B1 Fe(0) and Coke as “Active” Cap Media for PCB Destruction/Sequestration Gregory V. Lowry Kathleen M. Johnson Paul J. Murphy Meghan L. Smith EPA-TIO Anacostia.

Slides:



Advertisements
Similar presentations
ABSTRACT Background. Sydney Harbour (SH), Nova Scotia has long been subject to effluent and atmospheric inputs of metals, polycyclic aromatic hydrocarbons.
Advertisements

PCBs Total Maximum Daily Loads San Francisco Bay Fred Hetzel SFB-RWQCB May 13, 2003.
1 Utilizing Engineered Permeable Reactive Caps To Minimize Re-Suspension Of COC – Post Dredge WEDA Midwest Chapter – Green Bay April 27, 2012 Allen Bullock.
Irene Seco Manuel Gómez Alma Schellart Simon Tait Erosion resistance and behaviour of highly organic in-sewer sediment 7th International Conference on.
LEACHATE MANAGEMENT AND TREATMENT
NASSCO and Southwest Marine Sediment Investigation Preliminary Results Thomas Ginn, Ph.D. Dreas Nielsen June 18, 2002.
Biodegradation and Natural Attenuation
Basic concepts (Early Diagenesis, chapters 2-3) Transport and Physical properties Sedimentation without diagenesis (reactions that alter solid composition.
Dale T Littlejohn Senior Geologist. What is fate and transport in the vadose zone? Vadose Zone Hydrocarbon release from buried pipeline Aquifer Surface.
Gas/Particle Partitioning. Why is gas/particle partitioning important? Dispersion of Pollutants Introduced into the Atmosphere as Determined by Residence.
Land Treatment of Mine Water Presented by: Andre Sobolewski, Microbial Technologies.
Environmental Geosciences Human Interactions with the Environment Andrea Koschinsky Organics.
Environmental Geotechnology Presentation Naval Air Station, Pensacola, Florida.
Biodegradation of organic pollutants in a composting environment in Mauritius Vijayalaxmi Jumnoodoo PhD Candidate Department of Chemical and Environmental.
Sediment Quality Criteria William Fish Civil Engineering Environmental Sciences And Resources.
Sydney Tar Ponds, Canada Matt Greaves and Tom Baker.
Permeable Reactive Barriers for Inorganic Contaminants and Treatment of Acid Rock Drainage USEPA Scientist - to - Scientist Meeting Las Vegas, Nevada June.
1 Kent S. Sorenson, Jr. Ryan A. Wymore Enhanced Bioremediation for Treatment of Chlorinated Solvent Residual Source Areas – Case Study and Implications.
Modeling Phytoremediation of Heavy Metal Contaminated Mine Spoil Dumps
Organic Compounds 1. Organic Compound Properties In general, not very soluble in water Uncharged or weakly charged Can exist as dissolved, solid, or gaseous.
Enhancement of Pollutant Removal in Bioretention Cells by Soil Amendment Glenn O. Brown, Professor, PE, Ph.D., D.WRE Biosystems and Agricultural Engineering.
University of Georgia College of Agriculture and Environmental Sciences Department of Crop and Soil Sciences Environmental Sciences.
R SRP Research Webinar Session II February 9, 2015 Dual-Biofilm Reactive Barrier for Treatment of Chlorinated Benzenes at Anaerobic- Aerobic Interfaces.
CE 510 Hazardous Waste Engineering
Emergy & Complex Systems Day 4, Lecture 8 …. Emergy and Environmental Impact Assessment Emergy and Environmental Impact Assessment Oil spill, phosphate.
Adsorption Equilibrium Adsorption vs. Absorption –Adsorption is accumulation of molecules on a surface (a surface layer of molecules) in contact with an.
The situation in Norway concerning sediments/dredging Tore Lundestad, Port of Borg, Norway.
Effects of copper on marine invertebrate larvae in surface water from San Diego Bay, CA Gunther Rosen 1, Ignacio Rivera-Duarte 1, Lora Kear-Padilla 2,
Porewater Collection and Risk Evaluation 27 th Alabama Water Resources Conference Orange Beach, AL Jacob Gruzalski Environmental Standards, Inc.
1 of 25 The EPA 7-Step DQO Process Step 5 - Define Decision Rules 15 minutes Presenter: Sebastian Tindall DQO Training Course Day 2 Module 14.
Hazardous Waste/ Bioremediation
Ross MacNames Edward Jackson Samantha Quiroga.  Elevated levels of Polychlorinated Biphenyls (PCBs) found in sediment of the Little Brazos River
Hazardous Materials HAZMATs Chemicals That Present Hazard or Risk –Ignitability: catch fire readily; gasoline –Corrosivity: may corrode storage tanks (e.g.
Waste Management Overview & Land Disposal Restrictions.
Fate and Transport of Ethanol in the Environment Presented to the Environmental Protection Agency Blue Ribbon Panel Presented by Michael C. Kavanaugh,
VLIZ Spatial and Temporal Assessment of high Resolution Depth profiles Using novel Sampling Technologies Lille, March 18, 2005 Modelling metal speciation.
BIOCHLOR A Screening Level Natural Attenuation Model and Database for Solvents C.E. Aziz C. J. Newell A.P. Smith Groundwater Services, Inc. J.R. Gonzales.
: Heavy Metal Contamination in Highway Marking Glass Beads NJDOT Research Study: Heavy Metal Contamination in Highway Marking Glass Beads Conducted by:
Hierarchical Modeling Linking to Science-Support Models EXAMPLE Hierarchical Modeling Linking to Science-Support Models Groundwater Modeling System RT3D.
Bioremediation-From the Lab to the Field
Value of Mass Balance Modeling in Formulating a PTS Reduction Strategy for the Great Lakes Joseph V. DePinto Limno-Tech, Inc. Ann Arbor, MI GLRC PBS Strategy.
Bioremediation Definition: Use of living organisms to transform, destroy or immobilize contaminants Goal: Detoxification of the parent compound(s) and.
Evaluation of Intrinsic Biodegradation and Amendments to Support Enhanced Monitored Natural Recovery of Sediments Tom Krug and David Himmelheber, Geosyntec.
Are SPLP or TCLP testing data adequate for understanding soil adsorption coefficients? Chris Bailey, T&T.
Sheen Characterization 2009 Data and Observations July 2010 Progress Meeting McCormick & Baxter Superfund Site Portland, Oregon.
NIRT: Targeted Delivery and Microbial Interactions of Polymer-Functionalized Nanoparticles for Groundwater Source-Zone Remediation (BES ) 1,2 Robert.
Decommissioned BCR Organic Media Characterization Standard Mine Superfund Site, Crested Butte, CO Neal Gallagher, Eric Blumenstein, Tom Rutkowski, John.
Application of Method 1668A to the Analysis of Dioxin-Like PCBs and Total PCBs in Human Tissue and Environmental Samples Coreen Hamilton, Todd Fisher,
Polychlorinated Biphenyls (PCBs)
Developing a Cumulative Effects Monitoring Program for the Saint John Harbour – Contaminants Karen Kidd and Angella Mercer Canadian Rivers Institute, UNB.
In-situ Immobilization of Mercury in Sediment and Soil by A New Class of Stabilized Iron Sulfide Nanoparticles Zhong Xiong, Feng He, Don Zhao, Mark O.
Partitioning and Bioavailability Assessment for Sediments from South Wilmington Wetlands Huan Xia and Upal Ghosh Department of Chemical, Biochemical,
1 of 27 The EPA 7-Step DQO Process Step 5 - Define Decision Rules (15 minutes) Presenter: Sebastian Tindall Day 2 DQO Training Course Module 5.
US Army Corps of Engineers BUILDING STRONG ® Dynamic PCB Partitioning in Ashtabula Harbor, Ohio Sediments Andrew Lenox Environmental Engineer US Army Corps.
Developing Functional Fe 0 -based Nanoparticles for In Situ Degradation of DNAPL Chlorinated Organic Solvents Greg Lowry 1, Kris Matyjaszewski 2, Sara.
In Situ Sediment Treatment: State of the Practice
Potomac Toxics Monitoring Status and Issues ICPRB March 8, 2004.
Titansorb ® Filter Media for Arsenic removal by Watch ® GmbH.
1 FORMER COS COB POWER PLANT From Characterization to Redevelopment Brownfields2006 November 14, 2006.
Presentation for Office of Surface Mines on Potential Use of the Leaching Environmental Assessment Framework to enhance source terms for use of CCRs in.
INTRODUCTION Cd Usually it combined with other elements such: oxygen, chlorine, or sulfur. Cd 2+ activities in soils is about M. levels of Cd in.
Benefits of Laboratory Treatability Studies in Support of Full-Scale Design for In Situ Remedies Michaye McMaster Geosyntec Consultants Sandra Dworatzek.
Recycling of APC fly ash in a pilot-scale road subbase
Mark L. Brusseau University of Arizona
Department Civil and Environmental Engineering
Elizabeth River PCB TMDL Study: Numerical Modeling Approach
James River PCB TMDL Study: Numerical Modeling Approach
Effects of phosphate rock and iron-oxide on immobilization of lead and arsenic in Florida shooting range soils U. Saha, A. Fayiga, A. Wang, L.Q. Ma, and.
FAQs for Evaluating the Soil-to-Groundwater Pathway
Development of Activated Hydrochar from Paddy Straw
Presentation transcript:

B1 Fe(0) and Coke as “Active” Cap Media for PCB Destruction/Sequestration Gregory V. Lowry Kathleen M. Johnson Paul J. Murphy Meghan L. Smith EPA-TIO Anacostia River Internet Seminar March 12, 2003

B2 Overview “Active” cap concept Potential “active” media –Fe(0)-based media for PCB dechlorination –Coke breeze to strongly sequester PCBs Simulated cap performance Media concerns Summary

B3 Conceptual Model Criteria: No PCB flux through active layer after 100 years Degradable Products q River Water Contaminated Sediment Active Layer(s) Bioturbation Layer Consolidation Layer Z=0 +Z

B4 Potential “Active” Media Study Goals –Evaluate suitability of Fe(0) and coke as ‘active” media Measure PCB destruction rates and partition coefficients Determine cap composition and thickness Estimate costs based on reactivity, lifetime, and materials costs

B5 Rationale for Fe(0) Fe(0)-based reactants are proven dechlorinators –Fe(0) dechlorinates halogenated hydrocarbons e.g. TCE and other chlorinated solvents Extensive use in PRBs –Pd/Fe(0) dechlorinates PCBs Grittini et al. 1995, Wang et al –Nano-sized Fe(0) may dechlorinate PCBs Wang et al Low levels of H 2 produced during Fe(0) corrosion –Potential to stimulate microbial dechlorination

B6 Approach Fe(0) Batch experiments monitoring PCB loss and product formation –Peerless Fe(0) –Pd/Fe(0) –Nano-size iron Individual PCB congeners –Structure/activity relationships

B7 Fe(0) Media Nano Fe(0) Size: nm Fisher Fe(0) Size: 0.15 mm Peerless Fe(0) Size: mm 0.05% Pd/Peerless Fe(0) Size: mm

B8 Nano Fe(0) B8

B9 0.05% Pd/Fe(0) B9

B10 Fe(0) Reactive Media Summary MEDIARESULTS k (yr –1 ) RELATIVE COST Commercial Fe(0)No Observable Reaction0$$ Pd/Fe(0) (500 ppmw Pd) Rapid dechlorination of 22’35’ does not appear sustainable 21$$$ Nano Fe(0) Dechlorination of 22’35’-CB to 22’3-CB and other congeners 6$$$$

B11 Rationale for Coke Breeze Inexpensive –~$40/ton Environmentally Friendly –TCLP good –Likely to meet SQVs and CCC * standards *EPA 822-Z Sequestered PCBs less bioavailable –Talley et al. 2002

B12 Furnace Coke and Coke Breeze

B13 Properties: Coal vs. Coke COALCOKE Moisture (%)42 Volatile Organics (%)300.7 Fixed Carbon (%)6092 Ash (%)67 Porosity (%) Size (mm)--<20 Particle Density (g/cm 3 )

B14 Sorptive Media Coke –Strong PCB sorption (K d ) –Less bioavailable (Talley et al. 2002) Sediment (low) Fly Ash COKE Sediment (high) Activated Carbon K d (L/kg) b Jonker et al SORPTION STRENGTH

B15 Modeling Diffusive Transport of Biphenyl CAP MEDIAn (--)K d (L/kg)R Sand a Peerless Fe(0) b Coke0.660,00072,000 a f oc = 0.001, b f oc = 0.02, K d =K oc *f oc, log K oc =4 (biphenyl) D e =1.9 E-5 cm 2 /s for all cases. This incorporates diurnal seepage of ±5 cm/d due to tides.

B16 Simulated Porewater Concentration Profiles of Biphenyl after 100 Years B16

B Year Performance: Required Active Layer Thickness & Cost $/m 2 ($/ft 2 ) B17

B18 Media Concerns Toxicity –Fe(0) Peerless Fe(0) contains heavy metals (% range) Metals should remain sequestered (not demonstrated) –Coke Little or no concern TCLP test OK CCC should be met (under investigation) SQVs should be met (under investigation)

B19 Coke: TCLP and CCC Criteria MetalCoke (mg/kg) Leachate (mg/L) TCLP Limit (mg/L) CCC Limit (mg/L) Arsenic<10< Barium N/A Cadmium<10< Chromium<10< Lead<10< Selenium<10<0.11N/A Mercury<0.033< Silver<10< TCLP=Toxic Characteristics Leaching Procedure CCC=Criterion Continuous Concentration

B20 Active Capping Summary Coke –Inexpensive and promising PCB sequestration media –Thinnest caps possible –Provides NO PCB dechlorination Fe(0) –Cost-effective abiotic PCB destruction NOT currently possible –Fe(0)-enhanced biodegradation possible, but not yet explored Mixed Fe(0)/coke cap –Provides sequestration –PCB dechlorination possible but not proven

B21 Ongoing Research PCB sorption isotherms for coke breeze Fe(0)-sediment-coke microcosms to assess potential for enhanced PCB biodegradation Column studies to assess long term performance of each media Methods for Evaluating Cap Performance

B22 Acknowledgements HSRC S & SW EPA SITE Program NSF Alcoa

B23 Thank You After viewing the links to additional resources, please complete our online feedback form. Thank You Links to Additional Resources C23