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ARCHIVED REPORTS_XR0004383
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PR0539293
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ARCHIVED REPORTS_XR0004383
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Last modified
11/20/2019 3:28:14 PM
Creation date
11/20/2019 3:20:49 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004383
RECORD_ID
PR0539293
PE
2957
FACILITY_ID
FA0022465
FACILITY_NAME
VALLEY MOTORS
STREET_NUMBER
800
Direction
E
STREET_NAME
MAIN
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
800 E MAIN
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\wng
Tags
EHD - Public
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Perhaps these peaks are due to the presence of a non-gasoline compound, such as a chlorinated <br /> hydrocarbon, several of these have been detected in VM-I and VM-2 in the past <br /> 4.3 Concentration Trends r <br /> Figure 4 shows hydrocarbon concentrations in VM-2 since monitoring began in July 1996 This <br /> graph shows a highly unusual trend both TPH-g and total BTEX concentrations have increased <br /> over time Although low concentrations have been recorded on several occasions, the overall <br /> trend is clear Presently, concentrations are approximately 1 order of magnitude greater than they <br /> were in 1996 <br /> A similar trend of increasing concentrations has not been observed in the other wells in VM-1, <br /> for example, concentrations remained relatively constant from 1995 through 1998, but then the <br /> TPH-g concentration spiked to its highest level in early 1999 (Figure 5) BTEX concentrations <br /> did not follow suit, and actually declined in early 1999 and remained low until early 2000 After <br /> peaking in early 1999, the TPH-g concentration began a long decline, and the present <br /> concentration appears to be slightly below the initial level in 1995 However, BTEX began rising <br /> as TPH-g was declining At the end of 2000, both TPH-g and BTEX concentrations were very <br /> low, and since then they have risen and fallen in phase This in-phase pattern is a more typical <br /> situation, and easier to interpret than the out-of-phase variations that were observed prior to <br /> 2001 Possible explanations for the observed patterns are discussed below <br /> 5.0 CONCLUSIONS <br /> 5.1 Hydraulic Gradient <br /> The hydraulic gradient returned to a more normal trend this quarter, and groundwater resumed <br /> its northeastward flow This confirms our conclusion in the Third Quarter 2001 Report that the <br /> southeast flow direction observed in September was a transient situation due to a lack of <br /> equilibration in the depth to groundwater in VM-4 <br /> 5.2 interpretation of Concentration Trends <br /> As discussed in section 4 2, hydrocarbon concentration trends in the monitor wells are not <br /> following patterns that are typical of most sites Rather than remaining relatively constant or <br /> declining slowly in all wells, concentrations have remained constant, declined, or increased in <br /> various wells When only four wells are involved, this is an unusual situation At least four <br /> possible interpretations should be considered <br /> 5.2.1 Hypothesis: Northeastward Migration of the Contaminant Plume <br /> One possible explanation for the increase in hydrocarbon concentrations in VM-2 is migration of <br /> the dissolved-phase gasoline plume from the former UST area in the western portion of the site <br /> This interpretation is moderately compatible with the hydraulic gradient data, although gradient <br /> contours have implied that flow has usually been more to the east than to the northeast <br /> • 4 II <br />
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