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ARCHIVED REPORTS_REMEDIAL ACTION DOCUMENT
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0009025
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ARCHIVED REPORTS_REMEDIAL ACTION DOCUMENT
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Last modified
5/19/2021 2:55:48 PM
Creation date
5/19/2021 12:15:50 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
REMEDIAL ACTION DOCUMENT
RECORD_ID
PR0009025
PE
2960
FACILITY_ID
FA0004055
FACILITY_NAME
LATHROP GAS DEHYDRATOR
STREET_NUMBER
13751
Direction
S
STREET_NAME
WILLOW GLEN
STREET_TYPE
RD
City
STOCKTON
Zip
95206
APN
19105010
CURRENT_STATUS
01
SITE_LOCATION
13751 S WILLOW GLEN RD
P_LOCATION
99
P_DISTRICT
003
QC Status
Approved
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REMEDIATION COMPLETION REPORT-LATHROP DEHYDRATOR STATION 3.0 FIELD ACTIVITIES <br /> The top four feet of material(approximately 250 cubic yards) excavated from the <br /> agricultural field east of the property fence was stockpiled to the north of the excavation and <br /> along the eastern side of the fence for later reuse.Two composite samples (samples 90Stockl <br /> &90Stock2)were taken from the stockpiled native agricultural soil and analyzed for TPH-d, <br /> TPH-mo and TPH-g/BTEX to confirm that the material was free of petroleum <br /> hydrocarbons. No petroleum hydrocarbons or BTEX were detected above reporting limits in <br /> either sample. <br /> 3.6 Verification Sampling <br /> Verification soil samples were collected from the bottom and side walls of the excavation <br /> area and analyzed to document soil conditions prior to backfilling.The goal of the <br /> excavation was to remove,to the extent feasible within site constraints,soil containing <br /> petroleum hydrocarbon concentrations above the preliminary remedial cleanup goals.These <br /> goals are 10 mg/kg for TPH-g,100 mg/kg for TPH-d,1,000 mg/kg for TPH-mo,and non- <br /> detect for BTEX (not applicable if TPH-d and TPH-g are below their respective criteria), <br /> based on the Leaking Underground Fuel Tank models and the RAD (CH2M HILL 2003). <br /> Approximate locations of verification samples were determined by overlaying a 20-foot- <br /> square <br /> 0-footsquare grid system onto the excavation area.Actual sample locations were determined in <br /> the field by the field geologist to sufficiently characterize the excavation boundaries <br /> (Figure 4).Sample identifications were assigned based on the location and depth of the <br /> sample, and the order in which the samples were collected.Soil samples were analyzed for <br /> TPH-g and BTEX (EPA Methods 5030 and 8260) and TPH-d and TPH-mo (EPA Methods <br /> 8015 and 3550 Modified)by an on-site mobile laboratory (Mobile Chem Labs,Inc.).To <br /> ensure that high quality data were obtained,field and laboratory quality assurance/quality <br /> control (QA/QC) protocols were used. <br /> Sampling activities are summarized below and results of analytical testing are included in <br /> Tables 1 and 2.The approximate locations of verification samples are illustrated on Figure 3. <br /> A total of 31 soil samples were collected from the excavation during construction.The <br /> samples comprised the following: <br /> • 24 final verification samples(17 were collected from the perimeter side walls and 7 were <br /> taken from the bottom of the excavation). Analytical results are presented in Table 1. <br /> • 7 over-excavation samples (used to identify localized areas where further excavation <br /> was warranted).Two of the over-excavation samples (sampled at 8.5 feet bgs and 10 feet <br /> bgs)were not analyzed because neighboring samples collected at greater depths <br /> indicated low or no detectable levels of contamination. Analytical results are presented <br /> in Table 2. <br /> Analytical reports and chain-of-custody documents are included in Appendix D. Highlights <br /> of the results are summarized below: <br /> • 18 of the 24 final verification samples indicated concentrations that were below their <br /> respective preliminary remedial cleanup goals. <br /> SFOILATHROPCOMPLETIONREPORT 12-1.04.DOC 8 <br />
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