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REMOVAL_2023
Environmental Health - Public
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2300 - Underground Storage Tank Program
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PR0231233
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REMOVAL_2023
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Entry Properties
Last modified
9/17/2025 2:48:32 PM
Creation date
7/29/2024 1:23:00 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2300 - Underground Storage Tank Program
File Section
REMOVAL
FileName_PostFix
2023
RECORD_ID
PR0231233
PE
2361
FACILITY_ID
FA0002479
FACILITY_NAME
7-ELEVEN INC #17334
STREET_NUMBER
4501
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11017004
CURRENT_STATUS
02
SITE_LOCATION
4501 N PERSHING AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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UST SYSTEM REMOVAL REPORT <br />7-ELEVEN STORE NO. 17334, 4501 N. PERSHING AVENUE, STOCKTON, CA 95207 <br />Field Activities <br />March 3, 2023 <br />v:\1858\active\185851132\05_report_deliv\deliverable\reports\2023_rpt_17334_ust.docx 3.1 <br /> <br />3.0 FIELD ACTIVITIES <br />3.1 UST REMOVAL ACTIVITIES <br />On January 26, 2023, Stantec observed the removal of two 10,000-gallon double-walled steel USTs at the site. The <br />USTs were triple rinsed on site and were approved for removal by the EHD. The tanks were transported to Sims <br />Metal Management in Richmond, California for destruction and disposal. The product piping was also triple rinsed on <br />site and transported to US Ecology in Beatty, Nevada for disposal. The rinsate manifest and disposal documentation <br />for the USTs and piping are provided in Appendix A. <br />The UST overburden soil was stockpiled during the UST removal activities and reused in the excavation as backfill. <br />Clean, imported fill (sand and road base) was placed into the remainder of the excavation in six to eight-inch-thick <br />lifts, and compacted using a roller. The site surface was completed with asphalt. The soil compaction report is <br />included in Appendix B. <br />3.2 SOIL AND GROUNDWATER SAMPLING ACTIVITIES <br />On January 26, 27, and 30, 2023, Stantec personnel collected eleven soil samples under the direction of the San <br />Joaquin County EHD. Three additional soil samples were collected from the UST excavation sidewalls. Soil samples <br />were obtained at depths ranging from two to six feet bgs beneath the former dispenser islands and product piping, at <br />approximately 14 feet bgs from the bottom of the UST excavation, and at depths ranging from four to six feet from the <br />excavation sidewalls. The soil samples were collected from the excavator bucket. The soil samples were <br />immediately placed in clean laboratory supplied glass jars. Each jar was completely filed to minimize headspace and <br />sealed with a Teflon lined screw cap. Each sample was labeled and placed on ice in a cooler. <br />Groundwater was encountered within the excavation during tank replacement activities at approximately 11 feet bgs. <br />One groundwater sample was collected from the UST excavation. The groundwater sample was collected with a <br />disposable bailer and immediately placed in clean laboratory supplied containers. The sample was labeled and <br />placed on ice in cooler. <br />3.3 ANALYTICAL METHODS <br />The soil and groundwater samples were delivered under chain-of-custody to PACE Analytical National (PACE), a <br />California state-certified laboratory located in Mount Juliet, Tennessee. Soil and groundwater samples were analyzed <br />for total petroleum hydrocarbons as gasoline range organics (TPH-GRO) by Environmental Protection Agency (EPA) <br />Test Method 8015, and for BTEX, MTBE, tert-amyl methyl ether (TAME), tert-butyl alcohol (TBA), diisopropyl ether <br />(DIPE), ethyl-tert-butyl ether (ETBE), and full scan volatile organic compounds (VOCs) by EPA Test Method 8260B. <br />Soil and groundwater samples were also analyzed for lead by EPA Test Method 6010B and methanol by EPA Test <br />Method 8015M.
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