connection to the aquifer <br /> during sand pack filling. Previous experience has shown this to be a reliable well design in fine <br /> grained and stratified depositional environments in this region. A bentonite seal was placed atop <br /> the sand pack, and a cement grout seal (cement mix witnessed and approved by the SJC/EHD <br /> representative in the field prior to sealing) was placed atop the bentonite using a tremie line, <br /> filling from the bottom to top of the borehole. A traffic-rated wellhead access box and security <br /> device completed the well. <br /> 4.2 Monitoring Well Top of Casing Well Head Survey <br /> The top of well casing elevations were surveyed by the City of Tracy in January 2010 to the <br /> same known datum as existing monitoring wells MWHP-5, MWHP-6, MWHP-7 and MWHP-8. <br /> Wright has attached this information to the report. <br /> 4.3 Monitoring Well Development and Sampling <br /> The contract sampler developed the well on October 22, 2009 after waiting at least 72 hours for <br /> the well cement grout seals to set, and then purged and sampled after development. The <br /> monitoring well was first purged using calculated well volumes based upon the depth to water in <br /> each casing prior to sampling. Depth to groundwater measurements were made to the nearest <br /> one-one hundredth of one foot, and also checked for the presence of separate phase product. As <br /> each purge volume is removed, measurements of pH, electrical conductivity, turbidity, and <br /> temperature will be taken until these parameters stabilize over two measurements, which are <br /> interpreted to indicate aquifer water entering the casing. The well was allowed to stabilize to <br /> about 80%of its initial water level before sampling. <br /> Page 3 of 9 <br />