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ARCHIVED REPORTS_XR0008340
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0541936
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ARCHIVED REPORTS_XR0008340
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Entry Properties
Last modified
5/18/2020 11:48:22 AM
Creation date
5/18/2020 11:14:46 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008340
RECORD_ID
PR0541936
PE
2957
FACILITY_ID
FA0006149
FACILITY_NAME
RANCH MARKET
STREET_NUMBER
23569
Direction
S
STREET_NAME
SANTA FE
STREET_TYPE
RD
City
RIVERBANK
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
23569 S SANTA FE RD
QC Status
Approved
Scanner
LSauers
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EHD - Public
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S EC ® R <br /> • Mr Michael Infurna—SJCEHD <br /> March 13, 2003 <br /> Page 6 <br /> Remediation System Performance Summary <br /> Soil vapor extraction was initiated at the site on September 26, 2002, under Authority to Construct <br /> number N-4613-1-0, issued by the San Joaquin Valley Air Pollution Control District (SJVAPCD) <br /> Ozone sparging was initiated at the site on November 20, 2002 Operation and maintenance (O&M) <br /> of the remediation system is performed on a weekly basis A brief description and performance <br /> evaluation of the remedial system between January 16 and February 5, 2003, is presented below <br /> SVE System <br /> The soil vapor extraction (SVE) system is comprised of ten SVE wells (VE-1 through VE-10) and <br /> utilizes a Solleco TCAT 500 scfm catalytic oxidizer as the abatement device During the first quarter <br /> 2003, the SVE system was approximately 100% operational, and the SVE system removed <br /> approximately 222 9 pounds of TPHg, 3 3 pounds of benzene, and 0 pounds of MtBE SVE system <br /> operational and analytical data including hours of operation, applied vacuum, flow rate, ambient <br /> dilution status, field FID, influent TPHg and benzene concentrations, and mass removal data are <br /> presented in Table 5 MtBE removal data is presented in Table 6 A summary of the emissions data <br /> is supplied in Table 7 SVE well data, including open/closed status, vacuum, flow, and FID data are <br /> presented in Table 8 Graphical presentation of TPHg and benzene mass removal and influent <br /> concentration data are shown on Figures 6 and 7 Copies of the O&M field notes are included in <br /> Attachment 1 Influent and effluent vapor sample laboratory analytical reports are included in <br /> Attachment 2 <br /> Ozone Spargeng System <br /> 3 <br /> An ozone generator, enclosed in a wooden shed, injects ozone into groundwater in 20 ozone sparge <br /> wells (S-1 through S-20) located onsite and offsite A ozone meter installed in the shed will shut <br /> down the remediation system if the sensor detects excessive ozone levels greater than 0 01 ppm <br /> within the shed The ozone injection manifold is set up to inject ozone for 10 minutes at a time into <br /> the sparge wells It can cycle through 10 wells at 100% the maximum injection rate, or all 20 wells <br /> (two wells at a tame) at 50% the maximum injection rate With either arrangement, approximately, <br /> 2 5 pounds of ozone (total for all wells) is injected into the subsurface each day <br /> After system startup on November 26, 2002, several ozone leaks were detected at the injection <br /> manifold and were repaired O&M has since been performed weekly to record ozone sparge <br /> operational data such as ozone concentrations and hours of operation, and to check for leaks at the <br /> ozone injection manifold and the ozone sparge wellheads During the first quarter 2003, ozone was <br /> not detected around any ozone sparge well boxes or inside the compound Historical operational <br /> data including well open/closed status, flow rate, and applied pressure data are presented in Table 9 <br /> Future Work <br /> Future work planned in the second quarter 2003 include the following tasks <br /> + Transfer site to new environmental consultant to perform future environmental work <br /> r <br /> Riverbank-03-10 doe SECOR lntematronal Incorporated <br /> 5 <br />
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