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ARCHIVED REPORTS XR0000767
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3500 - Local Oversight Program
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PR0544155
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ARCHIVED REPORTS XR0000767
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Last modified
2/15/2019 3:50:06 PM
Creation date
2/15/2019 2:02:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000767
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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EHD - Public
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' S E C 0 R <br /> Second Quarter 2004, Quarterly Progress Report <br /> July 13, 2004 <br /> ' Page 2 <br /> 3 0 EVALUATION OF GROUNDWATER EXTRACTION <br /> ' GWET and Sod Vapor Extraction (SVE) systems were activated on July 3, 2000 Certified laboratory <br /> analytical reports and chain-of-custody documentation and remedial system operation and maintenance <br /> ' field data sheets are included in Appendices D and E, respectively On August 20, 2003, SVE was <br /> discontinued as approved by the Regional Water Quality Control Board (RWQCB) in their letter dated <br /> August 18, 2003 A copy of this letter is included in Appendix F A brief description and performance <br /> evaluation of the GWET remedial system during 2Q04 are presented below <br /> s 31 Groundwater Extraction System <br /> i <br /> ' The GWET system includes groundwater extraction wells EX-1, EX-2 and EX-3 (Figure 5) These wells <br /> are equipped with submersible pumps connected through mechanical piping to a series of granular <br /> activated carbon (GAC) vessels prior to an industrial sewer discharge point Chevron discharges treated <br /> groundwater at the subject site under City of Lodi (City)wastewater discharge permit#328 <br /> To assess effectiveness of the GWET system, process samples were collected monthly during this <br /> ' reporting period Sample locations include a influent port (INFL) prior to the first GAC vessel, between <br /> the first and second GAC vessels (MID-1), between the second and third GAC vessels (MID-2), and <br /> before discharge (EFFL) to the industrial sewer During these sampling events, INFL, MID-1, MID-2 and <br /> EFFL samples were analyzed for TPHg, BTEX, MtBE, TBA, DIPE, EtBE, TAME, ethanol, methanol, EDB <br /> and 1,2-DCA Maximum concentrations of detected constituents are presented below Current and <br /> historical analytical information is presented as Table 3 <br /> ' Maximum Constituent Concentrations(pgh) <br /> Zone <br /> ' MtBE TBA EtBE TAME Ethanol Methanol <br /> INFL 9 <10 <2 <2 <100 <400 <br /> ' MID-1 <2 <10 <2 <2 <100 <400 <br /> MID-2 <2 <10 <2 <2 <100 <400 <br /> EFFL <2 <10 <2 <2 <100 <400 <br /> Exglanatio_ns <br /> <Indicates the constituent was not present at or above the method detection limit shown <br /> tBetween December 12, 2003 and March 09, 2004, the GWET system discharged a total of 765,216 <br /> gallons of treated groundwater (Table 4) As of March 09, 2004, the GWET system had treated a total of <br /> 9,428,621 gallons Calculated discharge rates during the 2Q04 monitoring period ranged from 5 58 to <br /> ' 6 77 gallons per minute (gpm) <br /> uring ZUU4, trie system extracted an estimated U 2 pounds of I PHg I o date, the system <br /> ah s extr`acT6d approximately 9 7 pounds of TPHg, 0 2 pound of benzene, and 85 0 pounds of MtBE Plots of GWET <br /> system mass removal trends and influent groundwater TPHg, benzene, and MtBE concentrations versus <br /> time are shown on Figure 6 and 7, respectively <br /> ' 11Chevron1957751Penodic Monitonng\Q P R=0412nd Quarter-2004 QPR doc <br />
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