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3815_PGSF WMVD Pkg 2_Vol 4-2_03.03.2026_BXWA_Certified
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3815_PGSF WMVD Pkg 2_Vol 4-2_03.03.2026_BXWA_Certified
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Last modified
4/22/2026 2:55:34 PM
Creation date
4/22/2026 2:02:54 PM
Metadata
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Contracts
Contractor's Name
KLB Construction, LLC
Approval Date
4/22/2026
Council Approval Date
4/8/2026
Department
Public Works
Department Project Manager
Randy Loveless
Subject / Project Title
PGSF West Marine View Drive Storm and Combined Sewer, Package 2 Volume 4.2
Tracking Number
0005222
Total Compensation
$0.00
Contract Type
Capital Contract
Contract Subtype
Capital Construction Contracts and Change Orders
Retention Period
10 Years Then Transfer to State Archivist
Imported from EPIC
No
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ASPECT CONSULTING <br />114 FINAL PROJECT NO. AS190583A-08 MAY 21, 2025 <br />A statistical evaluation of Unit D soil copper concentrations indicates that the <br />95 percent UCL of 24 mg/kg is below the PCL of 36 mg/kg, 11.8 percent of samples <br />(17/144) exceed the PCL, and two samples have copper concentrations that are more than <br />two times the PCL. With revised compliance statistics that take into account the natural <br />background level for copper, the frequency of exceedance can be 14 percent and the <br />magnitude of exceedance can be 3.3 times the PCL (118 mg/kg). One soil result from Unit <br />D contains copper at a concentration that is more than 3.3 times the PCL (166 mg/kg). <br />However, a sample hypothesis test with a confidence of 95 percent, using the Wilcoxon- <br />Mann-Whitney test, indicates no statistical difference between Ecology’s natural <br />background data set for copper and the data set for Unit D. Considering these results, <br />copper soil concentrations within Unit D achieve statistical compliance. <br />On the north end of Unit D, shoreline wells MW-05 and NRP-MW-03 each had one or <br />more copper exceedances in groundwater during the 2012 sampling events (up to 3.6 and <br />15.9 µg/L, respectively), but no exceedances were detected in either well during the 2013 <br />and 2014 sampling events (Table 6-10). The concentrations of dissolved copper detected <br />in intertidal porewater sample PW-07 and in seep samples Seep-10, -11, and -12, all <br />located downgradient of the two shoreline wells with groundwater exceedances (MW-05 <br />and NRP-MW-03), were less than the PCL (Table 6-22). <br />6.5.5.2.3 Mercury <br />Mercury was detected exceeding the groundwater PCL of 0.025 µg/L in two Unit D <br />locations (Table 6-10; Figure 6-D8). The highest reported concentration of mercury in <br />groundwater in Unit D is at well UST-29-MW-101 where dissolved mercury was detected <br />at a concentration of 0.199 µg/L. <br />Mercury was detected in Unit D soil at concentrations exceeding the PCL at six locations <br />(Figure 6-D8). A statistical evaluation of Unit D mercury soil concentrations indicates a <br />95 percent UCL of 0.06 mg/kg, which is below the PCL of 0.1 mg/kg, 4.1 percent of the <br />samples (6/147) exceed the PCL, and there are two samples that contain mercury at more <br />than two times the PCL. Based on this data, Unit D mercury concentrations do not comply <br />statistically with the PCL. <br />There is no apparent spatial correlation between mercury exceedances in soil versus in <br />groundwater (Figure 6-D8). The highest concentration of mercury in soil in Unit D is <br />located at well TM-MW-04, where groundwater data collected during three separate <br />sampling events does not contain mercury above the groundwater PCLs (Table 6-10), <br />demonstrating empirically that mercury is not leaching to groundwater at levels that result <br />in exceedances of the PCLs. Mercury is below the PCLs in groundwater collected from <br />shoreline monitoring wells, including well REC6-MW-02, which is in Unit C, but <br />downgradient from well UST29-MW-101, or in intertidal porewater or seep samples <br />(Figure 6-D8). <br />6.5.5.2.4 Nickel <br />Three groundwater nickel exceedances were detected in Unit D groundwater, at inland <br />wells TM-MW-02, TM-MW-04, and UST29-MW-101 (Figure 6-D9; Table 6-10). There <br />is only one location within Unit D where soil nickel concentrations exceed the PCL, at <br />boring TM-B-02 (Figure 6-D9). However, Unit D nickel concentrations do not statistically
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