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r. <br /> Underground Storage Tank Deline"31 n Sampling Using Cone Penetration Testing <br /> With An Ultra-Violet Optical Screening Tool Report <br /> 216 N.California Street <br /> Page 3 of 7 <br /> underground utilities until the first day of drilling and required positive location of lines by hand digging <br /> or vacuum excavation prior to drilling within 10 lateral feet of surface markings. This requirement made <br /> drilling in the traffic or parking lane of northbound California Street impractical during this phase of the <br /> investigation. Prior to initiating fieldwork at the Site, all field personnel were familiarized with the Site <br /> Specific Health and Safety Plan included in the Work Plan. <br /> 2.2 CONE PENERATION TEST FIELD PROCEDURES <br /> The CPT borings were hydraulically advanced using a 2-inch diameter conical bit in conjunction with a <br /> UVOST module. The soil behavior (tip pressure and sleeve friction) was logged as the probe was <br /> advanced. The ratio of soil behaviors was used to classify the penetrated soil by soil behavior type <br /> (SBT), which is similar to the Unified Soil Classification System (USCS). The UVOST module emitted <br /> _ ultra-violet light through a window in the module that caused hydrocarbon molecules to fluoresce. Fiber- <br /> optic cables transmit fluorescence data to the surface, where intensity and decay were recorded <br /> approximately every 2 inches. The UVOST data was correlated to the SBT data. Decay signatures <br /> indicated the type of hydrocarbon impact and the signal intensity indicated the location. Data logs were <br /> prepared containing observations including SBT, UVOST measurements, and the location of soil and <br /> groundwater samples. Soil and groundwater samples were collected from the borings for laboratory <br /> analyses based upon CPT and UVOST measurements. <br /> Discrete depth soil samples were collected from the borings with a 1-inch outside diameter (O.D.), <br /> 12-foot-long core barrel fitted with a clean, single use, stainless steel liner. The soil sampling equipment <br /> was`7c eaneTprior to collecting the samples. Soil samples were collected from selected borings and <br /> intervals for laboratory analyses. The liners were sealed at the ends with Teflon® sheeting, capped, and <br /> labeled. The samples were placed in a cooler with Blue Ice® and delivered under chain-of-custody <br /> procedures to a California-certified laboratory for analyses. <br /> The groundwater samples from the borings were collected using a push-type groundwater sampler. The <br /> .- sampler has a sealed, retrievable stainless steel screen. The sampler was pushed in a closed position to <br /> the desired sampling interval. The sampler push rod was then retracted exposing the inlet screen. <br /> Groundwater flowed hydrostatically from the formation into the inlet screen. A groundwater sample was <br /> retrieved from within the screen with a small diameter stainless steel bailer. The groundwater samples <br /> were discharged directly from the bailer into laboratory supplied sample containers. The sample <br /> containers were sealed, labeled, placed in a cooler with Blue Ice®, and delivered under chain-of-custody <br /> procedures. Upon completion of the borings and sampling, the borings were grouted with neat cement to <br /> the surface with SJCEHD observation and/or authorization. <br /> _ 3.0 SOIL AND GROUNDWATER INVESTIGATION <br /> Each CPT location consisted of one to four co-located but separate borings within a 4-foot radius. First, <br /> the CPT/UVOST testing probe was advanced to a depth of 100 feet bgs to evaluate the vertical extent of <br /> ■- soil contamination. Separate borings were advanced to collect each groundwater sample at selected <br /> depths after CPT/UVOST data and logs were analyzed. The last boring was advanced to collect the soil <br /> samples. CPT 1-1 was placed in the landscaped area, approximately 5 feet east of the former location of <br /> .. the UST and previously-advanced SB-1. Groundwater samples were collected at depths of 61 feet and 75 <br /> feet bgs from two separate borings, CPT 1-2 and 3, to minimize the potential for cross-contamination as <br /> directed in the contingent Work Plan approval letter from SJCEHD dated October 30, 2008. Four soil <br /> samples were then collected from a separate boring, CPT 1-4 at depths of approximately 60 feet, 72 feet, <br /> 80 feet, and 100 feet bgs,based upon indications of contamination from the UVOST tool. <br /> is CONDOR <br />