Reduction of chlorinated ethanes by nanosized zero-valent iron: kinetics, pathways, and effects of reaction conditions.

Nanosized iron (< 100 nm in diameter) was synthesized in the laboratory and applied to the reduction of eight chlorinated ethanes (hexachloroethane (HCA), pentachloroethane (PCA), 1,1,2,2-tetrachloroethane (1,1,2,2-TeCA), 1,1,1,2-tetrachloroethane (1,1,1,2-TeCA), 1,1,2-trichloroethane (1,1,2-TCA), 1,1,1-trichloroethane (1,1,1-TCA), 1,2-dichloroethane (1,2-DCA), and 1,1-dichloroethane (1,1-DCA)) in batch reactors. Reduction of 1,1,1-TCA increased linearly with increasing iron loading between 0.01 and 0.05 g per 124 mL solution (0.08-0.4 g/L). Varying initial concentrations of PCA between 0.025 and 0.125 mM resulted in relatively constant pseudo-first-order rate constants, indicating PCA removal conforms to pseudo-first-order kinetics. The reduction of 1,1,2,2-TeCA decreased with increasing pH; however, dehydrohalogenation of 1,1,2,2-TeCA became important at high pH. All chlorinated ethanes except 1,2-DCA were transformed to less chlorinated ethanes or ethenes. The surface-area-normalized rate constants from first-order kinetics analysis ranged from < 4 x 10(-6) to 0.80 L m(-2) h(-1). In general, the reactivity increased with increasing chlorination. Among tri- and tetrasubstituted compounds, the reactivity was higher for compounds with chlorine atoms more localized on a single carbon (e.g., 1,1,1-TCA > 1,1,2-TCA). Reductive beta-elimination was the major pathway for the chlorinated ethanes possessing alpha,beta-pairs of chlorine atoms to form chlorinated ethenes, which subsequently reacted with nanosized iron. Reductive alpha-elimination and hydrogenolysis were concurrent pathways for compounds possessing chlorine substitution on one carbon only, forming less chlorinated ethanes.

[1]  W. Shiu,et al.  A critical review of Henry’s law constants for chemicals of environmental interest , 1981 .

[2]  J. Khim,et al.  Rapid reductive destruction of hazardous organic compounds by nanoscale Fe0. , 2001, Chemosphere.

[3]  A. Dahmke,et al.  Combined Zero- and First-Order Kinetic Model of the Degradation of TCE and cis-DCE with Commercial Iron , 1999 .

[4]  J. Gotpagar,et al.  Reductive dehalogenation of trichloroethylene using zero-valent iron , 1997 .

[5]  S. Braus-Stromeyer,et al.  Dichloromethane as the sole carbon source for an acetogenic mixed culture and isolation of a fermentative, dichloromethane-degrading bacterium , 1993, Applied and environmental microbiology.

[6]  D. Sholl,et al.  TCE dechlorination rates, pathways, and efficiency of nanoscale iron particles with different properties. , 2005, Environmental science & technology.

[7]  R. Gillham,et al.  Reduction of N-nitrosodimethylamine with granular iron and nickel-enhanced iron. 2. Mechanistic studies , 2000 .

[8]  Peter Adriaens,et al.  Carbon tetrachloride transformation on the surface of nanoscale biogenic magnetite particles. , 2004, Environmental science & technology.

[9]  Hsing-Lung Lien,et al.  Treatment of chlorinated organic contaminants with nanoscale bimetallic particles , 1998 .

[10]  Thomas E. Mallouk,et al.  Hydrodechlorination of Trichloroethylene to Hydrocarbons Using Bimetallic Nickel-Iron Nanoparticles , 2002 .

[11]  Timothy L. Johnson,et al.  Kinetics of Halogenated Organic Compound Degradation by Iron Metal , 1996 .

[12]  J. Vogan,et al.  Performance evaluation of a permeable reactive barrier for remediation of dissolved chlorinated solvents in groundwater. , 1999, Journal of hazardous materials.

[13]  D. Burris,et al.  Chlorinated Ethene Reduction by Cast Iron: Sorption and Mass Transfer , 1998 .

[14]  Elizabeth R. Carraway,et al.  Dechlorination of Pentachlorophenol by Zero Valent Iron and Modified Zero Valent Irons , 2000 .

[15]  Wei-xian Zhang,et al.  Transformation of chlorinated methanes by nanoscale iron particles , 1999 .

[16]  Tie-hui Li,et al.  Reductive Dechlorination of Trichloroethene and Carbon Tetrachloride Using Iron and Palladized-Iron Cathodes , 2000 .

[17]  E. C. Butler,et al.  Effects of iron purity and groundwater characteristics on rates and products in the degradation of carbon tetrachloride by iron metal. , 2004, Environmental science & technology.

[18]  A. L. Roberts,et al.  Pathways and Kinetics of Chlorinated Ethylene and Chlorinated Acetylene Reaction with Fe(0) Particles , 1999 .

[19]  J. Farrell,et al.  Electrochemical investigation of the rate-limiting mechanisms for trichloroethylene and carbon tetrachloride reduction at iron surfaces. , 2001, Environmental science & technology.

[20]  Yong-Hong Chen,et al.  Dechlorination of chloromethanes on iron and palladium‐iron bimetallic surface in aqueous systems , 1999 .

[21]  T. Mallouk,et al.  Surface Chemistry and Electrochemistry of Supported Zerovalent Iron Nanoparticles in the Remediation of Aqueous Metal Contaminants , 2001 .

[22]  W. Ford,et al.  Poly(propylene imine) dendrimer complexes of Cu(II), Zn(II), and Co(III) as catalysts of hydrolysis of bis-(p-nitrophenyl) phosphate , 1999 .

[23]  Paul G Tratnyek,et al.  Characterization and properties of metallic iron nanoparticles: spectroscopy, electrochemistry, and kinetics. , 2005, Environmental science & technology.

[24]  Rosy Muftikian,et al.  A method for the rapid dechlorination of low molecular weight chlorinated hydrocarbons in water , 1995 .

[25]  Hsing-Lung Lien,et al.  Nanoscale iron particles for complete reduction of chlorinated ethenes , 2001 .

[26]  D. Burris,et al.  Sorption of trichloroethylene and tetrachloroethylene in a batch reactive metallic iron-water system. , 1995, Environmental science & technology.

[27]  M. Macka,et al.  Capillary electrophoretic study of interactions of metal ions with crown ethers, a sulfated β‐cyclodextrin, and zwitterionic buffers present as additives in the background electrolyte , 2002, Electrophoresis.

[28]  U. Wiesmann,et al.  Kinetics and reaction engineering aspects of the biodegradation of dichloromethane and dichloroethane , 1996 .

[29]  Wei-xian Zhang,et al.  Synthesizing Nanoscale Iron Particles for Rapid and Complete Dechlorination of TCE and PCBs , 1997 .

[30]  M. Scherer,et al.  Kinetics of nitrate, nitrite, and Cr(VI) reduction by iron metal. , 2002, Environmental science & technology.

[31]  Timothy L. Johnson,et al.  Degradation of carbon tetrachloride by iron metal: Complexation effects on the oxide surface , 1998 .

[32]  R. Gillham,et al.  Reduction of n-nitrosodimethylamine with granular iron and nickel-enhanced iron. 1. Pathways and kinetics , 2000 .

[33]  K. Hayes,et al.  Influence of amine buffers on carbon tetrachloride reductive dechlorination by the iron oxide magnetite. , 2005, Environmental science & technology.

[34]  Robert W. Gillham,et al.  Long‐Term Performance of an In Situ “Iron Wall” for Remediation of VOCs , 1998 .

[35]  Paul G Tratnyek,et al.  Reductive dehalogenation of chlorinated methanes by iron metal. , 1994, Environmental science & technology.

[36]  D. Elliott,et al.  Field assessment of nanoscale bimetallic particles for groundwater treatment. , 2001, Environmental science & technology.

[37]  G. Hadjipanayis,et al.  Chemistry of Borohydride Reduction of Iron(II) and Iron(III) Ions in Aqueous and Nonaqueous Media. Formation of Nanoscale Fe, FeB, and Fe2B Powders , 1995 .

[38]  E. Carraway,et al.  Reductive dechlorination of TCE by zero valent bimetals , 2003, Environmental technology.

[39]  R. L. Valentine,et al.  Chemistry and Microbiology of Permeable Reactive Barriers for In Situ Groundwater Clean up , 2000 .

[40]  R. Gillham,et al.  Long-term performance monitoring for a permeable reactive barrier at the U.S. Coast Guard Support Center, Elizabeth City, North Carolina. , 1999, Journal of hazardous materials.

[41]  J. Khim,et al.  Kinetics of reductive denitrification by nanoscale zero-valent iron. , 2000, Chemosphere.

[42]  R. Schwarzenbach,et al.  Corrinoid-Mediated Reduction of Tetrachloroethene, Trichloroethene, and Trichlorofluoroethene in Homogeneous Aqueous Solution: Reaction Kinetics and Reaction Mechanisms , 1997 .

[43]  S. Aust,et al.  Iron autoxidation and free radical generation: effects of buffers, ligands, and chelators. , 2002, Archives of biochemistry and biophysics.

[44]  Tie-hui Li,et al.  Electrochemical and column investigation of iron-mediated reductive dechlorination of trichloroethylene and perchloroethylene , 2000 .

[45]  J. Gossett Measurement of Henry's law constants for C1 and C2 chlorinated hydrocarbons , 1987 .

[46]  K. Hayes,et al.  Kinetics of the Transformation of Trichloroethylene and Tetrachloroethylene by Iron Sulfide , 1999 .

[47]  W. Flanagan Biodegradation of dichloromethane in a granular activated carbon fluidized‐bed reactor , 1998 .

[48]  J. Gossett,et al.  Biodegradation of dichloromethane and its utilization as a growth substrate under methanogenic conditions , 1991, Applied and environmental microbiology.

[49]  Paul G Tratnyek,et al.  Kinetics of Carbon Tetrachloride Reduction at an Oxide-Free Iron Electrode , 1997 .

[50]  S. Judd,et al.  Zero-Valent Iron for Water Treatment , 2000 .