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3500 - Local Oversight Program
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PR0545734
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Entry Properties
Last modified
6/5/2020 1:20:26 PM
Creation date
6/4/2020 2:57:35 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545734
PE
3528
FACILITY_ID
FA0010191
FACILITY_NAME
TRACY-PONTIAC-CADILLAC-GMC TRUCK
STREET_NUMBER
2450
STREET_NAME
TOSTE
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
238020-06
CURRENT_STATUS
02
SITE_LOCATION
2450 TOSTE RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' 18 July 2002 <br /> AGE-NC Project No 96-0254 <br /> Page 9 of 17 <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 scfin per well can be used to enhance air <br /> flow and oxygen concentrations during the process This may result in unwanted dehydration of the <br /> ' soil, but dehydration can be ameliorated by monthly injection of distilled water to each well <br /> The hydrocarbon-degrading bacteria are also tolerant to a wide range ofsoll conditions For instance, <br /> ' pH can range from 4 to 9 5 and electrical conductivity has little or no effect unless sodium <br /> concentrations exceed 5% on a weight basis <br /> 5 2 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 wcll 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 /> 5 2 4 Monitoring Activities <br /> ' After inoculation,the inoculation wells and groundwater monitoring wells should bemonitoredover <br /> a period of several months through periodic field measurements of organic vapor, carbon dioxide, <br /> and oxygen concentrations Quarterly or semi-annual monitoring activities should also include the <br /> ' installation of soil borings to collect soil samples to monitor bacterial populations, nutrient <br /> availability and soil remediation progress If monitoring Indicates areas of slow remediation, <br /> additional inoculation or addition of nutrients maybe required <br /> 5 2 5 Duration <br /> tDuration(and cost) is dependent on the volume of soil and i,,rater to be remediated, the number of <br /> inoculation and monitoring wells,the average concentrations of contaminants and nutrients,and the <br /> ' temperature and permeability of the soil Theoretically,the radius of influence oftheinoculation well <br /> should increase rapidly at first, then gradually decline as the affected volume Increases and the <br /> bacteria encounter decreasing hydrocarbon concentrations toward the margins of the hydrocarbon <br /> ' plume Shorter-chain hydrocarbons are typically consumed first and longer-chain hydrocarbons later <br /> • Remediation at sites with similar soil composition typically takes between 12 and 48 months <br /> IAdvanced GwEnvimnnwnhl,Inc <br />
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