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ARCHIVED REPORTS_XR0009582
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009582
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Last modified
5/4/2020 3:09:24 PM
Creation date
5/4/2020 2:38:41 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009582
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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A .! <br /> Canepa's Car Wash <br /> 248 East Park Street,Stockton,California <br /> First Quarter Groundwater Monitoring Report,January 2003 <br /> Page 3 of 5 <br /> iTable 1 —Groundwater Elevation Data (January 2003) <br /> Monitoring Well TOC Elevation Screened Depth to Groundwater Groundwater <br /> Interval(b s) Elevation <br /> MW-1 1278 45 -65 2617 -1339 <br /> MW-2 12 18 45 - 65 2708 -1490 <br /> MW-3 13 57 45 - 65 2756 -13 99 <br /> MW-4 1266 40- 60 25 80 -13 14 <br /> MW-5 1306 40 -60 2731 -1425 <br /> MW-6 1353 40 - 60 2751 -1398 <br /> MW-7 12 86 40 - 60 2656 -1370 <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 result for the groundwater sample collected from MW-2 by <br /> EPA Method 8020 (330 gg/L) was inconsistent with histoncal results The sample was therefore re- <br /> analyzed by EPA Method 8260B The results of the EPA Method 8260B analysis indicated that MTBE <br /> as not detected at or above the laboratory reported detection limit of 0 5 gg/L in the sample from MW- <br /> 2 Histoncal 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 to MW-5 have <br /> generally increased as the groundwater elevation has increased(Figure 7, Attachment A) <br /> Concentrations of MTBE 1n monitor well MW-6 have ranged from c 0 5 to 21 gg/L over time, with a <br /> general trend of increasing concentration since April 2001 (Figure 8, Attachment A) Low concentrations <br /> of MTBE have been detected sporadically to groundwater samples collected from monitor wells MW-1, <br /> MW-3, MW-4, and MW-7 MTBE has htstoncally not been detected at or above laboratory reported <br /> detection limits In MW-2 and MW-5, with the exception of a questionable laboratory analytical result to <br /> April 1997 for MW-2 <br /> i <br /> IL 4) CONDOR <br />
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