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WORK PLANS FILE 2
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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4491
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3500 - Local Oversight Program
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PR0544625
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WORK PLANS FILE 2
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Last modified
7/3/2019 7:59:49 PM
Creation date
7/3/2019 4:28:33 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0544625
PE
3528
FACILITY_ID
FA0003113
FACILITY_NAME
ZAPIEN MARKET
STREET_NUMBER
4491
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25504003
CURRENT_STATUS
02
SITE_LOCATION
4491 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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Y _ <br /> CL EARATER <br /> G R O U 'P, P N C. <br /> ' EnDirnn mCntal SE rDiCCS <br /> Initial Stem Operation and Monitoring. <br /> On September 28, 1998, the SVE system was started for initial source testing. Clearwater and <br /> SJVUAPCD personnel were present. <br /> The air sparge system delivered air to the- two sparge wells for fifteen minute intervals <br /> approximately every four hours at a pressure of 3psi. Soil gas was extracted from all,seven wells <br /> noted above (Figures 2 and 3). The manual air dilution valve to the catalytic oxidizer was open <br /> approximately 10%. The influent air stream entered the catalytic oxidizer at a temperature of 675°F <br /> and at a rate of 152 scfm. The system is configured.such that soil gas will not be'introduced to the <br /> catalyst until the process air stream has attained a minimum temperature of 650°F. Process air <br /> exited the catalytic oxidizer at a temperature of''l,035°F (the system automatically shouts down if <br /> the exhaust temperature exceeds 1,150°F). <br /> Air samples were collected from both the "influent" and "effluent" sample ports using Tedlar bags <br /> (Figure 3). The samples were labeled, documented on a chain-of-custody form, and stored in a <br /> dark container for transport to the project laboratory. The samples were analyzed by Entech <br /> Analytical Labs, Inc., a DHS-certified laboratory located in Sunnyvale, California, for <br /> concentrations of total petroleum hydrocarbons;as gasoline (TPHg), and benzene, toluene, <br /> ethylbenzene, and xylene isomers (BTEX) by EPA.Methods 8015 (modified) and 8020. <br /> Initial System Monitoring Results <br /> The results of initial monitoring indicate that electric catalytic oxidizer achieved a hydrocarbon <br /> destruction efficiency of>97%. TPHg concentrations in the influent and effluent air samples were <br /> and 370 mg/m3 and <10 mg/m3, respectively. :Based on these data and flowrates, the system <br /> recovered TPHg from the subsurface at a rate of 5 lbs/day, and the TPHg emission rate_following <br /> treatment was <0.15 lbs/day. Thus, system operation complies with the conditions in the <br /> Authority-to-Construct permit. <br /> System Status <br /> Clearwater intends to restart the system for and extended period of remedial operation. The system <br /> is <br /> will be operated in essentially the same-manner;;as that during start-up.testing,.except.for..minor <br /> e <br /> ongoing adjustment to enhance contaminant rcovery rates and maintain appropriate system <br /> operational parameters over time. The system•will be operated such that it complies with all <br /> Mr. Craig Mitchell, S]VUAPCD 2 October 1, 1998 <br />
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