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ARCHIVED REPORTS_XR0012101
Environmental Health - Public
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ARCHIVED REPORTS_XR0012101
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Last modified
3/16/2020 5:49:27 PM
Creation date
3/16/2020 2:32:48 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012101
RECORD_ID
PR0541875
PE
2960
FACILITY_ID
FA0024017
FACILITY_NAME
CHEVRON SITE 306415
STREET_NUMBER
437
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
1392417
CURRENT_STATUS
01
SITE_LOCATION
437 E MINER AVE
P_LOCATION
01
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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' ENSR AEGON <br /> suggest that the Unocal plume is a relative) minor source of groundwater impacts at the Vintage Car Wash <br /> gg p Y 9 P g <br /> site. This conclusion is based on the following observations: <br /> 1. Groundwater concentrations in Zone A are below detection limits upgradient of the Vintage Car Wash <br /> site (i.e., at well MW-7), whereas Zone A groundwater concentrations at the Vintage Car Wash site <br /> (i.e., at well VX-1) have been comparable to source area concentrations at the Unocal site, indicating <br /> that a source area exists at the Vintage Car Wash site. <br /> 2. Groundwater concentrations in Zone B on the Vintage Car Wash site (i.e., wells MW-1, MW-2, and <br /> MW-3) are significantly higher than those detected at the most downgradient Unocal wells screened <br /> in Zone B (i.e., monitoring wells U-20 and U-21). <br /> 3. Groundwater concentrations of TPH, benzene and MTBE detected downgradient of the Vintage Car <br /> Wash site in Zone C are higher than those detected upgradient of the Vintage Car Wash site. <br /> Based on these observations, it is concluded that Unocal station #0187 does not contribute to groundwater <br /> contamination in Zone A at the Vintage Car Wash site, but may be a minor contributor to Zone B <br /> contamination at the Vintage Car Wash site. It is not clear whether the downgradient extent of impacts at the <br /> Vintage Car Wash site has been delineated. Dissolved-phase petroleum hydrocarbon concentrations in <br /> Vintage Car Wash site monitoring wells MW-12 and MW-13 are below MCLs. However, additional delineation <br /> by Vintage Car Wash may be necessary near the corner of Grant Street and Lindsay Avenue. <br /> ' The presence of a downward hydraulic gradient and the pattern of subsurface impacts are suggestive of a <br /> potential sinking plume at the site,caused by a downward component to the hydraulic gradient. While <br /> concentrations are declining downgradient of the site, the centerline of the plume may be becoming <br /> progressively deeper. The higher benzene concentrations detected in downgradient Zone C monitoring well <br /> U-21 relative to those detected in well U-12 are consistent with a sinking plume. TPHg concentrations at these <br /> two wells are not consistent with a sinking plume; however, due to the predominance of relatively hydrophobic <br /> aliphatic hydrocarbons in TPHg, its migration is more strongly affected by sorption than benzene, which may <br /> account for the difference in trends, as TPHg concentrations do not extend as far downgradient. <br /> 3.4 Groundwater concentration trends <br /> Groundwater concentration data are summarized in Table 3-3. Since the ozone sparging system became <br /> operational in December 2000, concentrations in several monitoring wells have declined. However, <br /> concentrations were declining prior to installation of the ozone sparging system in the majority of these wells. <br /> In addition, concentrations have been declining at monitoring well U-1, which is upgradient and beyond the <br /> area of influence of the ozone sparge system, suggesting that the ozone sparge system may not be wholly <br /> responsible for the decline in concentrations observed in wells near the system. A summary of concentration <br /> trends in selected wells is presented in Table 3-4. Trends were determined using a Mann-Kendall statistical <br /> analysis. Individual analyses spreadsheets and a description of the Mann-Kendall methodology are presented <br /> in Appendix A. Appendix A also includes graphical depictions of concentrations data referenced to the <br /> installation of the ozone sparging system. These graphs do not show an increasing rate of contaminant <br /> degradation following installation or expansion of the ozone sparging system. <br /> 3.5 Biodegradation parameters <br /> Dissolved oxygen data for wells in the immediate vicinity of the sparge wells(i.e., U-3, U-10, NP-1-22/65/111 <br /> and NP-2-221601116)do not show an increasing trend(see Table 3-5). These data suggest that the ozone <br /> sparging system may not be effective at treating impacts on site. However, this could be related to operational <br /> considerations(see Sections 3.4 and 5.3). <br /> r <br /> J:1Rem_Eng\Project Files1P60(6000- <br /> 6999)18940-UNOCAL Porttolio CEosure\6940- 3-3 January 2006 <br /> UNOCAL Portfolio Closure\She 0187-Stockton <br /> East MinoACSM ReporflCSM Report_Finat.doc <br />
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