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2.3 Field Investigation <br /> The scope of work for this project included an underground utility location survey and the <br /> advancement of two soil borings using Cone Penetrometer Testing (CPT) methods Details of <br /> the investigation methods are presented in the following sections <br /> 2.3.f Underground Utility Location Survey <br /> On February 11, 2002, an underground utility location survey was conducted to assess the <br /> absence or presence of unreported underground utilities at the site The utility survey was <br /> conducted using ground-penetrating radar (GPR) and radio frequency survey equipment The <br /> utility survey cleared utilities for the proposed CPT boring locations <br />* 2.3.2 Drilling and Groundwater Sample Collection <br />■ Two borings were advanced to 30 5 meters (100 feet) using a truck mounted Cone Penetrometer <br /> Testing (CPT) rig A boring location map is presented in Figure 2 The boring locations were <br /> selected by Caltrans to provide data for determining the vertical extent of contamination The <br /> CPT borings were performed to obtain deep lithologic data on the aquifer and to collect discreet <br /> groundwater samples As the first boring was advanced, cone bearing tip resistance, sleeve <br /> friction, friction ratio, and pore water pressure were measured using the cone penetrometer tip <br /> Using the CPT results, subsurface conditions were interpreted in order to determine aquifer <br /> zones to collect groundwater samples from The CPT log indicated that potential water bearing <br /> zones were located at 19 8 meters (65 feet), 27 4 meters (90 feet), and 30 5 meters (100 feet) <br /> The second boring, SC-1, was advanced to obtain groundwater samples from the targeted zones <br /> using Hydropunch methods <br /> Groundwater samples were collected from each of the zones using Hydropunch methods The <br /> samples were collected by advancing approximately 1 meter(3 3 feet) below the targeted zone <br /> and raising the probe to expose the 1 5-meter (5-foot) screen New disposable polyethylene and <br /> stainless steel bailers were used for groundwater collection The groundwater samples were <br /> labeled, packaged with ice, and stored in an insulated chest for transport under chain-of-custody <br /> manifest to a California-certified analytical laboratory Groundwater samples were labeled with <br /> the boring number, depth, date, time, and initialed For example SC-1-64, where SC-1 is the <br /> boring number and 64 is the sample depth in feet Temperature, pH, and conductivity of each <br />' groundwater sample were recorded on field report forms Drilling and sampling procedures are <br /> included in Appendix B <br /> Following the last sample, an expendable Hydropunch tip was knocked out and the hole grouted <br /> with 20 1 cement/bentonite grout, from the bottom up, during removal of the probe casing <br /> x,k—b-rectu,obgrl CRFPI3COMMan&wDPLVWWJBW n.luidbc 2-2 <br /> 4102 <br />