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2900 - Site Mitigation Program
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PR0544431
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Last modified
5/7/2019 3:06:32 PM
Creation date
5/7/2019 2:33:11 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0544431
PE
2952
FACILITY_ID
FA0006730
FACILITY_NAME
CLAUDE C WOOD CO
STREET_NUMBER
681
Direction
E
STREET_NAME
LOCKEFORD
STREET_TYPE
ST
City
LODI
Zip
95240
APN
04905002
CURRENT_STATUS
02
SITE_LOCATION
681 E LOCKEFORD ST
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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Site Closure Report 5 <br /> Fortner Claude C.Wood Construction Yard,681 East Lockeford Street,Lodi,CA November 16, 1999 <br /> One sample, CCW-WOT-1, was collected from the tank pit floor at a depth of 6 feet below the <br /> tank invert and 12 feet below surface grade (Figure 3). An additional sample, CCW-WOT-2, <br /> was also collected from the stockpiled soil generated during the tank removal. Both samples <br /> were transported under chain of custody to American Environmental Network, Inc. for analyses <br /> Due to presence of stained soil in the waste oil tank pit floor, the SJCEHD filed an Underground <br /> Storage Tank Unauthorized Release (leak)/Contamination Site Report for the waste oil tank <br /> (Appendix B). The type of fuel released at the site was listed as diesel. <br /> 3.2 Waste Oil UST Removal Soil Sample Analyses <br /> The tank pit floor sample and stockpile sample were analyzed for the following constitents: <br /> benzene, toluene, ethylbenzene, xylenes (BTEX)via EPA Method 8020, total petroleum <br /> hydrocarbons-as-gasoline (TPHg), TPH-as-diesel (TPHd), and TPH-as-motor oil(TPHmo)using <br /> EPA Method 8015 modified, volatile aromatic hydrocarbon compounds using EPA method <br /> 8010, PCB's using EPA Method 8080,heavy metals cadmium (Cd),total chromium (Cr), lead <br /> (Pb),Nickel (Ni), and zinc(Zn) using EPA method 6010; and chromium VI (Cr VI)Using EPA <br /> method 7196. As shown in Table 1, contaminants identified in the sample collected from the <br /> tank pit floor were motor oil at 400 milligrams per kilogram (mg/kg), diesel at 3,300 mg/kg, <br /> gasoline at 150 mg/kg, and combined BTEX at 1.167 mg/kg. The heavy metals analyzed for <br /> were either not present above the laboratory reporting limit or present at background <br /> concentrations. No volatile aromatic hydrocarbons or PCB's were reported with concentrations <br /> above the laboratory reporting limit. A summary of the stockpile soil sample results are <br /> presented in Table 2. A copy of laboratory report is included in Appendix C. <br /> 3.3 Soil Over-Excavation and Sample Collection <br /> Due to the presence of petroleum hydrocarbons in the soil sample collected from the waste oil <br /> tank pit and the surface stains observed with the above ground tank farm, over-excavation of the <br /> soil was conducted in October 1994. During excavation, hydrocarbon stained soil were observed <br /> by ASTA from the surface and discontinuously extending to approximately 22 feet bgs. The <br /> contaminated soil was easily identified by staining and odor. As shown in Figure 4, the final <br /> excavation dimensions were 41 feet wide by 62 feet long, and extended to depths of 18 to 22 feet <br /> bgs. A total of 2,000 cubic yards of soil was generated and stockpiled during the excavation of <br /> AJ-ClosureRpt.RPT.wpd <br />
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