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COMPLIANCE INFO_PRE 2019
Environmental Health - Public
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PR0508111
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COMPLIANCE INFO_PRE 2019
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Last modified
5/4/2021 2:01:53 PM
Creation date
5/4/2021 1:56:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
FileName_PostFix
PRE 2019
RECORD_ID
PR0508111
PE
2950
FACILITY_ID
FA0007946
FACILITY_NAME
POSDEF POWER COMPANY
STREET_NUMBER
2526
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14503009
CURRENT_STATUS
01
SITE_LOCATION
2526 W WASHINGTON ST
QC Status
Approved
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EHD - Public
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LETTER REPORT — WASTE OIL TANK SITE ASSESSMENT <br />POSDEF Power Company, 2526 West Washington Street, Stockton <br />October 29, 1998 <br />Page two <br />On or about April 19, 1998, the tank was inspected and tested. The test indicated that <br />the secondary containment had failed; however, the primary containment had not failed. <br />The source of water in the interstitial space resulted from the secondary containment <br />failure and the high groundwater beneath the site. Based on these findings, POSDEF <br />began to formulate a plan to abandon the tank in place. The decision to abandon the <br />tank in place rather than removing the tank is based on the close proximity of a concrete <br />pedestal that structurally supports a large turbine. As such, tank removal would <br />compromise the structural integrity of this power generating source. <br />Scope of Work <br />The objective of this project was to collect soil and possibly groundwater-grab samples <br />in close proximity to the bottom of the tank, at a depth of approximately five (5) feet, to <br />assess the potential for in-place closure. To achieve this objective, two soil borings <br />were advanced with a hand auger as close to each end of the tank as possible. <br />To access the subsurface soil at both soil boring locations, the 16-inch thick concrete <br />surface was first cored by Cal-West Concrete Coring. The first soil boring (SB-1) was <br />positioned approximately one foot south of the southwest corner of the tank. An <br />aboveground clean oil tank and aboveground piping prevented access to the west end <br />of the tank. The second soil boring (SB-2) was positioned approximately two feet east <br />of the eastern end of the tank. Aboveground piping prevented closer access to the end <br />of the tank. The locations of both soil borings are shown on Figure 1. <br />In accordance with the attached PHS/EHD drilling permit, both soil borings were <br />advanced with a hand auger to a total depth of approximately five feet below ground <br />surface (bgs). At the total depth of five feet, a soil sample was collected from both soil <br />borings using a slide hammer lined with a brass sleeve. The sample sleeve was capped <br />with Teflon® sheets and plastic end caps, labeled, and stored in an iced cooler for <br />transport under chain-of-custody documentation to GeoAnalytical Laboratories, Inc. <br />(GeoAnalytical), a state of California certified hazardous waste testing laboratory <br />(Certification #1157). <br />GeoAnalytical analyzed both soil samples for Total Petroleum Hydrocarbons (TPH)-as- <br />gasoline, TPH-as-diesel, TPH-as-kerosene, and TPH-as-motor oil by EPA 8015M, <br />benzene, toluene, ethylbenzene and xylenes (BTEX) by EPA Method 8020M, <br />chlorinated hydrocarbons by EPA Method 8240, metals (Cadmium, Chromium, Lead, <br />Nickel and Zinc) by EPA Methods 6010 and 7420, and PCBs by EPA Method 8080.
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