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ASPECT CONSULTING <br />86 FINAL PROJECT NO. AS190583A-08  MAY 21, 2025 <br />the PCL (108 mg/kg). The highest detected concentration of copper in Unit A is 87 mg/kg. <br />The results of the statistical analysis indicate that the copper in Unit A soils are in <br />compliance with the PCL since the 95 percent UCL of 18.mg/kg is below the PCL of <br />36 mg/kg, less than 10 percent of samples exceed the PCL, and no samples contain copper <br />at a concentration greater than three times the PCL. <br />The groundwater copper exceedances are scattered and generally low level, with all but <br />two exceedances less than two times the stringent 3.1 µg/L PCL (Table 6-10). One <br />groundwater sample collected from each of BCT-MW-106 and BCT-MW-107 contained <br />dissolved copper at concentrations of 13.3 µg/l and 13.8 µg/l, respectively, which are <br />more than four times higher than the PCL (Table 6-10). Only one out of six samples from <br />one Unit A shoreline well marginally exceeded the copper PCL (4.35 µg/L in MW-01) <br />(Figure 6-A7; Table 6-10). Dissolved copper concentrations were below the PCL in both <br />samples collected from the SEEP-01 located within the intertidal shoreline (Table 6-22). <br />Based on the spatial distribution of soil and groundwater exceedances for copper in Unit <br />A, there are not clearly identifiable soil sources for the groundwater copper exceedances. <br />For example, the highest soil copper concentrations (up to 265 mg/kg) were historically <br />detected in the area of the Old Machine Shop (OMS-series explorations), but there are no <br />groundwater copper exceedances detected historically in groundwater at either of wells <br />OMS-MW-01 or OMS-MW-02 in that area. <br />6.5.1.2.2.2 MERCURY <br />The soil mercury PCL based on leaching is the 0.1 mg/kg PQL, which is slightly above the <br />0.07 mg/kg natural background soil concentration (Table 5-3). Therefore, any detection of <br />mercury in soil is an exceedance, and soil mercury exceedances are scattered across <br />Unit A with no particular association to historical operations, as depicted on Figure 6-A9. <br />A statistical evaluation of all mercury soil data from Unit A indicates a 95 percent UCL of <br />0.07 mg/kg, which is below the soil PCL of 0.1 mg/kg, with 10.3 percent of the samples <br />exceeding the PCL (8/78), and one concentration that exceeds two times the PCL. Revised <br />compliance statistics that take into account the natural background level for mercury <br />indicate that the frequency of exceedance can be 15 percent, but the magnitude of <br />exceedance remains at two times the PCL. Mercury was not detected above the laboratory <br />reporting limit in 89.7 percent of the soil samples collected from Unit A and the 90th <br />percentile of the population has a concentration of 0.07 mg/kg, which is below the soil <br />PCL of <br />0.1 mg/kg and equal to natural background for the Puget Sound region. <br />Consistent with the low mercury concentrations in soil, dissolved mercury was detected <br />above the groundwater PCL in only one of 18 wells located in Unit A (well <br />BCT-MW-105; Figure 6-A9), in only one of five samples collected from that well, and at <br />a concentration (0.0255 µg/L) that only marginally exceeds the groundwater PCL of <br />0.025 µg/L (Table 6-10). No dissolved mercury exceedances were detected in wells <br />downgradient of BCT-MW-105, or in the SEEP-01 samples (Table 6-22).