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COMPLIANCE INFO_1999
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2300 - Underground Storage Tank Program
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PR0231898
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COMPLIANCE INFO_1999
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Last modified
6/9/2020 8:21:13 PM
Creation date
6/3/2020 9:43:02 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
COMPLIANCE INFO
FileName_PostFix
1999
RECORD_ID
PR0231898
PE
2332
FACILITY_ID
FA0003966
FACILITY_NAME
SHARPE SITE/DEF LOG AGENCY
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
02
SITE_LOCATION
850 E ROTH RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\UST\UST_2332_PR0231898_850 E ROTH_1999.tif
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EHD - Public
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UST Closure Report <br /> Sharpe Defense Distribution Region West <br /> Lathrop,California Page 25 <br /> The sludge and rinsate from triple rinsing the tanks and overlying piping were transported by <br /> Delta Oilfield Services to Chico Drain Oil Services for treatment and disposal. The eight tanks <br /> were inerted with `dry ice' and transported by Trident Truck Lines from the site on December 23 <br /> and 24, 1998 to Ecological Control Industries' (ECI) licensed treatment and disposal facility in <br /> Richmond, California. <br /> The product and vapor return piping were triple rinsed then excavated and removed along with <br /> three ground-level, and six overhead fuel dispensers after demolishing and removing two <br /> concrete dispenser islands and their drive aprons. The rinsate was transported by American <br /> Valley Waste Oil to Industrial Service Oil Company's treatment and disposal facility in Los <br /> Angeles on February 5, 1999. The piping and dispensers were transported by Ecological Control <br /> Industries to their treatment/disposal facility in Richmond, CA on February 9. <br /> About 800 cubic yards of silty sand were removed from the UST excavation. It had no obvious <br /> petroleum product odor or discoloration. A lithologic log of a pre-UST installation borehole <br /> suggests that the original UST excavation was backfilled with native sediments, that is, with silty <br /> sand, clayey sand and sandy clay. The initial stockpiles of excavated soil along the western and <br /> southern sides of the excavation were consolidated into two stockpiles (SPA and SPB)just west <br /> of the north and south ends of the excavation. The soil in the two stockpiles were mixed, aerated <br /> and moved to the south side of 3`d Avenue (stockpile SPD) on February 3 and 10 after approval <br /> was obtained by the Base Environmental Department from the San Joaquin Valley Unified Air <br /> Pollution Control District to aerate the soil. The 60 cubic yards of soil excavated from the <br /> product and vapor return pipe trenches were stockpiled (in SPC) just south of the dispenser <br /> island sites on February 4. The stockpile was moved, upon direction from the U.S. Army Corps <br /> of Engineers, to a site about 400 feet southeast of the UST excavation. <br /> Technicians from Neil O. Anderson & Associates and later, GeoAnalytical Laboratories, Inc. <br /> collected 123 soil samples and 8 groundwater samples from the UST excavation and stockpiled <br /> soil. The samples were collected under the direction and guidance of representatives of the San <br /> Joaquin County Environmental Health Board, then later, the Central Valley Regional Water <br /> Quality Board. A total of 78 soil samples and one groundwater sample were analyzed at North <br /> State Environmental and GeoAnalytical Laboratories for TPH-G, TPH-D, BETX, oxygenates <br /> and total lead. <br /> Nineteen soil samples were collected from the floor of the UST excavation. They included three <br /> samples from beneath the concrete tie-down pad obtained by boring through the concrete in the <br /> north, central and southern parts of the excavation, and 16 from the margins of the pads. <br /> Concentrations of MTBE of 8 to 1000 µg/kg were detected in the samples from the west and <br /> southeast sides, and beneath the northern part, of the UST pads. Benzene concentrations ranged <br /> up to 100 mg/kg in the three samples in which MTBE was detected. The concentration of TPH- <br /> -D was greater than the method detection limit in only three of the samples, the highest was <br /> 200 mg/kg. Lead concentrations ranged from less than 1.0 mg/kg to 22 mg/kg. The groundwater <br /> sample collected from the floor of the UST excavation after purging about 350 gallons of water <br /> from it, contained a very high concentration of MTBE (450 µg/kg) and trace to minor <br /> N:\PROJECTS\3546\Reports\3546 UST Closure Report DraR.doc March 24,1999 <br />
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