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PR0537059
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Last modified
3/5/2020 11:03:22 AM
Creation date
3/5/2020 10:35:13 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0537059
PE
2950
FACILITY_ID
FA0021268
FACILITY_NAME
SACRAMENTO VALLEY LMTD PRTNRSHP DBA VERIZON WIRELESS
STREET_NUMBER
114
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
LODI
Zip
95240
APN
04308411
CURRENT_STATUS
01
SITE_LOCATION
114 N MAIN ST
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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1 } <br /> 1pPrivged Attorney Work Product <br /> re¢ <br /> 6.0 INVESTIGATION FINDINGS <br /> Bureau Veritas evaluated the data generated during this investigation. Our findings are summarized in <br /> the following sections. <br /> 6.1 SOIL BORING OBSERVATIONS <br /> In general, soils encountered consisted of silty gravel and clayey silt with gravel extendin f <br /> 5.0 feet bgs. Damp to moist conditions were encountered in the soil borings, like result rea <br /> rainfall. Bureau Veritas did not observe evidence of contaminated soil (e.g., d' of n, o 8 in the <br /> borings. No volatile organic compounds were detected in the field PID rea s. <br /> 6.2 SOIL ANALYTICAL RESULTS <br /> Copies of the laboratory analytical reports are presented in Appendix C. A summary of the analytical <br /> testing performed for the soil samples is presented in Table 1. Soil analytical data were compared to the <br /> Department of Toxic Substances Control California Human Health Screening Levels(CHHSLs). There <br /> currently are no CHHSLs established for GRO, DRO, MRO and VOCs. Therefore, where appropriate, the <br /> soil analytical data is compared to San Francisco Bay Regional Water Quality Control Board (SFRWQCB) <br /> Environmental Screening Levels(ESLs)for commercial properties and direct exposure soil screening <br /> levels for construction/trench worker exposure scenario, where appropriate. <br /> The following is a summary of analytical results: <br /> • VOCs, GRO, and PCBs were not detected above the laboratory reporting limits, which were <br /> below the applicable CHHSLs and ESLs. <br /> • DRO concentrations were detected in each of the three analyzed soil samples (BV-1-2'-2.5', BV- <br /> 2-2'-2.5' and BV-3-2'-2.5') at concentrations of 6.9 milligrams per kilogram (mg/kg), 24 mg/kg, <br /> and 11 mg/kg, respectively. These concentrations are below the RWQCB commercial and <br /> construction/trench worker ESLs established at 83 mg/kg and 4,200 mg/kg, respectively. <br /> Commercial CHHSLs are not established for DRO. <br /> • MRO concentrations were detected in two of the three samples(BV-2-2'-2.5'and BV-3-2'-2.5') at <br /> concentrations of 130 mg/kg and 55 mg/kg, respectively. These concentrations are below the <br /> RWQCB commercial and construction/trench worker ESLs established at 2,500 mg/kg and 4,200 <br /> mg/kg, respectively. Commercial CHHSLs are not established for MRO. <br /> 6.3 QUALITY ASSURANCE/QUALITY CONTROL <br /> The laboratory completed the quality assurance/quality control (QA/QC) activities required for the <br /> samples such as lab control samples and matrix spikes. No QA/QC issues with the analyses were noted <br /> in the laboratory reports(Appendix A). The QA/QC parameters for the samples were generally within <br /> acceptable limits and suggested that the data is useful for its intended purpose. <br /> 4 <br />
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