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ARCHIVED REPORTS_2019-MAY 15 SITE ASSESSMENT REPORT
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ARCHIVED REPORTS_2019-MAY 15 SITE ASSESSMENT REPORT
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Last modified
1/19/2024 2:59:55 PM
Creation date
1/9/2024 1:44:56 PM
Metadata
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Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2019-MAY 15 SITE ASSESSMENT REPORT
RECORD_ID
PR0504201
PE
4430
FACILITY_ID
FA0000214
FACILITY_NAME
PILKINGTON NORTH AMERICA INC PLANT 10
STREET_NUMBER
500
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
AVE
City
LATHROP
Zip
95330-9739
CURRENT_STATUS
01
SITE_LOCATION
500 E LOUISE AVE
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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15 May 2019 <br />AGE Project No. 14-3002 <br />Page 12 of 17 <br />• Only one SVOC/PAH was detected in the waste samples analyzed. Bis <br />(2-ethylhexyl) phthalate was detected in B18-5 at a concentration of 2.33 mg/kg; <br />the concentration was significantly below the ESL (Table 4). <br />• PCBs were detected in 5 of 6 waste samples at concentrations ranging from <br />0.202 mg/kg in B16-5 to 0.680 mg/kg in B20-5. PCBs were detected below the <br />ESL and hazardous waste limit in the samples analyzed (Table 4). <br />• TPH were not detected above laboratory reporting limits in any of the waste <br />samples analyzed (Table 4). <br />• Dioxin/Furans were detected in all twelve waste samples analyzed at TEQ <br />concentrations ranging from 0.238 pg/g in mixed waste/soil sample B35-14 to <br />52.2 pg/g in waste sample B36-6. The dioxin/furans concentration detected in <br />B36-6 (52.2 pg/g) was above the ESL of 22 pg/g, but well below the hazardous <br />waste limit of 10,000 pg/g. However, the environmental screening level for dioxins <br />is based on the congener 2,3,7,8-TCDD, and that specific congener was not <br />detected above 22 pg/g in sample B36-6 (Table 4; Appendices G and H). <br /> <br />No additional analytes were reported above laboratory detection limits in the waste <br />samples analyzed. Analytical results of waste samples are summarized in Tables 2 <br />through 4. PCB, dioxin/furan, and TPH concentrations are depicted in Figures 3 through 5 <br />and in cross-sectional view in Figures 6 through 9. The laboratory reports (listed in <br />Section 5.3.), QA/QC reports, and chain of custody forms are included in Appendix H. <br />Laboratory EDF files will be QA/QC checked and uploaded to the State Water Board <br />GeoTracker site. <br /> <br /> <br />5.5. ANALYTICAL RESULTS OF GROUNDWATER SAMPLES <br /> <br />A total of nine grab groundwater samples were collected from borings B1, B6, B13, B16, <br />B23, B28, B31, B35 and B40. Additionally, AGE assisted CVRWQCB staff with collecting <br />a tenth groundwater sample from boring B18. Groundwater samples collected from <br />borings B16 and B35 were collected near the center of Waste Cell No. 1 and Waste Cell <br />No. 2, respectively, while the groundwater sample collected from B13 was collected in <br />the general location of the former groundwater injection well utilized by the former power <br />plant. Except for dioxin/furans, all groundwater samples collected by AGE were analyzed <br />for the constituents listed in Section 3.3. Samples collected from B13, B16 and B35 were <br />additionally analyzed for dioxin/furans. <br /> <br />The following is a summary of the analytical results: <br />• Arsenic was detected in the groundwater samples analyzed at concentrations <br />ranging from 0.008 mg/l in B13 to 0.094 mg/l in B6. Arsenic was detected above <br />the MCL of 0.01 mg/l in eight of the nine groundwater samples, but significantly <br />below the hazardous waste limit (Table 5).
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