&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 ------- 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. ------- |