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INSTALL 2019 TANK TOP UPGRADE
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2300 - Underground Storage Tank Program
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PR0231104
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INSTALL 2019 TANK TOP UPGRADE
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Last modified
9/22/2021 10:12:36 AM
Creation date
3/4/2019 4:21:53 PM
Metadata
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Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
INSTALL
FileName_PostFix
2019 TANK TOP UPGRADE
RECORD_ID
PR0231104
PE
2351
FACILITY_ID
FA0003863
FACILITY_NAME
SOHAL #3
STREET_NUMBER
2494
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15328008
CURRENT_STATUS
01
SITE_LOCATION
2494 E FREMONT ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Mr. Gurjinder Singh <br /> Sohal #3 <br /> February 28 , 2019 - Page 3 <br /> PROJECT HISTORY <br /> In 1996 older vintage single-walled USTs , dispensers and associated product piping were removed and <br /> replaced by the existing fueling facilities . Based upon the results of soil samples collected from beneath <br /> the location of the former USTs , dispensers , and product piping an Unauthorized Release Report (URR) <br /> was issued and the responsible party ( RP) , Shell Oil Products , US , was required to perform site <br /> investigation and cleanup activities . Based upon the results of the soil sampling , groundwater <br /> monitoring , and remedial actions , the Central Valley Water Board , in its letter dated August 11 , 2015 , <br /> issued a no further action (NFA) determination (see Attachment 2 for a Summary of Previous Work) . <br /> DISPENSER AND PIPING UPGRADE SOIL SAMPLING <br /> During February 2019 , the existing MPDs and piping was removed . M2ZM was contracted to provide a <br /> California Professional Geologist to collect 20 soil samples on February 13 and 19 , 2019 at the direction <br /> of Ms . Elena Manzo with the SJCEHD from beneath the locations of the former MPDs and product and <br /> vent piping as well as sample from a five cubic yard stockpile of excavated soil (see Figure 2 for the <br /> sample locations) . <br /> All sampling equipment was washed with a non -phosphate cleanser, pre- rinsed with tap water, and <br /> finally rinsed with deionized water prior to sampling . The soil samples were stored in 1 1 /24ch4ameter <br /> stainless steel tubes , sealed with TeflonTM liners and end caps , labeled , placed in an ice chest at a <br /> temperature of less than 4 ° C , and transported to a California State-certified laboratory for analysis . <br /> Sample identification and chain -of-custody procedures were followed for the samples to ensure sample <br /> integrity and to document sample possession from the time of collection to the ultimate destination . <br /> The sample labels identified the job number, sampler, date and time of collection , and a sample number <br /> unique to each sample . The soil samples were analyzed at BC Laboratories , Inc . ( BC Labs ) for total <br /> petroleum hydrocarbons (TPH) as gasoline using Environmental Protection Agency ( EPA) <br /> Method 8015M ; benzene , toluene , ethylbenzene , and xylenes ( BTEX) the fuel oxygenate methyl tertiary <br /> butyl ether ( MTBE) , tertiary butyl alcohol (TBA) , diisopropylether ( DIPS ) , ethyl tertiary butyl ether <br /> ( ETBE) , tertiary amyl methyl ether (TAME) ; the lead scavengers ethylene dibromide ( EDB ) , <br /> 1 , 24chloroethane ( 1 , 2-DCA) , ethanol , and naphthalene using EPA Method 82608 , and total lead using <br /> EPA Method 6010B . <br /> TPH as gasoline was detected in only one of the 20 soil samples collected beneath the MPDs and piping <br /> at a trace concentration of 0 . 56 milligrams/kilogram (mg/kg ) in the sample collected from beneath the <br /> southeast piping elbow (SEPE4) , as well as a trace concentration of 0 . 26 mg/kg in the stockpile sample <br /> (SP) . Toluene , ethylbenzene , and xylenes were also detected at trace concentrations of 0 . 019 , 0 . 0084 , <br />
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