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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0508043
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/24/2021 7:04:54 PM
Creation date
5/24/2021 11:28:39 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
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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GEOIVIATRIX <br /> any of the surrounding monitoring wells (upgradient and downgradient), which are located <br /> within an 80-foot radius of well MW-1 and are screened at depths coincident with the separate- <br /> phase petroleum (Figure 6). Data indicate that the Iow levels of TPHd detected in groundwater <br /> samples collected by Radain are due to soluble biogenic material in the groundwater samples. <br /> Groundwater samples that were treated with silica gel to remove this material did not contain <br /> detectable concentrations of TPHd. These data indicate that the residual petroleum in the <br /> subsurface, including the separate-phase petroleum and residual petroleum beneath the water <br /> table, is depleted of soluble constituents and is not providing a source of dissolved petroleum <br /> constituents to groundwater. Analysis of the separate-phase petroleum by CRTC indicate that <br /> the material is a highly weathered San Joaquin Valley Crude; the type of crude oil that was <br /> transported through the OVPL. <br /> 5.0 SCREENING-LEVEL HEALTH RISK ASSESSMENT <br /> Pursuant to the Consistent Technical Approach,the potential risks to human health posed by <br /> residual petroleum in site soil were assessed using appropriate land use scenarios. A screening- <br /> level HRA was used, as opposed to a more detailed, site-specific quantitative risk assessment, <br /> because only a few petroleum constituents have been detected in soil, no petroleum constituents <br /> have been detected in groundwater, and the areal extent of residual petroleum is limited. The <br /> screening-level HRA for soil consists of a comparing existing analytical data, which include <br /> historical data and data presented in this report, to existing risk-based criteria to assess whether <br /> the petroleum constituents detected at the site present a potential risk to human health. The <br /> screening-level HRA performed for the separate-phase petroleum consists of a qualitative <br /> evaluation of potential exposure. <br /> 5.1 SCREENING-LEVEL HEALTH RISK ASSESSMENT FOR SOIL <br /> As previously mentioned,the site is a former pump station located in a primarily light <br /> industrial/agricultural area of Vernalis, California. The potential future use of this property, <br /> which is currently vacant, is likely to be industrial. Therefore, this screening-level HRA is <br /> based on the assumption that potential exposure to petroleum constituents will occur under an <br /> industrial land use. The most likely receptors under such a land use scenario are industrial <br /> and/or construction workers. <br /> The risk-based criteria selected for the evaluation of soil are the U.S. EPA Region 9 <br /> Preliminary Remediation Goals (PRGs; USEPA Region 9, 1998). These risk-based eriteria <br /> establish concentrations of chemicals in soil that are unlikely to result in unacceptable risk to <br /> %1sf31deptdatalDoc Safe15000s1501 PST HRA Rpt.doc 10 <br />
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