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2003-0049. Table 2-1 presents the monitoring schedule and summarizes the analytical <br /> methods utilized during the current monitoring period. Water quality samples were also <br /> analyzed in the field for dissolved oxygen, turbidity, temperature, specific conductance, <br /> and pH and recorded on well data sheets. The groundwater monitoring wells and <br /> leachate were sampled in accordance with the sampling and analysis procedures detailed <br /> in Appendix B. The well data sheets, raw laboratory data, certificates of analyses, and <br /> chain-of-custody records related to the sampling program are included in Appendix C. <br /> Field and laboratory analyses are summarized in Tables 3-1 through 3-6. <br /> 3.1.2 A/ C Results <br /> The QA/QC program completed for the fourth quarter 2008 water quality monitoring <br /> event at the Austin Unit included analyses of three field blanks, three trip blanks, three <br /> laboratory method blanks, and one duplicate sample. The trip, field, and laboratory <br /> method blanks were analyzed for VOCs by EPA Method 8260 and method blanks were <br /> analyzed for all required analyses. The results of the QA/QC program indicate that <br /> chloroform was detected above the PQL in two field blanks during the monitoring period. <br /> Review of the primary sample results indicates that a similar concentration was detected <br /> in the primary sample collected from well AMW-1 during the monitoring period and was <br /> flagged as a suspected field/laboratory contaminant. During the fourth quarter 2008 <br /> monitoring event, a duplicate sample was collected from well AMW-10 and labeled <br /> DUP. Duplicate groundwater results are presented along with the primary data in Table <br /> 3-2. With the exception of arsenic, comparison of the values in the primary sample with <br /> the duplicate indicates that there was good agreement (within 5%). <br /> Review of laboratory analysis dates with required holding times indicates that all samples <br /> were submitted and analyzed within the required holding times during the fourth quarter <br /> 2008. Based on the results of the laboratory blank and duplicate analyses, it is concluded <br /> that the laboratory data generated for the fourth quarter 2008 monitoring period are <br /> generally acceptable and the water quality samples collected from the Austin Unit appear <br /> to be representative of water quality at the site. <br /> 3.1.3 Groundwater Elevations and Contours <br /> Prior to purging and sampling, each well was sounded for water depth using a weighted <br /> electronic sounder, and the static water level was recorded on a well data sheet <br /> (Appendix Q. The groundwater elevations were calculated for each well by subtracting <br /> the depth-to-water measurement from the top-of-casing reference elevation. The current <br /> groundwater elevation data for the Austin Unit are summarized in Table 3-4. <br /> The groundwater elevation data obtained during this quarterly monitoring period were <br /> used to generate the groundwater elevation contour map shown on Figure 3-1,which <br /> indicates that groundwater beneath the Austin Unit generally flows to the north at an <br /> average hydraulic gradient of approximately 0.002 ft/ft. <br /> D:UO08_0010\FA_4QO8.doc <br /> 9 Geologic Associates <br />