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ARCHIVED REPORTS_2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
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ARCHIVED REPORTS_2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
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Last modified
2/10/2020 6:58:46 PM
Creation date
2/10/2020 4:41:37 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
2003 FEASABILITY STUDY REPORT AND SITE ASSESSMENT WORK PLAN
RECORD_ID
PR0542464
PE
2960
FACILITY_ID
FA0024404
FACILITY_NAME
CHEVRON FUEL TERMINAL 1001621
STREET_NUMBER
22888
STREET_NAME
KASSON
STREET_TYPE
RD
City
BANTA
Zip
95304
APN
23906015, 16, 17
CURRENT_STATUS
01
SITE_LOCATION
22888 KASSON RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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S E C O R <br /> • 2003 Feasibility Study Report and Site Assessment Work Plan <br /> July 18, 2003 <br /> Page 2 <br /> The tank farm area, which includes nine ASTs are enclosed by a 3-foot high secondary containment <br /> berm. A portion of this berm forms a spill containment area, which is located in the northern portion <br /> of the terminal. Fuel lines from the fuel storage tanks run above ground within the secondary <br /> containment area as well as below-ground within the tank-truck loading rack area (Figure 2). <br /> Retention ponds located on the north side of the terminal are used to store storm water as needed <br /> (SECOR, 2003c). <br /> Five spills have been documented at the site. The first spill occurred on June 9, 1984 around the <br /> Transmix Tank and consisted of 13,000 gallons of gasoline, diesel and heating oil. Soil was <br /> excavated immediately in the spill area until no subjective evidence of hydrocarbons remained. The <br /> second spill occurred in August of 1990 and consisted of a tank overflow of approximately 300 <br /> gallons of gasoline. The third spill occurred in August of 1998 when an unknown volume of gasoline <br /> was released as a result tank T-137 being overfilled. The fourth spill occurred in November of 1999 <br /> when an unknown quantity of red dye diesel was released from a tanker overfill at the loading racks. <br /> The last spill occurred on December 28, 2001 when a flange on a piping manifold, near MW-15A, <br /> failed and released less than 10 gallons of red dye diesel at the site (SECOR, 2003a). <br /> 2.1 Geology <br /> The site is in the Central Valley, which is a structural depression (approximately 400 miles long and <br /> 20 to 70 miles wide) extending from Redding to the Tehachapi Mountains. Water-producing deposits <br /> in the valley are primarily unconsolidated continental deposits (alluvium) of Pliocene age that extend <br /> to depths of up to 3,500 ft(USGS, 1998). <br /> Stratigraphy is relatively consistent across the site. The local geology consists of recent <br /> unconsolidated alluvial and fluvial deposits to the total depths explored of approximately 60 feet <br /> below ground surface (bgs). These sediments are a mixture of gravels, sands, silts and clays and <br /> are principal mixtures of sandy-silts and silty-clays. Specifically, lean clay extends from the surface <br /> down to approximately 10 feet bgs, which is underlain by silty sand to poorly graded sand to a depth <br /> of approximately 30 feet bgs. Records of borings adjacent to TW-5 and TW-6 indicated sandy lean <br /> clay extending to approximately 10 feet bgs with silty sand to poorly graded sand to a total explored <br /> depth of approximately 30 feet bgs. Generalized geological cross sections are included as Figures 3 <br /> and 4 (USGS, 1998). <br /> 2.2 Hydrogeology <br /> The principle source of groundwater in the area is the Tulare formation. The Tulare formation is <br /> separated into three zones, the Upper Tulare Aquifer, the Corcoran Clay Layer, and the Lower <br /> Tulare Aquifer (USGS, 1998). <br /> The Upper Tulare Aquifer lies from approximately 5 to 200 feet bgs. The Corcoran Clay consists of <br /> low permeability silty, diatomaceous clay, is generally encountered at 200 feet bgs, and is <br /> approximately 100 feet thick. The confined Lower Tulare Aquifer lies below the Corcoran Clay. No <br /> Aquitards or perched aquifers are likely based on regional geology (USGS, 1998). <br /> Site assessment activities completed at the site indicate that the Upper Tulare Aquifer is subdivided <br /> into the Upper A zone located from 5 to 15 feet bgs, the A zone located from 15 to 35 feet bgs, and <br /> I AChevron\1001621\REPO RTS\2003\2003FS\FS_2003_revD.doc <br />
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