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ARCHIVED REPORTS_XR0009616
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009616
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Last modified
5/4/2020 3:19:01 PM
Creation date
5/4/2020 2:46:28 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009616
RECORD_ID
PR0542235
PE
2960
FACILITY_ID
FA0024262
FACILITY_NAME
CANEPA CAR WASH
STREET_NUMBER
248
Direction
E
STREET_NAME
PARK
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906035
CURRENT_STATUS
01
SITE_LOCATION
248 E PARK ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Quarterly Monitoring Report,April 2000 <br /> Canepa s Car Wash(Park Street) <br /> October 20,2000 <br /> Page 4 <br /> TABLE 2 <br /> LABORATORY ANALYTICAL RESULTS (April 18 and 19,2000) <br /> Other <br /> B T E X MTBE Oxygenates/ TPH-G <br /> Additives* <br /> MONITOR Detection 03 03 03 06 10 1 0- 10 005 <br /> WELL/ DATE Limits—* µg/L µg/1, ltg/L Itg/L µg/L µg/L mg/L <br /> SAMPLE Sample I D <br /> MW-1 7/13/00 2038-MW1-7/13/00 ND ND ND ND ND ND ND <br /> MW-2 7/13/00 2038-MW2-7113/00 90 52 120 160 ND(20) ND(20-200) 69 <br />' MW-3 7/12/00 2038-MW3-7112/00 ND ND 03 ND 32 ND ND <br /> MW-4 7/13/00 2038-MW4-7/13/00 ND ND ND ND 14 ND ND <br />' MW-5 7/13/00 2038-MW5-7/13100 6,700 6,100 1,000 2,800 ND(20) ND(20-200) 24 <br /> MW-6 7/12/00 2038-MW6-7/I2/00 ND ND ND ND 12 ND ND <br /> MW-7 7/13/00 1 2038-MW7-7/13/00 ND 08 ND ND ND ND ND <br /> Unit Conversions Analytical <br /> µg/L parts per billion(ppb) B,T,E X=benzene,toluene,ethyl benzene,and total xylenes <br /> mg/L parts per million(ppm) TPH-G=total petroleum hydrocarbons,quantified as gasoline <br /> MTBE=Methyl tertiary Butyl Ether <br /> Other Oxygenates/Additives=ethanol,Di-isopropyl ether(DIPE),Ethyl tertiary-Butyl Ether <br /> (ETBE),tertiary-amyl Methyl Ether(TAME) and tertiary-Butanol <br /> *=See laboratory reports in Appendix C for actual laboratory reporting limits <br /> ND—not detected at or above the laboratory reporting limit <br /> ND(X)=not detected at or above a raised laboratory reporting limit See laboratory report sheets <br /> for reporting limits <br /> 5. DISCUSSION OF RESULTS <br /> 51 DISCUSSION OF GROUNDWATER ELEVATIONS <br /> Since September 1994, the groundwater elevation at the site has generally increased from approximately 35 feet <br /> bmsl to approximately l 1 feet bmsl A hydrograph of monitor wells MW-1 through MW-7 (Figure 6, Appendix <br /> A) tllustrates the fluctuation of the groundwater table The average depth to groundwater measured in the <br /> monitor wells on July 12, 2000 was approximately 22 5 feet below the monitor well measuring points, which is <br /> approximately 17 to 23 feet above the top of all well screens The groundwater elevation ranged from 10 48 to <br /> 12 15 feet bmsl The groundwater elevation contour map (Figure 2, Appendix A) indicates that the groundwater <br /> Igradient at the site is generally towards the northeast This is consistent with previous monitoring results <br /> 5 2 DISCUSSION OF ANALYTICAL RESULTS <br /> The laboratory analytical results for the July 2000 groundwater monitoring event are generally consistent with <br /> • the laboratory analytical results from the April 2000 groundwater monitoring event The concentrations of <br />' benzene and ethyl benzene detected in the groundwater sample collected from MW-5 represent historical highs <br /> N 410� <br /> L� CONDOR <br />
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