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Kennedy/Jenks Consultants <br /> The locations and well casing elevations of these new monitoring wells will be horizontally and <br /> vertically surveyed by a licensed land surveyor. The ground surface and top of well casing <br /> elevation will be surveyed to the nearest 0.01 foot relative to mean sea level using the National <br /> Geodetic Vertical Datum (NGVD 1988), relative to nearest benchmark at the Site. Horizontal <br /> locations of the new wells will also be surveyed to the nearest 0.1 foot relative to the California <br /> Coordinate system. <br /> 8.4 Groundwater Sampling <br /> Initial sampling of groundwater will be conducted from the newly-installed monitoring wells no <br /> sooner than 72 hours after these wells have been developed, in accordance with <br /> Kennedy/Jenks' Standard Operating Guideline—Groundwater Sampling (Appendix 1). <br /> Groundwater will be purged from the monitoring wells prior to sampling to acquire samples <br /> representative of aquifer conditions. The field parameters pH, temperature, and electrical <br /> conductivity will be monitored during purging to document stabilization of groundwater quality in <br /> accordance with Kennedy/Jenks' Standard Operating Guideline— Field Measurement of pH, <br /> Temperature, and Conductivity (Appendix J). Field parameters will be recorded on a <br /> groundwater purge and sample form. In accordance with the Monitoring and Reporting Program <br /> R5-2002-1048 (MRP), Musco will also continue to perform quarterly monitoring of the previously <br /> installed groundwater monitoring wells to obtain additional groundwater characterization data. <br /> Groundwater samples will be collected into appropriate containers provided by the analytical <br /> laboratory using a new disposable bailer or a positive displacement pump. One duplicate <br /> sample will be collected during each sampling event. Following collection, the samples will be <br /> labeled and placed into a chilled container held at four degrees Celsius. The samples will be <br /> submitted in the chilled container to a state-certified analytical laboratory using chain-of-custody <br /> procedures to document the sample handling process. The groundwater samples will be <br /> analyzed for the following water quality constituents and parameters by the analytical laboratory <br /> following their normal turnaround time and internal quality assurance/quality control (QA/QC) <br /> procedures: <br /> • Boron by EPA Method 200.7. <br /> • Calcium by EPA Method 6010. <br /> • Biochemical Oxygen Demand by EPA Method 410.4. <br /> • Chloride by EPA Method 300 Series. <br /> • Magnesium by EPA Method 6010. <br /> • Nitrate-Nitrogen by EPA Method 300 Series. <br /> • Ammonia by EPA Method 350.3. <br /> • Total Kjeldahl Nitrogen by EPA Method 351.4. <br /> • pH by EPA Method 150.1. <br /> • Potassium by EPA Method 6010. <br /> • Sodium by EPA Method 6010. <br /> • Specific Conductivity by EPA Method 120.1. <br /> • Sulfate by EPA Method 300 Series. <br /> • Bicarbonate Alkalinity by EPA Method 310.1. <br /> • Total Dissolved Solids by EPA Method 160.1. <br /> Phase I Groundwater Investigation Report and Work Plan for Phase 11 Investigation Page 29 <br /> Musco Family Olive Company, Tracy, California <br /> g:VsgroupntlmhyobY1TV130106.�mumwFre`A9+egxtaYdoVash <br /> 13" i"invwl rp(yhm U lnwa wk pWl Adw <br />