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ARCHIVED REPORTS_XR0006942
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0537485
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ARCHIVED REPORTS_XR0006942
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Last modified
7/27/2020 5:49:33 PM
Creation date
7/27/2020 3:53:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006942
RECORD_ID
PR0537485
PE
2957
FACILITY_ID
FA0021568
FACILITY_NAME
FORMER RAINWATER CAR WASH
STREET_NUMBER
420
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21931206
CURRENT_STATUS
01
SITE_LOCATION
420 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1 <br /> ' 05 September 2003 <br /> AGE-NC Project No 97-0333 <br /> ' Page 4 of 10 <br /> ' recorded during this time,AGE estimated that an average 1,745 gallons of water was discharged per <br /> day during this time <br /> 2 6 MASS-VOLUME REMOVAL CALCULATIONS <br /> ' Between 12 December 2002 and 27 March 203, an estimated 8 36 pounds of MTBE was extracted <br /> from ground water (Table 5), since the system was initiated on 21 January 2002, a total mass of <br /> 197 67 pounds of MTBE has been removed The December 2002 to March 2003 mass-volume <br /> ' calculations of MTBE-Impacted ground water extracted from the ground water pump-and-treat <br /> system are presented in Appendix B Plots of cumulative groundwater pump and treat mass removal <br /> trends and Influent ground water MTBE concentrations versus time are in Appendix C <br /> 3.0. GROUND WATER MONITORING AND SAMPLING <br /> I ' On 27 and 28 March 2003, ground water monitoring and sampling were performed at 47 ground <br /> water monitoring wells(MW-I through MW-13) Quarterly ground water monitoring procedures for <br /> !. the site were outlined in the AGE-prepared Work Plan Addendum, dated 03 April 2002,prepared by <br /> AGE and approved by San Joaquin County Environmental Health Department(SJCEHD)by letter <br /> ' dated 12 Apnl 2002 As-built monitoring well construction details are summarized in Table 6 <br /> 3 1 WELL MONITORING AND PURGE PROCEDURES <br /> On 27 March 2003, the depth to ground water was measured at each monitoring well from the top <br /> ' of each well casing to the nearest 0 01-foot utilizing a Sollnst water level meter The ground water <br /> elevation in each monitoring well was calculated by subtracting the measured depth to ground water <br /> from the surveyed casing elevation(Table 2) Ground water elevation and vertical gradient data for <br /> ' wells MW-11, MW-12 and MW-13 are depicted in cross section F-F' (Figure 3), ground water <br /> elevations were plotted In plan view for the Informal First Zone, Second Zone, Third Zone and <br /> Primary Aquifer Zone hydrogeologic flow units as defined in AGE's Cone Penetrometer Testing Site <br /> ' Investigation -Fourth Quarter 2000, dated 07 February 2001 (Figures 4 through 7) <br /> On 27 and 28 March 2003, approximately 6 to 13 gallons of ground water (a minimum of three <br /> casing-water volumes per well)were evacuated(purged)from wells MW-1 through MW-6 utilizing <br /> disposable polyethylene bailers Temperature,pH and conductivity were measured for stabilization <br /> at regular purge-volume intervals from each well using an Oakton water analyzer Field data and logs <br /> are provided in Appendix D The purged ground water was transferred to the ground water interim <br /> remediation system holding tank for treatment and disposal <br /> ' Advanced GeoEnvironmental,Inc <br />
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