&EFA
United States
Environmental Protection
Agency
Solid Waste and
Emergency Response
5403W
EPA510-F-93-018
October 1993
Groundwater
Remediation For
UST Sites
In Situ Bioremediation
In situ bioremediation is a technique for removing
biodegradable contaminants from groundwater. The
technique relies on microorganisms and supplemental
oxygen and nutrients to break down petroleum products
in the groundwater.
In situ bioremediation offers the advantage of being able
to treat contamination in place, without the need for
pumping or the subsequent treatment of pumped
groundwater. The technique is most effective in
permeable aquifers.
Petroleum Types And Constituents
Fresh, or weathered gasoline, diesd, jet fuel,
kerosene, motor oil, heavy fuel ofl» lubricating oils,
and crude oils
Volatile organic compounds (VOCs) such as
benzene, toluene, ethylbenzene, and xylene (BTEX);
residual semivolatile organic compounds (SVOCs)
such as polynuclear aromatic hydrocarbons; and
nonvolatile constituents
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In Situ Bioremediation
Advantages
Limitations
System
Components
Wastestream
Treatment
Parameters to
Monitor1
Cleanup Levels
and Timing2
Costs5
Degrades contaminants in place
Achieves lower concentration levels than pump and
treat
Effectiveness is limited in low permeability or
heterogeneous media
Ability to transport nutrients and oxygen might be
limited by soil and groundwater mineral content or pH
Targets only biodegradable constituents
Groundwater containment system
Oxygen delivery equipment
Nutrient delivery equipment
Injection trenches
Recovery walls or trenches
Pumps
Monitoring points
Recirculated groundwater treatment options:
Air stripping
Granulated activated carbon
Bioreactors
Constituent concentrations in groundwater
Microbial population in aquifer
pH and total organic carbon
Dissolved oxygen
Nutrient concentration
Flow rates
Generally, can achieve maximum contaminant levels
(MCLs)
Achieves £ 90% reduction of biodegradable constituents
For an ideal site3, ~90% in 6 months to 1 year
For an average site4, ~90% in 6 months to 4 years
Longer time required to degrade heavier hydrocarbons
For an ideal site3, $150,000 to $250,000
For an average site4, $200,000 to $500,000
'"Parameters to mentor* are for performance purposes only; compliance monitoring parameters vary by state.
3An Ideal site" assumes no delays in corrective action and a relatively homogeneous, permeable subsurface.
Vn average stW assumes mWnal delays h corrective action and a modmtelyheterogerieous and pameabte surface.
'Costs include equipment, and operation and maintenance.
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