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• Notify the applicable regulatory agencies a minimum of 48 hours prior to drilling/backfilling activities; <br /> • Clear boreholes/probes of utility lines through a geophysical survey. Boring placement will be modified <br /> as necessary based on the geophysical survey results to avoid damaging underground features. <br /> Additionally, to the extent practical based on subsurface lithology, clear boring locations using hand <br /> tools; <br /> • Complete a site checklist to identify substances within the areas to be tested that may contribute to any <br /> constituents identified in indoor/outdoor air samples. Partner will perform visual inspections and <br /> conduct interviews with on-site personal to document any factors that may influence indoor/outdoor <br /> air quality. To minimize potential impacts on the air samples, air sample locations will be strategically <br /> selected to avoid areas with potential interior contaminant sources; <br /> • Photograph site conditions; <br /> • Collect a total of five air samples using laboratory-provided, individually-certified clean 3- or 6-liter <br /> SUMMA canisters. Two samples will be collected from the interior of Suite 308A (former on-site dry <br /> cleaning facility suite), one sample will be collected from the interior of Suite 306, one sample will be <br /> collected from the interior of Suite 308B, and one ambient sample will be collected to the exterior of <br /> the building. Air sampling activities will be conducted during normal business hours/operations, with <br /> the building heating,ventilation, and air conditioning (HVAC) system on; <br /> • In general, indoor air samples will collected away from entrances and in areas where the air is relatively <br /> still to minimize potential dilution effects from outside air.Also,the indoor and outdoor air samples will <br /> be placed in strategic areas to avoid any disturbance from on-site employees and the public; <br /> • Partner will periodically monitor the sampling equipment; <br /> • Provide flow controllers for each canister calibrated to collect samples over an 8-hour period; <br /> • Analyze the two air samples collected from Suite 308A and the ambient air sample for CVOCs <br /> [specifically PCE; trichloroethene (TCE); 1,1-dichloroethene (DCE); cis-1,2-DCE;trans-1,2-DCE; and vinyl <br /> chloride) via EPA Method TO-15 Selective Ion Monitoring (SIM) Method (ultra-trace detection limit); <br /> and <br /> • Hold the two air samples collected from Suite 306 and 308B at the laboratory for potential future <br /> analysis based on the results of the additional soil gas sampling; <br /> • Advance two borings in Suite 308A to a terminal depth of 15 feet bgs collecting soil samples at 2 feet <br /> bgs and in 5-foot intervals from 5 feet bgs to the terminal depth; <br /> • Advance two borings on the exterior of the building to a terminal depth of 50 feet bgs or groundwater, <br /> whichever is shallower, collecting soil samples at 2 feet bgs and in 5-foot intervals from 5 feet bgs to <br /> the terminal depth and a grab groundwater sample at the terminal depth; <br /> • Drilling and sampling equipment will be pre-cleaned prior to arriving on-site. Downhole equipment and <br /> materials will be decontaminated in a detergent/tap water and double-rinsed with tap water or with a <br /> pressure washer between samples and/or borings to reduce the potential for cross-contamination. Soil <br /> samples will be collected using a 4-foot long by 2.25-inch diameter MacroCore sampler with a 4-foot <br /> long acetate liner, which was advanced by the direct-push drill rig using 4-foot long by 1.5-inch <br /> diameter drill rods.The sampler will be driven into the subsurface to allow undisturbed soil to enter the <br /> open MacroCore barrel and retrieved in 4-foot intervals to recover the soil-filled liners. A lengthwise <br /> section of each acetate liner was removed with a splitting tool to expose the soil. The soil column was <br /> visually inspected for discoloration, monitored for odors, and classified in accordance with the Unified <br /> Soil Classification System (USCS). Select intervals were placed in sealable plastic bags and field-screened <br /> with a photoionization detector (PID) calibrated to isobutylene. Soil depths selected for laboratory <br /> analysis will be sampled directly from the liners using a disposable plastic syringe and retained in one <br /> methanol-preserved and two sodium bisulfate-preserved volatile organics analysis (VOA) vials in <br /> Page 3 PARTNER <br />