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ARCHIVED REPORTS_XR0007664
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545739
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ARCHIVED REPORTS_XR0007664
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Last modified
6/8/2020 12:24:23 PM
Creation date
6/8/2020 12:20:29 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007664
RECORD_ID
PR0545739
PE
3528
FACILITY_ID
FA0006002
FACILITY_NAME
UNION OIL #6348
STREET_NUMBER
3788
Direction
N
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95376
APN
21225002
CURRENT_STATUS
02
SITE_LOCATION
3788 N TRACY BLVD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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S5# 6348, Tracy <br /> QM Report, 411192 <br /> . pit was overexcavated, however, overexcavation was restricted by the proximity <br /> of the pit to the product storage tanks <br /> In July, 1991 four monitoring wells were installed, and additional <br /> soil borings were drilled Hydrocarbons as gasoline (TPHg) were identified to <br /> soil near the fill spout of the south underground product storage tank. <br /> Additional borings were drilled to identify the lateral extent of this contamination <br /> Following well development, groundwater was sampled from the <br /> four wells on July 15, 1991 and again on August 15, 1991 Due to the fact that <br /> contamination was reported at MW-4 from the July sampling and was not <br /> detected from the August sampling, that well alone was again sampled on <br /> September 11 , 1991 No TPHg or BTEX was detected at that time, or from <br /> subsequent sampling events Laboratory results are summarized in Table 2 <br /> FIRST QUARTER, 1992 ACTIVITIES <br /> Following discussion with San Joaquin County Department of <br /> Public Health personnel, MW-1 has been dropped from the sampling program <br /> because, based on previous sampling, that well is situated to an upgradtent <br /> position and no contamination appears to have affected the location from on or <br /> . off site <br /> On March 13, 1992, all four wells were monitored by taking water <br /> level measurements and examining the water for any abnormalities Materials <br /> and instruments used for monitoring and for collecting samples were washed <br /> between each well with biodegradable soap and tap water and rinsed to <br /> distilled water The measurement of groundwater depth was made from the top <br /> of the PVC casing using an electronic water sounder. A bailer was lowered into <br /> the well to obtain a water sample which was observed for the presence of free <br /> product, sheen, or odor <br /> MW-2, MW-3, and MW-4 were bailed until at least two of the three <br /> parameters of temperature, pH, and conductivity had stabilized to within 10% of <br /> the previous reading Following this purging, water was collected to fill three 40 <br /> ml VOA vials so that no air remained in the vial following closure with a teflon- <br /> lined cap The vials were labelled, placed on ice, and sent to a state-certified <br /> laboratory under chain-of-custody control for analysts of TPHg and BTEX <br /> Fl DINGS <br /> Water-level measurements indicate that on March 13, 1992 the <br /> depth from the surface to the groundwater averaged approximately 7 feet The <br /> flow direction was to the N54W with a gradient of 0 0028 foot per foot These <br /> Mand earlier measurements are listed in Table 1 <br /> -2- <br />
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