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ARCHIVED REPORTS_XR0007289
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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WILSON
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3500 - Local Oversight Program
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PR0545106
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ARCHIVED REPORTS_XR0007289
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Last modified
12/19/2019 4:22:57 PM
Creation date
12/19/2019 4:05:23 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007289
RECORD_ID
PR0545106
PE
3529
FACILITY_ID
FA0003694
FACILITY_NAME
RIVER CITY PETROLEUM CARDLOCK
STREET_NUMBER
2211
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
11707050
CURRENT_STATUS
02
SITE_LOCATION
2211 N WILSON WAY
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\wng
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EHD - Public
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F ' <br /> fluctuating with the rise and fall of the groundwater elevation High groundwater elevations yield the <br /> • highest concentrations The groundwater gradient was to the west for this event, which is a complete <br /> reversal of the historic trends Before this current event all other events have produced a hydraulic <br /> gradient to the east or north If the present condition continues, this may explain the plume movement <br /> to the west under the building It also could be concluded that when the groundwater elevation drops, <br /> the gradient changes from the east to the west <br /> RECOMMENDATIONS <br /> It is recommended by the author that a deep monitoring well be installed in the dispenser area near <br /> monitoring well MW#1 This monitoring well should be installed to a depth of 100 to125 feet The <br /> author also recommends that two monitoring wells be installed west of the newly established MW#9S <br /> & 9D to determine the extent of both TPHg and 1,2-DCA contamination under the building One well <br /> would monitor first water to a depth of 60 feet The other well would monitor groundwater at the depth <br /> of 100 feet or more <br /> WORK IN PROGRESS <br /> The only work in progress is quarterly monitoring of the existing monitoring wells The soil stockpile <br /> on the westside of the site has been classified as non-detect for all analytes Authorization for removal <br /> has been requested of EHD <br /> REPORT ON SOIL BORE SAMPLE ANALYSIS AND CONSTRUCTION OF MW#9S&MW9D <br /> Sampled 08/15/2002 <br /> PROCEDURE <br /> The soil bore was drilled with a track mounted low profile drill with an 8" hollow stem auger The low <br /> profile drill was required due to the 16'clearance in the budding Soil samples were extracted with a split <br /> spoon sampler at five foot intervals from a depth of 20' to100' Soil was retained in a brass tube with <br /> Teflon sheet cover and a plastic cap Soil samples were transported under chain of custody to Sherwood <br /> Labs for analysis Sherwood analyzed the samples for BTEX and TPHg by EPA Method SW8020F <br /> Sherwood transported,under chain of custody,a portion of these soil samples to Entech Labs for analysis <br /> by EPA Method 8260FA for oxygenates and lead(see attached Soil Sample Analysis Recap sheet) <br /> Groundwater samples were not extracted during this soil bore <br /> FINDINGS FROM SOIL BORE SAMPLE ANALYSIS <br /> Samples from a depth of 60', 65', and 70' were the only samples that contained BTEX or TPHg above <br /> detection levels from this soil bore None of the soil samples analyzed contain Benzene above the <br /> detection levels and none of the soil samples contained 1,2-DCA above detection levels The soil bore <br /> was terminated at 100' of depth with some soil caving experienced at that depth <br /> MONITORING WELL CONSTRUCTION FOR MW#9S AND MW#9D <br /> Monitoring well MW#9D was constructed with a 1" PVC casing to a depth of 95', with the bottom 5' <br /> screened MW#9S was constructed with a 2" PVC casing to a depth of 60', with a 20' screened section <br /> 3 <br />
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