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Description | Synonyms | Applicability | Limitations | Site Information | Points of Contact | |
Data Needs | Performance | Cost | References | Vendor Info. | Health & Safety |
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Description:
Figure 4-32: Oxygen added to contaminated ground water and vadose zone soils can also enhance biodegradation of contaminants below and above the water table. Air sparging has a medium to long duration which may last, generally, up to a few years. |
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Synonyms: In-situ air sparging, in-situ aeration.DSERTS Code: F14 (Air Sparging) |
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Applicability: The target contaminant groups for air sparging are VOCs and fuels. Only limited information is available on the process. Methane can be used as an amendment to the sparged air to enhance cometabolism of chlorinated organics. |
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Limitations: Factors that may limit the applicability and effectiveness of the process include:
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Data Needs: A detailed discussion of these data elements is provided in Subsection 2.2.2. (Data Requirements for Ground Water, Surface Water, and Leachate). Characteristics that should be determined include vadose zone gas permeability, depth to water, ground water flow rate, radial influence of the sparging well, aquifer permeability and heterogeneities, presence of low permeability layers, presence of DNAPLs, depth of contamination, and contaminant volatility and solubility. Additionally, it is often useful to collect air-saturation data, in the saturated zone, during an air sparging test, using a neutron probe. |
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Performance Data: This technology is demonstrated at numerous sites, though only a few sites are well documented. Air sparging has demonstrated sensitivity to minute permeability changes, which can result in localized stripping between the sparge and monitoring wells. |
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Cost: The key cost driver information and cost analysis was developed in 2006 using the Remedial Action Cost Engineering and Requirements (RACER) software. Key Cost Drivers · Surface area (contaminant orientation) o Surface area of contamination is the primary cost driver, and directly affects the quantity of air sparge points. · Depth to Contamination o Depth is the secondary cost driver. Cost increases with depth since it impacts the drilling costs. Cost Analysis The following table represents estimated costs (by common unit of measure) to apply air sparging technology at sites of varying size and complexity. A more detailed cost estimate table which includes specific site characteristics and significant cost elements that contributed to the final costs can be viewed by clicking on the link below.
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References: Treatment Technologies for Site Cleanup: Annual Status Report (ASR), Tenth Edition, EPA 542-R-01-004 Innovative Remediation Technologies: Field Scale Demonstration Project in North America, 2nd Edition Treatment Experiences at RCRA Corrective Actions, December 2000, EPA 542-F-00-020 Abstracts
of Remediation Case Studies, Volume 4, June, 2000, EPA
542-R-00-006 California Base Closure Environmental Committee (CBCEC), 1994. Treatment Technologies Applications Matrix for Base Closure Activities, Revision 1, Technology Matching Process Action Team, November, 1994. EPA, 1997. Analysis of Selected Enhancements for Soil Vapor Extraction, EPA OSWER, EPA/542/R-97/007. ESTCP Document, 1999. Draft Air Sparging Design Paradigm. EPA, 2001. A Citizen's Guide to Soil Vapor Extraction and Air Sparging. EPA 542-F-01-006. Federal Remediation Technologies Roundtable, 1995. Remediation Case Studies: Bioremediation, EPA/542/R-95/002. Federal Remediation Technologies Roundtable, 1995. Remediation Case Studies: Groundwater Treatment, EPA/542/R-95/003.
Federal Remediation Technologies Roundtable, 1998. Remediation Case Studies: In Situ Soil Treatment Technologies (Soil Vapor Extraction, Thermal Processes), EPA/542/R-98/012
Federal Remediation Technologies Roundtable, 1998. Remediation Case Studies: Innovative Groundwater Treatment Technologies, EPA/542/R-98/015.
Hildebrandt, W. and F. Jasiulewicz, 1992. "Cleaning Up Military Bases," The Military Engineer, No. 55, p. 7, September-October 1992. USACE, 1997. In Situ Air Sparging Engineer Manual, EM 1110-1-4005. Treatment Technologies Applications Matrix for Base Closure Activities, November 1994 |
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Site Information:
Points of Contact:
Technology Specific Web Sites:
Vendor Information:
A list of vendors offering In Situ Physical/Chemical Water Treatment is available from EPA REACH IT which combines information from three established EPA databases, the Vendor Information System for Innovative Treatment Technologies (VISITT), the Vendor Field Analytical and Characterization Technologies System (Vendor FACTS), and the Innovative Treatment Technologies (ITT), to give users access to comprehensive information about treatment and characterization technologies and their applications. Health and Safety:
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Notice | |
Foreword | |
Report Documentation Page | |
Acknowledgement | |
Objectives | |
Background | |
How to use this document | |
Natural Resources | |
Cautionary Notes | |
Online Survey |
Presumptive Remedies | |
Data Requirements | |
Nonhalogenated VOCs | |
Halogenated VOCs | |
Nonhalogenated SVOCs | |
Halogenated SVOCs | |
Fuels | |
Inorganics | |
Radionuclides | |
Explosives |
Soil,Sed.,Bedrock & Sludge | |
In Situ Biological | |
In Situ Phys/Chem | |
In Situ Thermal | |
Ex Situ Biological | |
Ex Situ Phys/Chem | |
Ex Situ Thermal | |
Containment | |
Other Treatment | |
Ground,Surf. H2O,Leachate | |
In Situ Biological | |
In Situ Phys/Chem | |
Ex Situ Biological | |
Ex Situ Phys/Chem | |
Containment | |
Off Gas & Air Emissions | |
Biofiltration | |
High Energy Destruction | |
Membrane Separation | |
Oxidation | |
Scrubbers | |
Carbon Adsorption |
Document Sources | |
Listing by Author | |
Listing of Websites |
A. Vendors | |
B. Site Projects | |
C. Federal Databases | |
D. Factors Affecting Treat. | |
E. Source Documents | |
F. Synonyms |
Site Map | |
Screening Matrix | |
Synonym List | |
Search | |
Contact Us | |
Disclaimer, Privacy, and Security Notice |
Soil,Sed.,Bedrock & Sludge | |
Gr. & Surf. H2O, Leachate | |
Air Emissions/Off-Gases |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Techs for Air Emissions | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Techs for Air Emissions | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Techs for Air Emissions | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Techs for H2O | |
Treatment Train |
Properties & Behavior | |
Techs for Soil | |
Biological Techs | |
Thermal Techs | |
Other Techs | |
Common Techs | |
Treatment Train |
Bioventing | |
Enhanced Bioremediation | |
Phytoremediation |
Chemical Oxidation | |
Electrokinetic Sep. | |
Fracturing | |
Soil Flushing | |
Soil Vapor Extraction | |
Solidification/Stabilization |
Thermal Treatment |
Biopiles | |
Composting | |
Landfarming | |
Slurry Phase |
Chemical Extraction | |
Chemical RedOx | |
Dehalogenation | |
Separation | |
Soil Washing | |
Solidification/Stabilization |
Hot Gas Decon. | |
Incineration | |
OB/OD | |
Pyrolysis | |
Thermal Desorption |
Landfill Cap | |
Landfill Cap Enhancements |
Off-Site Disposal |
Enhanced Biodegradation | |
Natural Attenuation | |
Phytoremediation |
Air Sparging | |
Bioslurping | |
Chemical Oxidation | |
Directional Wells | |
Dual Phase Extraction | |
Thermal Treatment | |
Hydrofracturing | |
Air Stripping | |
Treatment Walls |
Bioreactors | |
Constructed Wetlands |
Adsorption/Absorption | |
Adv. Oxidation Processes | |
Air Stripping | |
GAC | |
Ground Water Pumping | |
Ion Exchange | |
Prec./Coag./Flocc. | |
Separation | |
Sprinkler Irrigation |
Physical Barriers | |
Deep Well Injection |