Comparative electrochemical treatments of two chlorinated aliphatic hydrocarbons. Time course of the main reaction by-products
• DCA and TCA more quickly degraded by electro-Fenton with BDD than anodic oxidation. • Faster mineralization of TCA compared to DCA. • Reaction pathways include oxidative and cathodic reductive dechlorination steps. • Chloroacetic, dichloroacetic, acetic, oxalic and formic acids are major by-produc...
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Published in | Journal of hazardous materials Vol. 192; no. 3; pp. 1555 - 1564 |
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Main Authors | , , , |
Format | Journal Article |
Language | English |
Published |
Kidlington
Elsevier B.V
15.09.2011
Elsevier |
Subjects | |
Online Access | Get full text |
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Summary: | • DCA and TCA more quickly degraded by electro-Fenton with BDD than anodic oxidation. • Faster mineralization of TCA compared to DCA. • Reaction pathways include oxidative and cathodic reductive dechlorination steps. • Chloroacetic, dichloroacetic, acetic, oxalic and formic acids are major by-products. • Released Cl
− is oxidized to ClO
3
− and mostly to ClO
4
− by bulk
OH and BDD(
OH).
Acidic aqueous solutions of the chlorinated aliphatic hydrocarbons 1,2-dichloroethane (DCA) and 1,1,2,2-tetrachloroethane (TCA) have been treated by the electro-Fenton (EF) process. Bulk electrolyses were performed at constant current using a BDD anode and an air diffusion cathode able to generate H
2O
2 in situ, which reacts with added Fe
2+ to yield
OH from Fenton's reaction. At 300
mA, almost total mineralization was achieved at 420
min for solutions containing 4
mM of either DCA or TCA. Comparative treatments without Fe
2+ (anodic oxidation) or with a Pt anode led to a poorer mineralization. The better performance of the EF process with BDD is explained by the synergistic action of the oxidizing radicals, BDD(
OH) at the anode surface and
OH in the bulk, and the minimization of diffusional limitations. The decay of the initial pollutant accomplished with pseudo first-order kinetics. Chloroacetic and dichloroacetic acids were the major by-products during the degradation of DCA and TCA, respectively. Acetic, oxalic and formic acids were also identified. The proposed reaction pathways include oxidative and reductive (cathodic) dechlorination steps. Chlorine was released as Cl
−, being further oxidized to ClO
3
− and, mostly, to ClO
4
−, due to the action of the largely generated BDD(
OH) and
OH. |
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Bibliography: | http://dx.doi.org/10.1016/j.jhazmat.2011.06.075 ObjectType-Article-1 SourceType-Scholarly Journals-1 ObjectType-Feature-2 content type line 23 |
ISSN: | 0304-3894 1873-3336 |
DOI: | 10.1016/j.jhazmat.2011.06.075 |