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0 Samples were collected by Del -Tech from each sample point containing sufficient liquid <br />and submitted to BC Laboratories (BC) of Bakersfield, California, a state certified <br />laboratory under contract to Forward. During the third quarter 2012 monitoring period, <br />samples were analyzed for the routine monitoring parameters stipulated in RWQCB <br />Order No. R5-2003-0049. Table 2-1 summarizes site monitoring parameters, analytical <br />methods, and monitoring frequency. Water quality samples were also analyzed in the <br />field for oxygen reduction potential (ORP), turbidity, temperature, specific conductance, <br />and pH and recorded on well data sheets. The groundwater monitoring wells and <br />leachate monitoring points were sampled in accordance with the sampling and analysis <br />procedures detailed in Appendix B. The well data sheets, laboratory data, certificates of <br />analyses, and chain -of -custody records for the sampling program are included in <br />Appendix C. The laboratory analyses and field results for groundwater monitoring wells, <br />surface water stations, lysimeter and leachate sampling stations are summarized in Tables <br />2-2 through 2-6. <br />The quality assurance/quality control (QA/QC) program completed for the third quarter <br />2012 water quality monitoring event included analyses of two field blanks, one trip <br />blank, two laboratory method blanks, and one duplicate sample. The field and trip blanks <br />were analyzed for volatile organic compounds (VOCs) by EPA Method 8260 and method <br />blanks were analyzed for all of the analytes included in the monitoring program. The <br />results of the QA/QC program indicate that two VOCs (chloromethane and styrene) were <br />detected at estimated trace concentrations in the trip blank during the monitoring period. <br />However, review of the primary sample results indicates that neither of these VOCs were <br />detected in the primary samples collected during the monitoring period. A duplicate <br />sample was collected from wells MW -14 and labeled FMW-Duplicate. With the <br />exception of hexavalent chromium, the duplicate sample analyses yielded good <br />correlation with a relative percent difference of less than 7 percent. Review of the <br />sampling dates and laboratory analytical certificates indicates that all of the laboratory <br />analyses were completed within required holding times. Based on the results of the <br />laboratory QA/QC analyses, it is concluded that the laboratory data generated for the <br />third quarter 2012 monitoring period are generally acceptable and the water quality <br />samples collected from the Forward Unit appear to be representative of water quality at <br />the site. <br />iff ZITMI CITIM It <br />Prior to purging and sampling, each well was sounded for water depth using a weighted <br />electronic sounder to an accuracy of 0.01 foot, and the static water level was recorded on <br />a Well Data Sheet (Appendix Q. The groundwater elevations were calculated for each <br />well by subtracting the depth -to -water measurement from the top -of -casing reference <br />elevation. The current groundwater elevation data for the Forward Unit is summarized in <br />IV Table 2-3. <br />C:\2012-0025\FA3Q12.doc 4 Geo -Logic Associates <br />