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Last modified
5/24/2021 11:19:37 AM
Creation date
5/24/2021 10:29:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4800 – General/Other 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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Mr.Mike Oliphant—CEMC <br /> Soil and Groundwater Investigation Report March 29,2013 <br /> Ahern Road—Vernalis Page 3 of 6 <br /> APN 255-180-15. Borings SB-7 through SB-9 were advanced to depths ranging from <br /> 40 to 42.5 feet bgs. There were no indications of hydrocarbons in these borings. <br /> The boring locations are shown on Figure 2. The boring logs, which describe Unified <br /> Soil Classification System descriptions, PID readings, and observations of hydrocarbon- <br /> affected soil and/or groundwater, are provided as Attachment C. SAIC collected soil <br /> samples from less than 10 feet bgs and just above first-encountered groundwater for <br /> analytical sampling. An additional soil sample was collected from borings SB-1 through <br /> SB-6 between 10 feet bgs and first-encountered groundwater. Due to the presence of <br /> SPO in borings SB-1 through SB-3, grab groundwater samples from first-encountered <br /> groundwater were not collected from these borings. A depth-discrete groundwater <br /> sample was collected from SB-2 from at 84 feet bgs. A representative of the SJCEHD <br /> was on site during borehole abandonment activities. <br /> ANALYTICAL METHODS AND SCREENING LEVELS <br /> SAIC submitted the soil and groundwater samples to Eurofins Lancaster Laboratories, <br /> LLC, for the following analyses: <br /> • Total petroleum hydrocarbons (TPH)quantified as crude oil (TPHc; carbon range <br /> C 10 to C36) using United States Environmental Protection Agency(EPA) Method <br /> 8015B Modified (this analysis performed on soil only); <br /> • TPH quantified as diesel (TPHd; carbon range CIO to C25) using EPA Method <br /> 8015B Modified with and without silica-gel cleanup if detected, and solely <br /> without silica-gel cleanup if not detected(this analysis performed on groundwater <br /> only); <br /> • Benzene,toluene, ethylbenzene, and total xylenes (BTEX) using EPA Method <br /> 8260B (groundwater by 25-milliliter purge); and <br /> • Polynuclear aromatic hydrocarbons (PAHs)using EPA Method 8270C (soil by <br /> selective ion monitoring and groundwater by large-volume injection). <br /> Groundwater analytical results were compared to the lowest,most conservative San <br /> Francisco Bay RWQCB Environmental Screening Levels?(ESLs) and interpreted <br /> narrative water quality objective (WQO) values for delineation purposes. Under the <br /> California Water Code, WQOs are numerical or narrative limits for constituents or <br /> characteristics of water designed to protect beneficial uses of a body of groundwater or <br /> surface water. EPA Regional Screening Levels9 (RSLs) and ESLs are used to evaluate <br /> soil laboratory analytical data. <br /> 7. San Francisco Bay RWQCB,2008. Screening for Environmental Concerns at Sites with Contaminated Soil and <br /> Groundwater(Interim Final). May. <br /> 8. Central Valley RWQCB,2007. Water Quality Control Plan(Basin Plan)for the Sacramento River Basin and San <br /> Joaquin River Basin(Fourth Edition). October. <br /> 9. EPA,2008. Regional Screening Levels(RSL)for Chemical Contaminants at Superfund Sites. September. <br />
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