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ARCHIVED REPORTS_XR0009581
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009581
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Last modified
5/4/2020 2:58:35 PM
Creation date
5/4/2020 2:38:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009581
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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3 <br /> Canepa's Car Wash <br /> 248 East Park Street,Stockton,California <br /> Second Quarter Groundwater Monitoring Report,April 2003 <br /> Page 3 of 5 <br /> • Table 1 —Groundwater Elevation Data (April 2003) <br /> Monitoring Well TOC Elevation Screened Depth to Groundwater Groundwater <br /> Interval(b s) Elevation <br /> MW-1 1278 45 - 65 2599 -1321 <br /> MW-2 12 18 45 - 65 2683 -1465 <br /> MW-3 1357 45 -65 2731 -1374 <br /> MW-4 1266 40-60 2564 -1298 <br /> MW-5 1306 40-60 2701 -1395 <br /> MW-6 13 53 40 -60 2719 -1366 <br /> MW-7 1286 40 -60 2633 -1347 <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 MTBE results for the groundwater samples collected from MW-2 <br /> and MW-5 by EPA Method 8020 (600 pg/L and 350 µg/L) were inconsistent with historical results The <br /> samples were therefore re-analyzed by EPA Method 8260B The results of the EPA Method 8260B <br /> analyses indicated that MTBE was not detected at or above the laboratory reported detection limit of 5 0 <br /> µg/L in the samples from MW-2 and MW-5 <br /> • Historical groundwater analytical data are presented in Table A, Attachment B A summary of the <br /> laboratory analytical results is presented in Table 2, on the next page Laboratory report sheets indicating <br /> analytical methods used, reporting limits, and the results of the analyses are included in Attachment D <br /> The concentration of benzene in monitor well MW-2 generally has 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 gg/L over time and was at <br /> California EPA's maximum contamination level (MCL) of 13 micrograms per liter (µg/L) for April 2003 <br /> (Figure 8, Attachment A) This reflects a downtrend from a peak of 21 4g/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 /> �ir 11 CONDOR <br />
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