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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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a i <br /> Privrlged Attorney Work Product <br /> KZXMEM <br /> 4.2 SOIL BORINGS <br /> On November 6, 2012, Bureau Veritas contracted with a California-licensed (C-57) drilling company, <br /> Enprobe Drilling Services (Enprobe) located in Oroville, California,to complete the drilling activities <br /> associated with this LSI. Enprobe advanced a total of three borings (BV1 through BV3) using truck- <br /> mounted direct-push (Geoprobe®) equipment. The three borings were advanced within the proposed <br /> utility trench areas to maximum depths of five feet bgs to collect soil samples at the locations identified in <br /> Figure 2. During drilling activities, soil cores were collected from the borings. Soil cores were obtained <br /> using a 4-foot-long by 2-inch-diameter core barrel sampler. The core barrel contained a plastic liner that <br /> retained a relatively undisturbed soil core from which soil samples were collected. <br /> 4.3 SOIL SAMPLING <br /> Two discrete samples were obtained from each of the three borings at depths from 2.0 to 2.5 feet bgs and <br /> from 4.5 to 5.0 feet bgs. These are the expected soil depths to which construction workers may be <br /> exposed during the proposed trenching activities. Soil samples were field screened for indications of <br /> possible contamination and for the presence of volatile and ionizable compounds using a photoionization <br /> detector(PID). The PID records total ionizable compounds in parts per million (ppm) meter units, but is <br /> not designed to identify or quantify specific compounds. Selected soil samples were cut from the acetate <br /> liners and sealed with Teflon tape and plastic end caps, labeled with identifying information, and stored in <br /> a pre-chilled ice-chest awaiting transportation to the laboratory. Selected soil samples were subsequently <br /> recorded onto a chain-of-custody document. <br /> 4.4 EQUIPMENT DECONTAMINATION <br /> New plastic liners were placed in the core barrel prior to each sampling interval. Down-hole equipment <br /> was washed in a solution of non-phosphate detergent and double rinsed with tap water after each use. <br /> 5.0 CHEMICAL ANALYSES <br /> A total of six discrete soil samples were transferred under formal chain of custody protocol to Test <br /> America Laboratories, Inc. a State of California certified laboratory, located in Pleasanton, California. <br /> Chain-of-custody records were completed and accompanied the sample shipments to the laboratory. The <br /> soil samples from the 2.0 to 2.5 feet bgs depths were individually analyzed for the following constituents <br /> as noted using United States Environmental Protection Agency (USEPA)-approved methods: <br /> Diesel and Motor Oil Range Organics (DRO and MRO) by 8015B with silica gel cleanup. <br /> • Polychlorinated Biphenyls (PCBs) by 8082. <br /> • Volatile Organic Compounds(VOCs)and Gasoline Range Organics(GRO) by 8260B. <br /> The soil samples were analyzed on a standard five business-day turn-around-time. The samples <br /> obtained from the 4.5 to 5.0 feet bgs were placed on hold and were not analyzed pending analytical <br /> results of the samples from the shallower 2.0 to 2.5 feet bgs depths. <br /> 3 <br />
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