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' 3. VERTICAL CHARACTERIZATION OF GROUNDWATER <br />' In order to vertically assess hydrocarbons in groundwater, a deep offsite well is proposed for <br /> installation The location of the proposed well is shown on Figure 12 This location is located <br /> offsite and downgradient of the former underground storage tanks The scope of work for the <br />' installation of the deep groundwater monitoring well is presented below <br /> 3.1 PRE-FIELD ACTIVITIES <br /> Prior to field work a permit for the installation of one deep gr oundwater monitoring well <br /> (MW14) will be acquired from the SJCEHD ETIC personnel will acquire offsite access from <br /> the property owner, appropriately mark the proposed well location as indicated in Figure 12, and <br /> Underground Service Alert will be contacted at least 72 hours prior to drilling A licensed utility <br /> line locator will be subcontracted by ETIC to clear the marked well location for drilling If the <br /> marked well location is over or adjacent to a utility line, ETIC personnel will mark another <br /> appropriate location, which will be screened by the utility line locator to clear the location for <br /> drilling <br /> 3.2 WELL INSTALLATION <br /> Proposed well MW14 will be constructed as a 2-inch-diameter groundwater monitoring well <br /> across a deeper permeable zone The proposed location as presented in Figure 12 was selected to <br /> assess the vertical extent of impacted groundwater downgradient of the former tank field <br /> lie Currently the greatest depth explored at the site is 51 feet bgs in well SW2 The construction of <br /> proposed well MW14 will be based on the additional hydrogeologic and lithologic information <br /> acquired while drilling to depths greater than 50 feet bgs Drilling will be terminated at a depth <br /> of 70 feet bgs if no second permeable zone is encountered <br /> The ultimate depth of MW14 will be dependent upon the subsurface hthology encountered <br /> below 50 feet bgs Soil samples will be screened visually and with an organic vapor meter for <br /> evidence of petroleum hydrocarbons If petroleum hydrocarbons are observed and/or detected, a <br /> conductor casing may be set to a depth of 50 feet bgs Soil samples will be collected at 5-foot <br /> intervals to 45 feet bgs and continuously from 45 feet bgs to the total depth of the borehole in <br /> order to examine the lithology and to locate the base of the upper confining layer, and the next <br /> permeable zone The anticipated depth of the bottom of the upper confining layer and next <br /> permeable zone below 50 feet bgs is unknown Once the base of the upper confining layer is <br /> encountered, the boring will be drilled further to a second permeable zone If a second <br /> permeable zone 1s encountered before 70 feet bgs, 5 to 10 feet of screen will be set in place and <br /> the monitoring well installation will be completed If a second permeable zone is not <br /> encountered, then a well screened from 65 to 70 feet bgs will be installed Details concerning <br /> ETIC field protocol for conductor casing and well installation are presented in Appendix H <br /> 3.3 WELL DEVELOPMENT AND SAMPLING <br /> Prior to collecting groundwater samples, the well will be property developed Development will <br /> i occur either prior to establishing the bentonite seal during well construction, or 72 hours after <br /> GSProjects1739421MAS7ER\WP1WPO3031WPtx da 1 1 <br />