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ARCHIVED REPORTS XR0003024
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0508132
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ARCHIVED REPORTS XR0003024
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Last modified
10/10/2018 9:07:00 AM
Creation date
10/9/2018 2:08:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS XR0003024
FileName_PostFix
XR0003024
RECORD_ID
PR0508132
PE
2957
FACILITY_ID
FA0007953
FACILITY_NAME
CHEVRON #9-5775
STREET_NUMBER
301
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04514002
CURRENT_STATUS
01
SITE_LOCATION
301 KETTLEMAN LN
P_DISTRICT
004
QC Status
Approved
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TMorelli
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EHD - Public
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S E C O R <br />Second Quarter 2004, QuarterlyProgress Report <br />July 13, 2004 g p <br />Page 1 <br />1.0 INTRODUCTION <br />SECOR International, Incorporated (SECOR), on behalf of Chevron Environmental Management <br />Company (Chevron), presents second quarter 2004 (2Q04) groundwater monitoring and sampling results, <br />and operational data for the groundwater extraction and treatment (GWET) system at 301 West <br />Kettleman Lane, Lodi, California (Figure 1). This report covers the period from March 10, 2004 through <br />June 14, 2004, and was prepared in accordance with Cleanup and Abatement Order (CAO) No. 5-00- <br />704, dated April 20, 2000 (Appendix A). <br />2.0 GROUNDWATER MONITORING AND SAMPLING <br />On April 30, 2004, Gettler-Ryan Incorporated (G -R), conducted 2Q04 groundwater monitoring and <br />sampling. Certified laboratory analytical reports and chain -of -custody documentation and sampling field <br />data sheets, are included in Appendices B and C, respectively. A brief summary of results is presented <br />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 />x from 57.74 to 63.69 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 />Insufficient monitoring wells in the C -zone prevent evaluation of the potential for groundwater flow in this <br />zone. <br />2.2 Sample Analytical Results <br />During the 2Q04, 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 isoconcentration map for MtBE is presented as <br />Figure 4. <br />lAChevron1957751Periodic Monitoring\Q P R1200412nd Quarter -2004 QPR.doc <br />Maximum Constituent Concentrations (µg11) <br />Zone <br />TPHg <br />Benzene <br />Toluene <br />Ethyl- <br />benzene <br />Xylenes <br />MtBE <br />TBA <br />EtBE <br />TAME <br />A- <br />zone <br />240 <br /><1 <br />1 <br /><1 <br /><1 <br />3,200 <br /><10 <br />180 <br />43 <br />B- <br /><50 <br />< <br />< n <br /><5 <br /><0.5 <br /><0.5 <br />C- <br />zone <br /><50 <br /><0.5 <br />0.8 <br /><0.5 <br /><0.5 <br /><0.5 <br /><5 <br /><0.5 <br /><0.5 <br />Explanations: <br />µgll = Micrograms per liter <br />< Indicates the constituent was not present at or above the method detection limit shown <br />lAChevron1957751Periodic Monitoring\Q P R1200412nd Quarter -2004 QPR.doc <br />
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