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ARCHIVED REPORTS_XR0009577
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009577
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Last modified
5/4/2020 3:11:11 PM
Creation date
5/4/2020 2:36:30 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009577
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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„ Canepa s Car Wash <br /> 248 East Park Street Stockton,California <br /> Second Quarter Groundwater Monitoring Report,May 2004 <br /> Page 3 of 5 <br /> iTable 1 —Groundwater Elevation Data(May 2004 <br /> Monitoring Well TOC Elevation Well Casing Depth to Groundwater Groundwater <br /> Screen Interval (feet) Elevation(feet-amsl) <br /> (feet-bgs) <br /> MW-1 12 78 45 - 65 2664 -13 86 <br /> MW-2 12 18 45 - 65 2749 -15 31 <br /> MW-3 1357 45 - 65 2806 -1449 <br /> MW-4 1266 40 - 60 2628 -1362 <br /> MW-5 1306 40 - 60 2770 -1464 <br /> MW-6 13 53 40 - 60 2794 -1441 <br /> MW-7 1286 40 - 60 2699 -14 13 <br /> 'TOC Elevation Elevations are measured from a mark on the top of the well casing and are referenced to NGS benchmark HS0391 using NAVD 88 <br /> datum <br /> bgs=below ground surface <br /> amsl=above mean sea level <br /> All wells were surveyed on October 5,2001 All measurements are to feet <br /> LABORATORY ANALYTICAL RESULTS <br /> The groundwater samples were analyzed by Excelchem Environmental Laboratones, 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-1 at a concentration of 41 µg/L, MW-2 at a concentration of <br /> 16,000 [ig/L, MW-3 at a concentration of 140 µg/L, and MW-5 at a concentration of 7,000 pg/L MTBE <br /> was not detected at or above a detection limit of 5 0 pg/L in the groundwater samples collected from <br /> MW-4, MW-6, and MW-7 Because the results for the MW-1, MW-2, MW-3, and MW-5 samples were <br /> inconsistent with historical results, the samples were reanalyzed for MTBE by EPA Method 8260B The <br /> results of the EPA Method 8260B analyses indicated that MTBE was not detected in the samples from <br /> MW-2, MW-3, and MW-5 at or above the laboratory reported detection limits of 5 0, 5 0, and 50 µg/L, <br /> respectively MTBE was detected at a concentration of 1 1 �tg/L in the groundwater sample collected <br /> from MW-1 <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 /> Low concentrations of MTBE have been detected sporadically in groundwater samples collected from <br /> monitor wells MW-1, MW-3, MW-4, and MW-7 MTBE has historically not been detected at or above <br /> laboratory reported detection limits in MW-2 and MW-5, with the exception of a questionable laboratory <br /> analytical result in April 1997 for MW-2 <br /> i <br /> S <br /> �� CONDOR <br />
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