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PR0526219
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Last modified
2/19/2020 4:39:32 PM
Creation date
2/19/2020 2:02:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0526219
PE
2960
FACILITY_ID
FA0017741
FACILITY_NAME
CATELLUS/CHEVRON PIPELINE ENV MGMT
STREET_NUMBER
14824
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
953047216
APN
20927005
CURRENT_STATUS
01
SITE_LOCATION
14824 W GRANT LINE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Scott Mansholt - 2 - 6 November 2006 <br /> Chevron — Catellus Property <br /> The purpose of the Catellus investigation was to evaluate and delineate the lateral and vertical <br /> extent of petroleum hydrocarbon impacts as the result of crude oil leaks from the former OVP <br /> and/or TAOC pipelines. Borings were advanced and soil and groundwater samples collected <br /> for analysis of the petroleum hydrocarbons of concern associated with the former pipelines. <br /> Current Investigation <br /> In June 2006, thirty-one soil borings were advanced, 45 soil samples and 27 groundwater <br /> samples were collected and submitted for analysis. Soil analytical results were compared to <br /> the U.S. EPA Region 9 Preliminary Remediation Goals Table (PRGs) and the Regional Water <br /> Quality Control Board (Region 2) - Environmental Screening Levels (ESLs) provided in <br /> Screening for Environmental Concerns at Sites with Contaminated Soil and Groundwater, <br /> 2005 (Interim Final). The analytical results from this investigation were compared to the <br /> respective PRGs and/or ESLs to estimate contaminant concentrations in soil, groundwater, <br /> and air that are considered protective of human health over a lifetime. Additionally, the Water <br /> Quality Objectives (WQOs) provided in the 2004 Regional Water Board document entitled <br /> Beneficial Use-Protective Water Quality Limits for Components of Petroleum-Based Fuels <br /> were considered in conjunction with the ESLs when determining the extent of affected <br /> groundwater. The lowest and most conservative PRG, ESL, and/or WQO constituent <br /> concentrations were considered. <br /> Soil Results <br /> Analytical results for the 45 soil samples collected and submitted for TPH as crude oil (TPHc) <br /> and BTEX (benzene, toluene, ethylbenzene and xylenes) constituents reported the following <br /> TPHc concentrations: 34 samples were ND (less than the method detection limit), five were <br /> less than 100 mg/kg, one was less than 1,000 mg/kg, two at 2,200 and 2,300 mg/kg and two <br /> were 13,000 and 17,000 mg/kg. The latter two results were from boring SB-8 at 2-feet and <br /> 9-feet, respectively, including benzene ND at <0,63 mg/kg and 0.64 mg/kg reported in these <br /> two samples. Separate phase crude oil was observed in SB-8 soil field samples to <br /> approximately 15-feet. Other than the SB-8 benzene detections, BTEX was ND for the <br /> remaining samples. The residential PRG for benzene in soil is 0.64 mg/kg and the ESL is <br /> 0.044 mg/kg; the industrial PRG for benzene is 1 .4 mg/kg. <br /> The majority of the polynuclear aromatic hydrocarbons (PAHs) generally, were ND except for <br /> samples from borings having elevated TPHc concentrations, in particular the 2-foot and 9-foot <br /> samples from SB-8. The PAH results for these two samples exceeded both the PRGs and <br /> ESLs for several of the individual compounds. Additionally, the remaining PAHs reported low <br /> concentrations at or slightly above the respective MDLs. Of these, two samples from SB-5 <br /> and SB-6 were equal to or slightly above the benzo (a) pyrene and naphthalene PRGs and/or <br /> ESLs for samples from 4-feet and 6-feet, respectively. Analysis of samples from beneath <br /> these depths was ND for PAH compounds. <br /> According to the report, TPHc concentrations in soil were identified as follows: <br /> • SB-6 at 6-feet - 2,200 mg/kg TPHc; the lateral extent of affected soil surrounding SB-6 <br /> has been delineated by nearby up/crossgradient borings SB-5, 7, 36, and 37, and by <br /> downgradient borings SB-23, and SB-24. <br />
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