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ARCHIVED REPORTS XR0000769
Environmental Health - Public
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ARCHIVED REPORTS XR0000769
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Last modified
2/15/2019 4:51:26 PM
Creation date
2/15/2019 2:06:28 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000769
RECORD_ID
PR0544155
PE
3526
FACILITY_ID
FA0000185
FACILITY_NAME
CITY GAS & LIQUOR
STREET_NUMBER
16470
STREET_NAME
CAMBRIDGE
STREET_TYPE
ST
City
LATHROP
Zip
95330
APN
19643032
CURRENT_STATUS
02
SITE_LOCATION
16470 CAMBRIDGE ST
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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S E C O R <br /> • Fourth Quarter 2003, Quarterly Progress Report <br /> January 14, 2004 <br />' Page 1 <br /> 1 0 INTRODUCTION <br />' SECOR International, Incorporated (SECOR), on behalf of Chevron Environmental Management <br /> Company (Chevron), presents fourth quarter 2003 (4Q03) groundwater monitoring and sampling results, <br /> and operational data for the groundwater extraction and treatment system (GWET) at 301 West <br /> Kettleman Lane, Lodi, California (Figure 1) This report covers the period from September 17 through <br /> December 11, 2003, and was prepared in accordance with Cleanup and Abatement Order (CAO) No 5- <br /> 00-704, dated April 20, 2000 (Appendix A) <br /> 2.0 GROUNDWATER MONITORING AND SAMPLING <br />' On October 27 and 28, 2003, Gettler-Ryan incorporated (G-R), conducted 4003 groundwater monitoring <br /> and sampling Certified laboratory analytical reports and chain-of-custody documentation and sampling <br /> field data sheets, are included in Appendices B and C, respectively A brief summary of results is <br />' presented below <br /> 2 1 Monitoring Well Gauge Data <br />' Monitoring well gauge data indicates the approximate depth to groundwater in A, B, and C-zones ranges <br /> from 60 61 to 62 11 feet below ground surface (bgs) Groundwater gauging data is presented in Table 1 <br />' The potential for groundwater in the A-zone near the site appears to be radially inward toward extraction <br /> well EX-3(Figure 2) The potential for groundwater flow in the B-zone appears to be variable (Figure 3) <br /> 2 2 Sample Analytical Results <br /> During the 4003, groundwater samples were analyzed for total petroleum hydrocarbons as gasoline <br /> (TPHg), benzene, toluene, ethyl-benzene, and total xylenes (BTEX), methyl tertiary butyl ether (MtBE), <br />' tertiary butyl alcohol (TBA), di-isopropyl ether (DIPE), ethyl tertiary butyl ether (EtBE), tertiary amyl methyl <br /> ether (TAME), ethanol, methanol, ethylene di-bromide (EDB), and 1,2-dichloroethane (1,2-DCA) Sample <br /> analytical results are summarized in Table 2 Maximum concentrations of detected constituents for A, B, <br />' and C-zones are presented in the table below An A-zone is oco ncent ration map for MtBE is presented as <br /> Figure 4 <br /> Maximum Constituent Concentrations(fLg/l) <br /> Zone <br /> TPHg Benzene Toluene Ethyl-benzene Xylenes MtBE TBA EtBE TAME <br />' A 1,100 <0 5 2 <0 5 3 1,100 26 100 14 <br /> zone <br />' B <br /> zone <50 <0 5 <0 5 <0 5 <0 5 <0 5 <5 <0 5 <0 5 <br /> C <50 j <0 5 <0 5 <0 5 <0 5 <0 5 <5 <0 5 <0 5 <br /> zone <br />' Exolanatlons- <br /> µgA R Micrograms per liter <br /> <Indicates the constituent was not present at or above the method detection limit shown <br />' I IChevron1957751Penodic Monitoring\Q P R1200314th Quarter-2003 QPR doc <br />
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