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ARCHIVED REPORTS_XR0008335
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0541936
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ARCHIVED REPORTS_XR0008335
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Entry Properties
Last modified
5/18/2020 12:39:58 PM
Creation date
5/18/2020 11:07:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008335
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
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LSauers
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EHD - Public
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including hours of operation, applied vacuum, flow rate, field PID data, influent TPHg and benzene <br /> concentrations, and mass removal data-are presented in Table 2. <br /> MTBE removal data are presented in Table 3. A summary of the emissions data is presented in <br /> Table 4. SVE well data, including open/closed status; vacuum, flow, and PID.data are presented-in <br /> Table 5. Graphical presentation of TPHg and benzene mass removal and influent concentration data <br /> are shown on Figures 6 and 7, respectively. Copies of the O&M field notes are included in <br /> Appendix A. Influent and effluent vapor sample laboratory analytical reports are included in <br /> Appendix B, <br /> As shown in Figure 6; the SVE system influent contaminant concentrations have remained fairly <br /> consistent since January 2004 with an average influent TPHg concentration of 138 ppmv.. The <br /> number of wells open to vacuum have been reduced to wells V2, V3,V5,.and V6. The mass removal <br /> trend (Figure 7).demonstrates that mass removal is on a steady lowangle incline. <br /> 3.3.2 Ozone Sparge 5 stem <br /> A .skid-mounted ozone sparge system, enclosed in a shed within the remediation compound, can <br /> inject ozone into groundwater through 19 available ozone sparge wells (S-1 through S-19) located <br /> on- and offsite. Sparge well S-20 was not connected to the sparge system manifold and is not used. <br /> An ozone meter attached to the ozone sparge system skid will shut down the remediation system if <br /> ozone is detected at levels greater than 0.01 ppm within the.shed, The ozone injection manifold is set <br /> up to inject ozone for 10 minutes at a time into the sparge wells. It can cycle through 10 wells at <br /> 100% the maximum injection rate (one well at a time), or all 19 wells(two wells at a time) at 50% <br /> the maximum injection rate. Approximately 2.5 pounds of ozone can be injected into the subsurface <br /> each day at optimum ozone production. Ozone production is variable dependent on atmospheric <br /> temperatures, The ozone sparge system is designed to deliver at an approximate-rate of 6 liters per <br /> minute. <br /> The ozone sparge system operated 86% of the time during the for the reporting period, Since April 9, <br /> the sparge system operated 100% of the time up to May 3. On May 3, it was observed that ozone was <br /> not being delivered to the sparge points due to mineral deposits in-the ozone lines. The lines were <br /> cleared and the Ozone sparge system was returned to service. On May 26, it was discovered that the <br /> air compressor on the sparge system had failed (piston blew through the casing of the compressor) <br /> and needed replacement, A new compressor was purchased from Nor Cal Instruments. On June 14, <br /> the new compressor was installed and the ozone sparge system was returned to service, At that time, <br /> the ozone .sparge system was capable of operating at maximum productivity producing <br /> approximately 2.5 pounds of ozone per day and delivering at a rate of 8 to 10 liters per hour. <br /> However, summer temperatures inside the ozone sparge shed have exceeded 100° Fahrenheit and <br /> ozone production was reduced. <br /> Project No.58643-06-01 .8 December 30,2004 <br />
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