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summer sampling events. However, winter precipitation has been below normal, with <br />Colorado experiencing an extended drought, and the effects of these dry conditions may be <br />resulting in continued elevated TDS and sulfate concentrations in the alluvial groundwater. <br />Radiochemistry <br />Based on the March 20, 2012 sampling results, the Radium 228 activity exceeded the site <br />NPL in well MW -04. As shown in Table 2, prior to this event, radium activities have never <br />exceeded numeric protection levels at the site. The elevated Radium 228 value at well <br />MW -04 appeared to be an outlier. The Radium 228 activity at well MW -04 reported from <br />the June 2012 sampling has returned to levels well below the NPL, and March 20, 2012 <br />result does appear to be an outlier. No significant trends in the radium data have been <br />observed in any of the monitoring wells. The combined radium 226 and radium 228 <br />activities do not currently exceed the 5 pCi/L Colorado groundwater Table Value standard <br />in any wells, as they have at well MW -04 for numerous monitoring events. There is no <br />indication that any GCC plant activities are responsible for elevated radium activities at the <br />GCC Facility, as these have been shown to be naturally occurring. <br />Field Parameters <br />Field parameters including temperature, pH, and conductivity were collected during the <br />June 2012 sampling event. Results of the field parameter monitoring are provided in Table <br />1. The data collected indicate that pH at the site is very close to neutral. Conductivity <br />continues to be elevated, and was highest at well MW -03 where the saturated thickness in <br />the well has been as low as 4 inches. Elevated conductivity can be directly correlated to <br />elevated TDS. <br />http:// groundwater. ucdavis.edu /Publication /Harter FWQFS 8084.pdf <br />Quality Control <br />One set of field duplicate samples was collected during the monitoring event. Sample <br />DUP -01 was submitted as a blind field duplicate of primary alluvial well sample MW002. <br />Field duplicate precision is measured as the Relative Percent Difference (RPD) between the <br />primary and duplicate sample results. The RPD is defined as the "absolute value of the <br />difference between the primary and duplicate results, divided by the average of the two <br />results." Precision between the results of the primary and duplicate samples was very good <br />for all parameters tested, with a maximum RPD between field duplicate detections for <br />metals of 7.3 percent for sulfate, or agreement within uncertainly windows for the radium <br />228 comparisons. <br />One equipment rinsate blank was collected during the June 21, 2012 monitoring event, and <br />was submitted for analysis of TDS and sulfate. The blank was collected by pouring <br />laboratory- supplied de- ionized water through a new bailer and into the appropriate sample <br />bottles. No TDS or sulfate were detected in the equipment blank. <br />All laboratory data packages were reviewed to ensure that quality control elements (holding <br />times, blanks, control samples, and matrix spikes), impacting precision and accuracy of the <br />5 <br />