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2900 - Site Mitigation Program
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PR0508043
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Last modified
5/27/2021 2:02:02 AM
Creation date
5/24/2021 4:13:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0508043
PE
2960
FACILITY_ID
FA0007905
FACILITY_NAME
CHEVRON PIPELINES
STREET_NUMBER
35500
STREET_NAME
WELTY
STREET_TYPE
RD
City
VERNALIS
Zip
95385
APN
25526003
CURRENT_STATUS
01
SITE_LOCATION
35500 WELTY RD
P_LOCATION
99
QC Status
Approved
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EHD - Public
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GEOMATRIX <br /> Samples were collected at five-foot intervals from each boring using a Modified California <br /> drive sampler (2.5-inch diameter by 18-inches in length). Soil cores were logged by a Geo- <br /> matrix geologist according to the Unified Soil Classification System (USCS) as presented in <br /> the American Society of Testing and Materials (ASTM) Standard D2488-90. Recovered soil <br /> was screened for organic vapors using a Photoionization Detector (PID). Boring logs are <br /> ® included in Appendix B. <br /> ® A minimum of four soil samples were collected for laboratory analysis from each boring <br /> (GMX-8, GMX-9, and GMX-1B). Soil samples were collected at depths of approximately 5 <br /> and 10 feet bgs in each boring to evaluate the presence of petroleum constituents in shallow <br /> soil. Soil samples were also collected from each boring from approximately 30 feet bgs. This <br /> depth correlates to the vadose zone/groundwater interface and the depth at which petroleum <br /> impacted soil was identified during previous investigations. Additionally, a soil sample was <br /> collected from the terminus of each boring to confirm the vertical extent of affected soil, if pre- <br /> sent(i.e., the sample was collected from a depth where field observations/measurements do not <br /> indicate the presence of petroleum constituents). No affected soil was encountered in GMX-9 <br /> and, therefore, a terminus sample was collected near the bottom of the boring. Terminus sam- <br /> ples were collected from depths of 88.5, 59.5, and 90-feet bgs in borings GMX-8, GMX-9, and <br /> GMX-1B,respectively. An additional sample was collected at a depth of 55.0 feet from <br /> GMX-8 due to field indications (i.e., PID readings above background) that petroleum hydro- <br /> carbons may be present at this depth. <br /> Soil samples were collected in 6-inch stainless steel sleeves, sealed with Teflon sheets,plastic <br /> end caps, and silicon tape. Soil samples were labeled, sealed in plastic bags, and placed imme- <br /> diately in an ice-cooled chest for subsequent delivery to the analytical laboratory, Friedman and <br /> Bruya, Inc. (F&B), of Seattle, Washington (a State-of-California certified laboratory), under <br /> Geomatrix chain-of-custody procedures. <br /> Soil cuttings are stored on-site in labeled 55-gallon steel drums pending proper disposal. <br /> Following sampling, cement grout was placed in the boreholes from the bottom to the ground <br /> surface with a tremie pipe. Grouting was performed under the supervision of a SJC-PHS <br /> inspector. <br /> 4.2 MONITORING WELL SAMPLING <br /> As per the request of the RWQCB, field activities described herein were coordinated to coin- <br /> cide with groundwater monitoring activities at the WFS Vernalis facility. On May 20, 2002, <br /> \\oakI\deptdata\Doc_Safc16000s\6447.001\ReportlUS Can Soi1GW Rpt.doc 6 <br />
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