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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0503634
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/7/2019 4:40:56 PM
Creation date
5/7/2019 4:15:53 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0503634
PE
2950
FACILITY_ID
FA0005914
FACILITY_NAME
VICTOR ROAD SHELL
STREET_NUMBER
880
STREET_NAME
VICTOR
STREET_TYPE
RD
City
LODI
Zip
95240
APN
04905032
CURRENT_STATUS
02
SITE_LOCATION
880 VICTOR RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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Karen Petryna L 1'0 <br /> Shell Oil Products <br /> 880 E. Victor Rd., Stockton, CA <br /> Page 2 of 5 <br /> EHD comments as follows: <br /> The plume of impacted groundwater, commonly first encountered in silty sand to <br /> poorly sorted sand between approximately 50 feet and 60 to 63 feet below <br /> surface grade (bsg) is reasonably delineated toward the northeast by MW-6, <br /> toward north by MW-5, toward the west northwest and southwest by MW-8 and <br /> MW-9, and toward the south by MW-10. The analytical data from groundwater <br /> samples from these wells does appear to indicate plume stability and minimal <br /> lateral migration in the 45- to 60-foot depth interval (locally to 63 feet bsg), except <br /> for the monitoring gap toward the east and beyond the impacted MW-7 toward <br /> the southeast. <br /> Boring logs from wells near CPT locations on this site show that the CPT logs <br /> can underestimate grain size, causing fine sand to be classified as silt or stiff <br /> fine-grained soil of uncertain composition, an observation made on other sites in <br /> San Joaquin County. EHD believes that MW-11 soil composition data indicates <br /> that the interval between 65 and 90 feet bsg may, and probably does, contain <br /> several thin permeable coarse-grained units masked in the CPT logs by <br /> interbedded fine-grained units. EHD is concerned that there may be unidentified, <br /> more highly permeable units underlying the monitored interval that can facilitate <br /> lateral migration of contaminants. <br /> A gravelly sand unit, identified and sampled in CPT-2 between 61 and 65 feet <br /> bsg, occurs just below the monitored interval, and is impacted by MTBE and <br /> TBA. The orientation of this probable channel bed deposit is not well defined at <br /> this time. This interval, being gravelly, may be a unit of much higher hydraulic <br /> conductivity and may be acting as a significant linear or curvilinear migration <br /> pathway that is currently not characterized or monitored. <br /> Cambria has concluded that the plume of impacted groundwater is not migrating <br /> away from the site; EHD agrees that there is no direct indication from the <br /> monitored interval that the plume is actively migrating, except possibly toward the <br /> southeast as indicated by MW-7. EHD's uncertainty with the 'no migration' <br /> characterization lies in the potential for unencountered and unrecognized <br /> coarser-grained channel deposits, such as the gravelly sand described above, <br /> occurring in the sand-rich subsurface of this site and acting as undetected <br /> contaminant migration pathways. <br /> Cambria concludes that MWA 1 demonstrates the vertical extent of impacted <br /> groundwater. EHD is not certain of this as review of historical groundwater <br /> elevation maps indicates that there is a fairly persistent trough or depression of <br /> the groundwater surface that trends from the UST area toward the southeast, <br /> putting the point selected for MW-11 in an up-gradient position from the inferred <br /> source area. The validity of MW-11, located approximately 30 feet from the <br />
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