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ARCHIVED REPORTS_XR0005649
Environmental Health - Public
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EHD Program Facility Records by Street Name
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N
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99 (STATE ROUTE 99)
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18846
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3500 - Local Oversight Program
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PR0545627
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ARCHIVED REPORTS_XR0005649
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Last modified
11/19/2024 1:50:30 PM
Creation date
4/28/2020 4:44:51 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005649
RECORD_ID
PR0545627
PE
3528
FACILITY_ID
FA0003883
FACILITY_NAME
VICTOR FINE FOODS
STREET_NUMBER
18846
Direction
N
STREET_NAME
STATE ROUTE 99
City
LODI
Zip
95240
APN
01709051
CURRENT_STATUS
02
SITE_LOCATION
18846 N HWY 99
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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v � <br /> concentrations were found to decline toward the north end ofthe tank.Most likely a spill occurred near <br /> the south end of the 12000-gallon diesel tank. <br /> Installation of Monitoring Well MW#1 (a.k.a. USTI) <br /> MW#1 was installed on 5/14/2001 to a depth of+/- 55'. Soil samples were extracted by a split spoon <br /> sampler at five intervals and the samples were analyzed for BTEX and Oxygenates(see Soil Sample <br /> Recap attached). Twenty feet of screened two inch PVC case was installed from 35' to 55'. The <br /> monitoring well was developed and the first set of water samples were taken on 5/2412001.The first set <br /> of water samples was non-detect for all analytes.The following is a report on the second set of water <br /> samples from this monitoring well. <br /> PROCEDURE <br /> Water Sampling and Analysis <br /> Water samples from MW#1 were extracted by Del Tech Geotechnical Support Services on 10/22/2001. <br /> The sample was transported under chain of custody to BSK Laboratories for analysis for oxygenates <br /> by EPA Method 8260,EPA 8015(M)and EPA 8020.Pump rates were one G.P.M.Depth to the water <br /> surface was 50.73'with a+/-4'stickup on the casing.The water table at the time of sampling is about <br /> 46' below the surface. <br /> FINDINGS <br /> This second consecutive water sample was found to be non-detect for BTEX, TPHg, TPHd, and all <br /> oxygenates. <br /> . CONCLUSIONS <br /> This second set of monitoring well water samples was analyzed by BSK Laboratories. The first set <br /> of samples extracted on 05/24/2001 was analyzed by Sherwood Labs and Entech Analytical Labs.Both <br /> sample set produced identical results. The sample sets were non-detect for all analytes. <br /> RECOMMENDATIONS <br /> The excavations for the UST removals should be backfilled with a one foot layer of compacted low <br /> permeable soil(k= l x 10-6 cm/sec)at the base of the backfill. This low permeable soil will prevent <br /> surface water migration though the contaminated plume.The remainder of the backfill may be random <br /> backfill material. <br /> i <br /> 2. REQUEST FOR NO FURTHER ACTION REQUIRED ON THIS UST SITE <br /> The Potential for Further Soil and Water Contamination by UST Leaking <br /> Potential for additional diesel contamination has been removed from the site when the UST was <br /> removed. <br /> The Extent of the Contamination Found in the Soil <br /> Only the south end ofthe 12000-gal UST was found to be leaking during removal.MW1 was located <br /> adjacent to the south end of the removal excavation to determine the vertical limits ofthe diesel plume. <br /> The diesel contamination is limited to a maximum depth of twenty-five feet below the surface. Low <br /> concentrations of TPHd were found in the ten and twenty-five foot samples.TPHd Concentrations of <br /> 868 mg/Kg and 1550 mg/Kg were found at fifteen and twenty feet of depth respectfully. The graph <br /> below illustrates TPHD concentration found in the MW#1 soil boring. <br />
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