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Web-based Class Project on Geoenvironmental Remediation
Soil Washing Prepared by: Jonathan Hubler Ken Metz With the Support of: Report prepared as part of course CEE 549: Geoenvironmental Engineering Winter 2013 Semester Instructor: Professor Dimitrios Zekkos Department of Civil and Environmental Engineering University of Michigan
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Outline Main Concept Theoretical Background Applicability
Advantages/Disadvantages Field Setup Examples of Different Systems Costs Case Histories
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Main Concept Ex-Situ Remediation Technique
Contaminants are prone to bind to fine grained soils, which are prone to bind to coarse grained soils General Process: Wash soil with liquid (often with chemical) Scrub Soil Separate clean soils from contaminated soil and washwater
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Main Concept Volume reduction process
Washed soil may be reused as backfill Six Steps: Pretreatment Separation Coarse-grained treatment Fine-grained treatment Process water treatment Residuals management
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Process Source: US EPA 1996
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Theoretical Background
Contaminants adhere to fine grained soils, which adhere to coarse grained soils (adhesion and compaction) Physiochemical processes involved: Desorption (contaminants desorbed from soil) Dissolution/solubilization (pH changes from reactions with washwater) Oxidation reduction (results in desorption or solubilization of contaminants)
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Theoretical Background
Equation to determine contaminant concentration: At equilibrium: Equation to determine removal efficiency:
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Applicability Proven to effectively remove:
Petroleum and fuel residues Radionuclides Heavy metals PCBs PCP Pesticides Cyanides Creosote Semivolatiles Volatiles
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Applicability Good to excellent at removing VOCs and metals from sandy and gravelly soils The lower the silt/clay content the more effective soil washing will be May not be applicable if contaminants adsorbed strongly Large sites - at least 5000 tons of contaminated soil
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Advantages Cost effective
Under ideal conditions – volume reduction of 90% Reuse of cleaned soil Closed system that can be controlled (pH, temp) High rate cubic yards per day Only a few permits
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Disadvantages Large area for system
Predominantly effective for very coarse soils Ineffective for soils containing more than 30-50% fines Washwater may need special treatment ($) May produce contaminated sludge Air emissions from equipment ($) Exposure of public to contaminants
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Field Setup Varies depending upon site and project Typical plant:
125’ x 250’ Process tons per hour
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Field Setup Source: ART Engineering
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Harbauer Soil Washing System
Source: US EPA 1996
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Mobile Soil Washing System
Source: US EPA 1996
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Cost Average: $150 to $250 per ton More cost effective for larger site
Costs: Initial (bench scale) Operational Set-up and break down Chemical analysis Disposal
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Source: FRTR 2006
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Case Histories Twin Cities Army Ammunition Plant
Remediation of high levels of VOCs and heavy metals Combination of soil leaching and soil washing used successfully 20,000 tons of soil treated (every 10 tons tested) 8 heavy metals removed, less than 175 ppm (initial level of lead 86,000 ppm) Soil reused at site
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System used at Twin Cities Site
Source: Fristad 1995
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King of Prussia Technical Corp Site
Used for processing industrial liquid waste 19,200 tons of contaminated soil Soil washing system – 25 tons/hr First full-scale use of soil washing to a Superfund Site Clean up levels met (e.g. – Cu (9070 mg/kg before, 860 mg/kg after) Total cost $7.7 million
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System used at KOP site Source: US EPA 1995
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Summary Ex-situ technique Volume reduction process
Good/Excellent for VOCs and heavy metals Coarse grained soils more effective At least 5000 tons to be cost effective Average cost - $ per ton
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References ART Engineering. “Soil Washing at King of Prussia Superfund Site” < (Mar. 16, 2013). Contaminated Land: Applications in Real Environments (CL:AIRE). (2007, September). “Understanding Soil Washing.” TB13. < 16, 2013). Federal Remediation Technologies Roundtable (FRTR). (2006). “Remediation Technologies Screening Matrix and Reference Guide: 4.19 Soil Washing.” < 16, 2013). Fristad, W. E. (1995). “Case Study: Using soil washing/leaching for the removal of heavy metal at the twin cities army ammunition plant.” Remediation, 5(4), Griffiths, Richard A. (1995). “Soil-washing technology and practice.” Journal of Hazardous Materials Sharma, Hari D., and Krishna R. Reddy (2004). "Soil Remediation Technologies." Geoenvironmental Engineering: Site Remediation, Waste Containment, and Emerging Waste Management Technologies. Wiley, Hoboken, NJ, United States Department of Energy (USDOE). (1998, July). “Cost and Performance Report: Chemical Extraction for Uranium Contaminated Soil, RMI Titanium Company Extrusion Plant Ashtabula Ohio.” USDOE. United States Environmental Protection Agency (USEPA). (1996, April). “A Citizen's Guide to Soil Washing.” EPA 542-F USEPA. (1995, March). “Cost and Performance Report: Soil Washing at the King of Prussia Technical Corporation Superfund Site Winslow Township New Jersey”. < 16, 2013) USEPA. (1991, September). “Guide for Conducting Treatability Studies Under CERCLA: Soil Washing.” Washington D.C., EPA/540/2-91/020A. USEPA. (1993, November). “Innovative Site Remediation Technology: Soil Washing/Soil Flushing.” EPA 542-B USEPA (1983, September). “NPL Site Fact Sheet: King of Prussia, New Jersey.” < (Mar. 16, 2013). USEPA (2010, September). “Superfund Remedy Report.” 13. EPA-542-R
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More Information More detailed technical information on this project can be found at:
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