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ARCHIVED REPORTS_XR0009579
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009579
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Last modified
5/4/2020 3:07:26 PM
Creation date
5/4/2020 2:37:55 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009579
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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f f <br /> Canepa's Car Wash <br /> 248 East Park Street,Stockton,California <br /> Third Quarter Groundwater Monitoring Report,July 2003 <br /> Page 3 of 5 <br /> Table I —Grounowater Elevation Data(July 2003) <br /> Momtormg Well TOC Elevation Screened Depth to Groundwater Groundwater <br /> Inter albs Eler ation <br /> MW-1 1278 45 -65 2633 -1355 <br /> MW-2 12 18 45 -65 2720 -1502 <br /> MW-3 1357 45 -65 2772 -1415 <br /> MW-4 1266 40-60 2600 -1334 <br /> MW-5 1306 40-60 2734 -14 28 <br /> MW-6 13 53 40 -60 2763 -1410 <br /> MW-7 1286 40-60 2667 -13 81 <br /> 'TOC Elevation Elevations are measured from the top of the well casing and are referenced to NGS benchmark HS0391 using NAVD 88 datum <br /> All wells were surveyed on October 5,2001 All measurements are in feet <br /> LABORATORY ANALYTICAL RESULTS <br /> The groundwater samples were analyzed by Excelchem Environmental Laboratories, Inc for total <br /> petroleum hydrocarbons quantified as gasoline (TPH-G) by EPA Method 8015m, for benzene, toluene, <br /> ethyl benzene, and total xylenes (BTEX) by EPA Method 8020, and for methyl tertiary-butyl ether <br /> (MTBE)by EPA Method 8020 The EPA Method 8020 analyses indicated that MTBE was detected in the <br /> groundwater sample collected from MW-2 at a concentration of 400 µg/L and that MTBE was not <br /> detected at or above an elevated detection limit of 500 Sg/L in the groundwater sample collected from <br /> MW-5 Because the result for the MW-2 sample was inconsistent with historical results and the detection <br /> • limit for the MW-5 sample was elevated, the samples were re-analyzed for MTBE by EPA Method <br /> 8260B The results of the EPA Method 8260B analyses indicated that MTBE was not detected in the <br /> samples from MW-2 and MW-5 at or above the laboratory reported detection limit of 5 0 µg/L <br /> Historical groundwater analytical data are presented in Table A, Attachment B A summary of the <br /> laboratory analytical results for the current monitoring event is presented in Table 2, on the next page <br /> Laboratory report sheets indicating analytical methods used, reporting limits, and the results of the <br /> analyses are included in Attachment D <br /> The concentration of benzene in monitor well MW-2 has generally had an inverse relationship with <br /> groundwater elevation (Figure 6, Attachment A) In contrast, benzene concentrations in MW-5 have <br /> generally increased as the groundwater elevation has increased(Figure 7,Attachment A) <br /> Concentrations of MTBE in monitor well MW-6 have ranged from < 0 5 to 23 lig/L historically and <br /> MTBE was not detected at or above the laboratory reported detection limit of 5 0 µg/L during the current <br /> monitoring event This reflects a downward trend from a peak of 21 µg/L in April 2002 Low <br /> concentrations of MTBE have been detected sporadically in groundwater samples collected from monitor <br /> wells MW-1, MW-3, MW-4, and MW-7 MTBE has historically not been detected at or above laboratory <br /> reported detection limits in MW-2 and MW-5, with the exception of a questionable laboratory analytical <br /> result in April 1997 for MW-2 <br /> • <br /> ILA CONDOR <br />
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