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2900 - Site Mitigation Program
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PR0526219
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COMPLIANCE INFO
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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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Soil and Groundwater Investigation Report <br /> Catellus Property September 2006 <br /> • The Interland Corporation leaking underground storage tank(LUST)case number <br /> 390518 at 8715 West Grant Line Road,which appears to have been located adjacent to <br /> the site on the east side of Byron Road. The quantity of gasoline leaked was reported to <br /> be 0 gallon,and the case was closed on June 21, 1990. <br /> Although the EDR report listed a few other sites within 1 mile of where hazardous substances or wastes <br /> had been used,managed, discharged, or spilled,all are located beyond'/2 mile,down gradient and down <br /> slope of the site. The EDR report is provided as Appendix B. <br /> November 2005 SBC Underground Communications Line Installation. In November 2005, <br /> immediately east of the Catellus site at the intersection of West Grant Line Road and West Byron Road, <br /> HCI,Inc. (HCI)of Turlock was excavating a trench for the installation of a SBC underground <br /> telecommunications line. HCI encountered affected soil and contacted Chevron Pipeline Company. <br /> Two trenches were being excavated: one larger trench approximately 80 feet long and approximately 12 <br /> feet deep on the east side of the UPRR,and a shorter trench approximately 10 feet long and 10 feet deep <br /> on the west side of the UPRR tracks and West Grant Line Road. To install the communications line,a <br /> horizontal boring was made(using a jack—and-bore rig)underneath the rail road connecting the two <br /> trenches. <br /> Laboratory analysis of groundwater samples collected by SAIC indicated TPH quantified as crude oil <br /> (TPHc,carbon range of CIO-C36)at a concentration of 12,000 micrograms per liter(µg/L)and PAHs at <br /> concentrations ranging from 0.02 to 3.0 micrograms per liter(µg/L). A stockpile sample contained TPHc <br /> at a concentration of 1,700 milligrams per kilogram(mg/kg)and PAH constituents at concentrations <br /> ranging from 0.018 mg/kg to 1.4 mg/kg. BTEX were not detected in any soil or groundwater sample. <br /> Additionally,one soil and one groundwater sample were sent to Chevron Energy and Technology <br /> Company for fingerprint analyses. The lab results reported a TPHc concentration of 131 mg/kg in the soil <br /> and 732 pg/L in the groundwater. Fingerprint analysis revealed that the hydrocarbons in the samples <br /> were extremely biodegraded San Joaquin Valley crude oil. <br /> 3. SCOPE OF WORK <br /> In order to define the extent of affected soil and groundwater at the Catellus site, SAIC conducted the <br /> following tasks,as described in the work plan: <br /> • Completed pre-field,project setup,and strategic planning activities,including the site-specific <br /> Health and Safety Plan,the Journey Management Plan,and the clearance of subsurface utilities. <br /> • Conducted a search of DWR files to obtain information on water supply wells and prepared a <br /> summary table,which is provided in this report. <br /> • Advanced 20 primary and 11 step-out borings from which soil and groundwater samples were <br /> collected and tested by Lancaster Laboratories in Lancaster,Pennsylvania for the constituents of <br /> concern. Soil samples were analyzed for: TPHc by U.S.Environmental Protection Agency(EPA) <br /> EPA Method 8015 Modified;BTEX by EPA Method 826013; and PAHs by EPA Method 8270C <br /> Selective Ion Monitoring(SIM). Groundwater samples were analyzed for:BTEX by EPA <br /> Method 826013;TPH quantified as diesel(TPHd,carbon range CIO to C25)by EPA Method 8015 <br /> Modified with and without silica-gel cleanup;PAHs by EPA Method 8270C SIM; and Total <br /> Dissolved Solids(TDS)by EPA Method 160.1. <br /> Thirty-one borings were installed to delineate the lateral extent of affected soil and groundwater. <br /> Of those borings,in order to delineate the vertical extent of affected soil,borings SB-1, SB-5, SB- <br /> O, SB-8, SB-15,and SB-20 were advanced through the zone of affected soil until crude oil was no <br /> ANNEWAr SO <br /> 3 From Science to Solutions- <br />
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