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ARCHIVED REPORTS_XR0002905
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3500 - Local Oversight Program
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PR0545252
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ARCHIVED REPORTS_XR0002905
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Last modified
1/31/2020 3:26:07 PM
Creation date
1/31/2020 2:01:11 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002905
RECORD_ID
PR0545252
PE
3528
FACILITY_ID
FA0002232
FACILITY_NAME
QUIK STOP MARKET #3132*
STREET_NUMBER
3555
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
071-180-20
CURRENT_STATUS
02
SITE_LOCATION
3555 W HAMMER LN
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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Quik Stop Market No. 132 July 28, 1992 <br /> Project No. 3-49132-33 Page 2 <br /> headspace gas injected into the gas chromatograph for analysis. For a more detailed <br /> description of the sampling and analytical methods, see the Tracer Research <br /> Corporation report attached as Appendix A. <br /> Field Work <br /> Originally, 13 locations were selected for soil gas or shallow groundwater sampling. <br /> Due to dense soils and resultant longer sampling times, of these, 10 were sampled <br /> (Figure 2). After penetration to the desired depth or refusal, the probe was withdrawn <br /> with a vacuum applied to the interior of the probe. A loss of vacuum would indicate <br /> that the open end of the probe was in a more permeable soil and air or groundwater <br /> was entering the pipe. Field notes were maintained as to the relative resistance of probe <br /> penetration and vacuum loss. These operations are summarized in Table 1. After <br /> sampling was completed, the hole was backfilled with a mixture of sand and cement to <br /> within approximately 3 inches of the surface where a cold-patch asphalt plug was <br /> pounded into the remaining hole. <br /> ' Analytical Results <br /> Subsurface probes were inserted in 10 locations, soil gas samples were obtained in seven <br /> locations, groundwater samples were obtained in six. Of these, both soil gas and <br /> groundwater samples were collected at three locations. Low concentrations of gasoline- <br /> related compounds were detected in three of the soil gas samples and two of the <br /> groundwater samples (Tables 2 and 3). <br /> Discussion <br /> ' At all locations, it was attempted to drive probes to 18 to 20 feet deep. This was <br /> accomplished at all locations except locations 3 and 6 where the probes met with refusal <br /> at shallower depths. An examination of the information from Tables 1, 2, and 3 reveal <br /> a pattern. During the sampling process it was noted that at a depth of approximately 10 <br /> to 12 feet, a marked increase in resistance to probe penetration occurred. In a previous <br /> investigation (Exceltech, Inc., July 1991), it was noted that at most areas, excluding <br /> those areas where a perched aquifer was located, a clay bed was encountered at about 10 <br /> to 12 feet and extended to 16 to 20 feet. The increased resistance below 8 to 14 feet <br /> and vacuum loss above 9 to 14 feet, would support the presence of a denser clay bed at <br /> depths below 8 to 12 feet. This clay is an aquitard and the increased resistance observed <br /> in the probe penetration is interpreted as representing the probe contacting this <br /> ' aquitard. The detected gasoline-related compounds were obtained from depths at <br /> j approximately 8 to 12 feet which would suggest that rainwater and any petroleum <br /> hydrocarbons present would encounter resistance to downward migration at this clay. <br />
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