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ARCHIVED REPORTS_XR0006733
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0543479
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ARCHIVED REPORTS_XR0006733
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Last modified
5/5/2020 10:39:16 AM
Creation date
5/5/2020 9:49:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006733
RECORD_ID
PR0543479
PE
2960
FACILITY_ID
FA0024679
FACILITY_NAME
CANEPA'S CAR WASH
STREET_NUMBER
6230
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95204
APN
081360030
CURRENT_STATUS
01
SITE_LOCATION
6230 PACIFIC AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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f Canepa's Car Wash <br /> 6230 Pacific Avenue, Stockton, California April 29, 1994 <br /> Phase 11 Site Characterization Page: S <br /> introduced. into the Bader as a final stage of cleaning This water was then gently <br /> poured into sample vials to be used as bailer blanks These bailer blanks were not <br /> tested unless their corresponding samples contained contaminants <br /> EImmediately prior to sampling, water levels and well depth measurements were taken <br /> to all wells at the site Each was evacuated using a stainless steel bladder pump which <br /> does not introduce air into the water column The pH, temperature and electrical <br /> conductivity of the water were monitored as the well was evacuated These <br /> parameters are noted on the Field bogs (Appendix G) Instruments calibrated to <br /> known standards were used to monitor these parameters At least five (5) well <br /> volumes were evacuated from each well, and more, if necessary, until the above <br /> parameters were stabilized <br /> The samples were carefiAly poured from a Teflon bailer into half gallon plastic <br /> containers and clean glass vials with Teflon-lined screw caps provided by the <br /> laboratory Care was taken to ensure that no air -,pane existed in the vials by inverting <br /> to check for bubbles and re-sampling if necessary The samples were analyzed or <br /> extracted within 14 days according to their EPA methods Water samples collected for <br /> analysis were analyzed by EPA method 602 for BTX&E compounds, method 3550 for <br /> gasoline range hydrocarbons and on the first four wells, method 601 for 1,1,1, <br /> tnchloroe&.ane, because this compound was found in the soil spoils pile test sequence <br /> Following the initial sampling,PHS/EM will evaluate the need to continue the volatile <br /> organic compound analysts. All analyses were conducted by Geo-Monitor, Inc, a <br /> State certified laboratory <br /> 4.0 Soil Conditions <br /> E <br /> The Soil Survey completed in 1988 by the U S Department of Agriculture, Soil Conservation <br /> E Service, generally classify the sod types as being Jacktone, Hollenbeck or Stockton types <br /> Generally, these sods are somewhat poorly to moderately well-drained, fine texture soils that <br /> are moderately deep to deep, down to a cemented hardpan <br /> Analysis of soil samples show boring B-1 to be contaminated from 35 feet down to the water <br /> table at approximately 55 feet below ground level MW-1 is only 8 feet from bonng B-1 and <br /> was not laboratory sampled Two tntervals of le-m.than 100 ppm were detected in MW-2 with <br /> a portable PID MW-3 was ND ("none-detected") for BTEX, Gasoline and TCE, but had <br /> traces of chloroform in the samples at 50 and 55 feet(Table 5) MW-3, 4, 5 and 8 were ND <br /> Both MW-6&7 had contamination at 50 and 55 feet,the capillary fringe and water table at the <br /> time of drdhng The soil corttaiwanon plan map shows depths m feet below ground level to <br /> the top of the plume(Figure 10) <br /> E <br />
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