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2900 - Site Mitigation Program
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PR0518459
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Last modified
11/30/2018 4:49:51 PM
Creation date
11/30/2018 4:03:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0518459
PE
2950
FACILITY_ID
FA0013913
FACILITY_NAME
HERITAGE SQUARE
STREET_NUMBER
640
Direction
N
STREET_NAME
SAN JOAQUIN
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13916110
CURRENT_STATUS
01
SITE_LOCATION
640 N SAN JOAQUIN ST
QC Status
Approved
Scanner
TMorelli
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EHD - Public
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*VWV %.O� <br /> LW No Further Action Request <br /> 640 N,San Joaquin Street,Stockton,CA <br /> s October 9,2002 <br /> Page 2 <br /> On May 23, 2002 buried fuel pipes at the site were traced by a line locating service from the east side of <br /> the school building, through the building basement, to the north side of the building along E. Park Street. <br /> The fuel lines were also traced to a natural gas-tired boiler located inside the school building. A backhoe <br /> ;+ was used to confirm the location of the fuel pipes north of the building. On May 24, 2002 a UST (TK-1) <br /> at an approximate depth of eight feet below ground surface (bgs) was partially excavated at this location <br /> north of the school building (Figure 2). Visual inspection of the contents of TKI confirmed that the UST <br /> v stored World War II-era bunker oil,a motor oil-like heavy hydrocarbon. <br /> Condor submitted a Phase II Environmental Site Assessment Work Plan dated June 5, 2002 to the San <br /> y Joaquin County Environmental Health Department (SJCEHD). The purpose of the work was to evaluate <br /> the potential for petroleum hydrocarbon contamination in soil and/or groundwater related to the UST <br /> (TK-1). Ms. Margaret Lagorio, the Supervising Environmental Health Specialist with the SJCEHD gave <br /> verbal approval of the Work Plan on June 7, 2002. <br /> On June 10 and 11, 2002 Condor personnel supervised the advancement of four direct push borings (B-I <br /> through B-4) to collect soil samples and a groundwater sample from the vicinity of TK-1, and four hand <br /> auger borings (C-1 through C-4) to collect soil samples from below the segment of underground piping <br /> beneath the concrete basement floor of the school building. The boring locations are shown in Figure 2. <br /> Borings B-1, B-2, and B-4 were advanced to approximate depths of 20 feet bgs; groundwater was not <br /> LW encountered prior to termination of these borings. Boring B-3 was advanced to a depth of 36 feet bgs and <br /> a groundwater sample was collected. Barings C-1 through C-4 were advanced to approximately two feet <br /> ' beneath the underground piping; a soil sample was collected at this depth from each of these borings. <br /> Sample locations with analytical results for borings C-1 through C-4 and B-1 through B-4 are shown in <br /> Figure 3. Sample depths for borings B-I through B-4 are indicated on the geologic logs provided in <br /> Appendix C. <br /> LW <br /> Discrete soil samples collected from borings B-1 through B-4 were analyzed for TEPH-D, TEPH-MO, <br /> TEPH-K, BTEX, and MTBE. Soil samples collected from hand auger borings C-I through C-4 were <br /> analyzed for TPH-G and total lead (Pb) in addition to the aforementioned hydrocarbon constituents. The <br /> discrete soil sample collected from boring B-3 with the highest contaminant concentrations (3572D-B'3- <br /> 15.5') was further analyzed for CAM 17 Metals. The groundwater sample collected from boring B-3 was <br /> analyzed for TEPH-D, TEPH-MO, TEPH-K, BTEX, and MTBE. Laboratory analytical results for soil <br /> and groundwater samples and CAM 17 Metals are provided in Table D and Table E, respectively, <br /> Appendix B. <br /> L Field observations and photoionization detector(.PID) measurements suggested that the soil in borings B- <br /> 1, B-2, B-4, C-1, C-2, C-3, and C-4 was not impacted by petroleum hydrocarbons. Laboratory analytical <br /> results of all the soil samples collected from these borings indicated that all of the analytes of concern <br /> a. were not detected at or above the laboratory reporting limits. TEPH-MO was detected in the first sample <br /> collected from boring B-3 at 15 feet bgs, and concentrations of toluene, ethyl benzene, total xylenes, <br /> TEPH-D, and TEPH-MO were detected in the soil sample collected at 15.5 feet bgs (Figures 3 and 4, <br /> Appendix A). TEPH-MO was detected in the groundwater sample collected from boring B-3. MTBE was <br /> not detected in any soil or groundwater samples collected at the site. Condor described the results of the <br /> Phase 11 Environmental Site investigation in the Phase II Environmental Site Assessment Report, dated <br /> July 3, 2002. <br /> a.. <br /> ;/� CONDOR <br />
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