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ARCHIVED REPORTS XR0008945
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0503634
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ARCHIVED REPORTS XR0008945
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Last modified
5/7/2019 4:56:18 PM
Creation date
5/7/2019 4:28:51 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008945
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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EHD - Public
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AMBRIA <br /> 62,000 ppb, 37,000 ppb, and 34,000 ppb, respectively The final groundwater samples collected <br /> from MW-4 on September 12 contained 31,000 ppb MTBE and 36,000 ppb TBA Certified <br /> analytical reports are provided in Appendix A <br /> September 2003 Drawdown Analyses. Water level fluctuations in wells MW-3 and MW-7 and <br /> piezometers P-1 and P-2 were small and correlated with each other The fluctuations in these <br /> wells and piezometers also correlated with barometric pressure fluctuations, which is common <br /> for unconfined aquifers A graph of barometric pressure reading versus time is presented in <br /> Appendix B Cambria observed a maximum drawdown of 0 23 feet in piezometer P-1, which is <br /> located approximately 12 feet from the pumping well MW-4 The water level in the pumping <br /> well MW-4 was drawn down approximately 6 5 feet, to near its total depth Based on this data, it <br /> does not appear that pumping from well MW-4 affected water levels at the observation points <br /> Instead, the data suggest that water level changes observed durmg_pumpng are_mostly attributed <br /> to changes_ip barometric pressure The lack of significant effect on groundwater levels in wells <br /> --,and piezometers near MW-4 from pumping in that well is a good indication that it would be very <br /> difficult to establish hydraulic control of groundwater beneath this site <br /> Of special interest is a discrete water level drawdown and subsequent recovery from the 3,000-to <br /> 4,000-minute interval This discrete fluctuation was observed at all the observation points, but <br /> does not correspond with a change in barometric pressure, and pump operation was consistent <br /> during this time interval Therefore, it does not appear—to be-an_effect_a umpmg from well <br /> MW-4 This fluctuation may have been i natural background fluctuation o mechanically <br /> induced by another source ` ;^f• � <br /> Because drawdown in the observation points was minimal, Cambria was limited to analyzing the <br /> recovery data from pumping well MW-4 Cambria analyzed the recovery data using AquiferTest <br /> for Wmdows® version 3 01 software from Waterloo Hydrogeologic, Inc Appendix B presents <br /> the pump test analysis reports Recovery data from the constant rate test were analyzed by the <br /> Theis Recovery method to estimate hydraulic conductivity and transmissivity Cambria <br /> estimated the hydraulic conductivity of this unconfined aquifer tobe 5 3�meters/day and the <br /> transmissivity to be 16 6 square meters per day The hydraulic conductivity yielded from the <br /> recovery data analysis is consistent with fine-grained sand (Todd, 1980) which correlates well <br /> with the soil types logged for this well (sand, silty sand, and sandy silt) These results are also <br /> consistent with the results of the 2002 aquifer pump test <br /> October 2003 GWE Event. Cambria conducted the second batch GWE event on well MW-4 <br /> from October 27 through 31, 2003 The GWE equipment and procedures for this event were the <br /> 0955 6 <br />
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