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ARCHIVED REPORTS_XR0005088
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545571
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ARCHIVED REPORTS_XR0005088
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Last modified
9/16/2020 1:42:05 AM
Creation date
3/18/2020 4:03:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005088
RECORD_ID
PR0545571
PE
3528
FACILITY_ID
FA0003570
FACILITY_NAME
BOBS MUFFLER & RADIATOR
STREET_NUMBER
466
STREET_NAME
MOFFAT
STREET_TYPE
BLVD
City
MANTECA
Zip
95336
APN
22104019
CURRENT_STATUS
02
SITE_LOCATION
466 MOFFAT BLVD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' 11 February 2003 <br /> • ' <br /> -AGE-NC Project No. 98-0520 <br />' Page I 1 of 21 ; <br />' There is considerable variation in the types of bacteria used by different remediation consultants for ; <br /> bioremediation. The bacteria are cultured and selected for their ability to degrade petroleum <br /> hydrocarbons.They are microaerophilic and facultatively anaerobic,and therefore abundant oxygen <br /> is not necessary for the process to occur. Exotic fbims of oxygen (such as hydrogen peroxide or <br /> liquid oxygen) are usually not required. <br /> Free oxygen increases,the metabolic rates of reaction in the bacteria. A small blower delivering <br /> atmospheric air to the subsurface at a rate of two to five standard cubic feet per minute (scfm)per <br /> well can be used to enhance air flow and oxygen concentrations during the process. This may result <br /> ' in unwanted dehydration of the soil, but dehydration can be ameliorated by monthly injection of <br /> distilled water to each well. <br /> ' The hydrocarbon-degrading bacteria are also tolerant to a wide range of soil conditions. For <br /> instance,,pH can range from 4.0 to 9.5 and electrical conductivity has little or no effect unless <br /> sodium concentrations exceed 5% on a weight basis. <br /> . 6.3.3. Inoculation Wells <br /> The effective radius of influence in soil of inoculation wells is typically 15 feet.Existing monitoring <br /> ' wells can be used for inoculation of the smear zone as well as ground water, but the inoculum will <br /> tend to go to the bottom of a monitoring well and pass into the saturated ground water zone from the <br /> annular space near the bottom.Although a greater radius of influence is usually obtained for ground <br /> ' water inoculation, since ground water movement can assist the bacterial migration, additional <br /> inoculation points would be needed for in-situ soil treatment of the vadose zone,utilizing temporary <br /> inoculation points or soil borings. <br /> 6.3.4. Monitoring Activities <br /> After inoculation, the inoculation wells and ground water monitoring wells should be monitored <br /> over a period of several months through periodic field measurements of organic vapor, carbon <br /> dioxide, and oxygen concentrations. Quarterly or semi-annual monitoring activities should also , <br /> ' include the installation of soil borings to collect soil samples to monitor bacterial populations, <br /> nutrient availability and soil remediation progress.If monitoring indicates areas of slow remediation, <br /> ' additional inoculation or addition of nutrients may be required. - <br /> 1 <br /> Advanced CeoEnvironmental,Inc. <br />
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