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Environmental Health - Public
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2900 - Site Mitigation Program
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PR0536234
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/28/2019 4:28:07 PM
Creation date
5/28/2019 4:23:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0536234
PE
2950
FACILITY_ID
FA0020819
FACILITY_NAME
CHEROKEE TRUCK STOP (FORMER)
STREET_NUMBER
3655
Direction
E
STREET_NAME
CHEROKEE
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
13206009
CURRENT_STATUS
01
SITE_LOCATION
3655 E CHEROKEE RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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CLEANUP AND ABATEMENT ORDER NO. 91- 722 -3- <br /> FOR DELTA TRUCK SALES <br /> STOCKTON, SAN JOAQUIN COUNTY <br /> 13. The disposal by the Discharger of wastewaters and sludges containing <br /> hazardous wastes threatens to result in a condition of pollution of ground <br /> water underlying the facility. The Discharger threatens to permit wastes <br /> generated from past steamcleaning activities at the site to be discharged <br /> into waters of the state. Pollution means an alteration of the quality of <br /> waters of the state by waste to a degree which unreasonably affects such <br /> waters for beneficial uses (Water Code, Section 13050(1 )) . <br /> 14. The TPCA requires that all persons discharging liquid hazardous wastes or <br /> hazardous wastes containing free liquids into a surface impoundment after <br /> 1 January 1985 file a Hydrogeological Assessment Report (HAR) in <br /> accordance with Sections 25208.7 and 25208.8 of the H&SC. <br /> 15. By letter of 16 September 1987 board staff informed the Discharger of <br /> their responsibilities under the TPCA, including the submittal of a <br /> complete and accurate HAR by 1 January 1988, and ceasing discharge by <br /> 30 June 1988. <br /> 16. The Discharger attempted to comply with this request. The exact location <br /> and dimensions of the buried SI were not determined prior to excavation of <br /> the hazardous oily wastes. In June 1989 and June 1990 approximately 5,000 <br /> yards of material were excavated from the surface impoundment and <br /> stockpiled on site. The stockpiled material consisted of a combination of <br /> native clayey soil , oily waste and paint from the surface impoundment <br /> bottom, and the concrete construction debris that was used to fill in the <br /> surface impoundment in 1985. An undetermined amount of lead contaminated <br /> oily waste still remained within the unexcavated sidewalls of the former <br /> landfilled area. <br /> 17. The Discharger submitted a HAR on 14 December 1990. Additional quarterly <br /> monitoring of wells and definition of the lateral extent of the <br /> contamination in the former landfill area will complete the HAR. The HAR <br /> included one round of ground water monitoring. <br /> 18. Although the Discharger stopped placing wastes into the impoundment, <br /> hazardous wastes continued to be stored or disposed of in the SI and <br /> landfilled area. The Board required the Discharger to come into <br /> compliance with Section 25208.4 of the H&SC by 15 March 1989. Ceasing <br /> discharge included the removal and proper disposal of hazardous wastes and <br /> hazardous wastes containing free liquid from the surface impoundment. <br /> 19. The Discharger complied with the requirement to cease discharge by <br /> excavating the buried surface impoundment and surrounding soils. However, <br /> residual hazardous waste constituents remain in the landfill area <br /> surrounding the former impoundment. The exact location and dimensions of <br /> the buried surface impoundment were not determined prior to excavation of <br /> the hazardous oily wastes. Roughly 5,000 cubic yards of material were <br /> excavated from the surface impoundment and stockpiled on site in June 1989 <br /> and June 1990. The stockpiled material consists of a combination of <br />
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