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ARCHIVED REPORTS_XR0002382
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545195
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ARCHIVED REPORTS_XR0002382
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Last modified
1/23/2020 3:23:40 PM
Creation date
1/23/2020 2:59:56 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002382
RECORD_ID
PR0545195
PE
3528
FACILITY_ID
FA0002915
FACILITY_NAME
TRACY MARKET INC
STREET_NUMBER
15
Direction
E
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
21435004
CURRENT_STATUS
02
SITE_LOCATION
15 E GRANT LINE RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Project 113-26-04,05,Page 9 <br /> November 17, 1995 <br /> After each well was developed, the bailer, pump, and down hole wiring and tubing <br /> were washed and operated in buckets with a TSP solution and rinsed twice in tap <br /> water Washing water was added to the drums <br /> Well purging and sampling was performed on September 25, 1995 First the well <br /> caps were removed from the wells The depth to water was measured at each <br /> location using an electronic sounding device with 0.01 feet accuracy. The sounder <br /> probe was washed and rinsed between wells <br /> Purging of the wells was accomplished by the removal of about 4-5 well volumes of <br /> groundwater (about 8-12 gallons) from wells MW-1, 2, 3, 5, 6, and 7 via an electric <br /> submersible pump operating at about 1-15 gpm About 40 gallons was removed <br /> from MW-8 Free product thickness of 0.02' was measured at MW-4 so the well was <br /> not sampled. None of the wells was drawn down more than a few inches during <br /> pumping at that rate. <br /> Groundwater was pumped directly into two septum vials per well The vials were <br /> filled until no head space remained and a positive meniscus was apparent. The vials <br /> were sealed, labeled, and placed into a cooler with ice for transport to the state <br /> certified analytical lab Chain of custody documentation and procedures were <br /> initiated <br /> Groundwater grab samples were obtained from the soil borings with a bailer The <br /> borings had been advanced about one foot beyond first encountered groundwater <br /> with the hand auger The bailer was cleaned between borings Groundwater was <br /> poured from the bailer into vials and handled as described above. <br /> At the Iab, all groundwater samples were analyzed for TPH as gasoline and BTEX <br /> Well Surveying, Groundwater Flow Direction <br /> The marks/notches at the top of the well casings were surveyed in October 1995 by a <br /> State Licensed Land Surveyor (Benchmark Consultants) to the nearest 0.001 foot, <br /> rounded to the nearest 0 01 foot (Table 2 Well Elevation Data). Elevations were shot <br /> from an established vertical datum (city benchmark) From the well elevations and <br /> depth to groundwater measurements, the elevation of the potentiometric surface <br /> was established relative to mean sea level (MSL) The top of casing elevations for <br /> the eight monitor wells range from 27 06 at MW-4 up to 29.28 feet above MSL at <br /> MW-3 Groundwater elevations at the wells ranged from 21 00 feet MSL at MW-1 <br /> and MW-4, to 2121 feet at MW-3 (Figure 3. Groundwater Elevation Data) <br /> Parker Environmental Services, 190 East 7th Street, Pittsburg, CA 94565-2317 <br /> Phone (510) 439-1024 Fax (510) 439-2566 <br />
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