Oxidation of chlorinated ethenes by potassium permanganate: a kinetics study

The kinetics of oxidation of perchloroethylene (PCE), trichloroethylene (TCE), three isomers of dichloroethylene (DCE) and vinyl chloride (VC) by potassium permanganate (KMnO 4) were studied in phosphate-buffered solutions of pH 7 and ionic strength ∼0.05 M and under isothermal, completely mixed and...

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Veröffentlicht in:Journal of hazardous materials 2001-10, Vol.87 (1), p.155-169
Hauptverfasser: Huang, Kun-Chang, Hoag, George E, Chheda, Pradeep, Woody, Bernard A, Dobbs, Gregory M
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container_issue 1
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container_title Journal of hazardous materials
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creator Huang, Kun-Chang
Hoag, George E
Chheda, Pradeep
Woody, Bernard A
Dobbs, Gregory M
description The kinetics of oxidation of perchloroethylene (PCE), trichloroethylene (TCE), three isomers of dichloroethylene (DCE) and vinyl chloride (VC) by potassium permanganate (KMnO 4) were studied in phosphate-buffered solutions of pH 7 and ionic strength ∼0.05 M and under isothermal, completely mixed and zero headspace conditions. Experimental results have shown that the reaction appears to be second order overall and first order individually with respect to both KMnO 4 and all chlorinated ethenes (CEs), except VC. The degradation of VC by KMnO 4 is a two-consecutive-step process. The second step, being the rate-limiting step, is of first order in VC and has an activation energy ( E a) of 7.9±1 kcal mol −1. The second order rate constants at 20°C are 0.035±0.004 M −1 s −1 (PCE), 0.80±0.12 M −1 s −1 (TCE), 1.52±0.05 M −1 s −1 ( cis-DCE), 2.1±0.2 M −1 s −1 (1,1-DCE) and 48.6±0.9 M −1 s −1 ( trans-DCE). The E a and entropy (Δ S ∗) of the reaction between KMnO 4 and CEs (except VC) are in the range of 5.8–9.3 kcal mol −1 and −33 to −36 kcal mol −1 K −1, respectively. Moreover, KMnO 4 is able to completely dechlorinate CEs, and the increase in acidity of the solution due to CE oxidation by KMnO 4 is directly proportional to the number of chlorine atoms in CEs.
doi_str_mv 10.1016/S0304-3894(01)00241-2
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Experimental results have shown that the reaction appears to be second order overall and first order individually with respect to both KMnO 4 and all chlorinated ethenes (CEs), except VC. The degradation of VC by KMnO 4 is a two-consecutive-step process. The second step, being the rate-limiting step, is of first order in VC and has an activation energy ( E a) of 7.9±1 kcal mol −1. The second order rate constants at 20°C are 0.035±0.004 M −1 s −1 (PCE), 0.80±0.12 M −1 s −1 (TCE), 1.52±0.05 M −1 s −1 ( cis-DCE), 2.1±0.2 M −1 s −1 (1,1-DCE) and 48.6±0.9 M −1 s −1 ( trans-DCE). The E a and entropy (Δ S ∗) of the reaction between KMnO 4 and CEs (except VC) are in the range of 5.8–9.3 kcal mol −1 and −33 to −36 kcal mol −1 K −1, respectively. Moreover, KMnO 4 is able to completely dechlorinate CEs, and the increase in acidity of the solution due to CE oxidation by KMnO 4 is directly proportional to the number of chlorine atoms in CEs.</description><identifier>ISSN: 0304-3894</identifier><identifier>EISSN: 1873-3336</identifier><identifier>DOI: 10.1016/S0304-3894(01)00241-2</identifier><identifier>PMID: 11566407</identifier><identifier>CODEN: JHMAD9</identifier><language>eng</language><publisher>Amsterdam: Elsevier B.V</publisher><subject>Activation energy ; Applied sciences ; Chemistry ; Decontamination. Miscellaneous ; Earth sciences ; Earth, ocean, space ; Engineering and environment geology. 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Experimental results have shown that the reaction appears to be second order overall and first order individually with respect to both KMnO 4 and all chlorinated ethenes (CEs), except VC. The degradation of VC by KMnO 4 is a two-consecutive-step process. The second step, being the rate-limiting step, is of first order in VC and has an activation energy ( E a) of 7.9±1 kcal mol −1. The second order rate constants at 20°C are 0.035±0.004 M −1 s −1 (PCE), 0.80±0.12 M −1 s −1 (TCE), 1.52±0.05 M −1 s −1 ( cis-DCE), 2.1±0.2 M −1 s −1 (1,1-DCE) and 48.6±0.9 M −1 s −1 ( trans-DCE). The E a and entropy (Δ S ∗) of the reaction between KMnO 4 and CEs (except VC) are in the range of 5.8–9.3 kcal mol −1 and −33 to −36 kcal mol −1 K −1, respectively. Moreover, KMnO 4 is able to completely dechlorinate CEs, and the increase in acidity of the solution due to CE oxidation by KMnO 4 is directly proportional to the number of chlorine atoms in CEs.</description><subject>Activation energy</subject><subject>Applied sciences</subject><subject>Chemistry</subject><subject>Decontamination. Miscellaneous</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Exact sciences and technology</subject><subject>Groundwaters</subject><subject>Hydrocarbons, Chlorinated - chemistry</subject><subject>Kinetics</subject><subject>Kinetics and mechanisms</subject><subject>Natural water pollution</subject><subject>Organic chemistry</subject><subject>Oxidation-Reduction</subject><subject>Perchloroethylene</subject><subject>Pollution</subject><subject>Pollution, environment geology</subject><subject>Potassium permanganate</subject><subject>Potassium Permanganate - chemistry</subject><subject>Reactivity and mechanisms</subject><subject>Soil and sediments pollution</subject><subject>Temperature</subject><subject>Trichloroethylene</subject><subject>Water treatment and pollution</subject><issn>0304-3894</issn><issn>1873-3336</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2001</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqF0M9vFCEUwHFiNHZb_RNqOJimPYzyBphle2lM01aTTXpQz-QNPFp0fqzAGPe_d7a7UW-eSODzgHwZOwXxDgQ07z8LKVQlzUqdC7gQolZQ1c_YAsxSVlLK5jlb_CFH7Djnb0IIWGr1kh0B6KZRYrlg6_tf0WOJ48DHwN1jN6Y4YCHPqTzSQJm3W74ZC-Ycp55vKPU4POCOXHLk3-NAJbrMc5n89hV7EbDL9PqwnrCvtzdfrj9W6_u7T9cf1pVTuimVAR28qylo1xiP0nsUAqmpTQ0kfKukAe8QHcB85GHeaEGjakMTdDAoT9jZ_t5NGn9MlIvtY3bUdTjQOGW7BFgpMKsZ6j10acw5UbCbFHtMWwvC7jLap4x218gKsE8ZbT3PvTk8MLU9-b9Th24zeHsAmB12IeHgYv7HSdDGzOxqz2iu8TNSstlFGhz5mMgV68f4n5_8BjRckDY</recordid><startdate>20011012</startdate><enddate>20011012</enddate><creator>Huang, Kun-Chang</creator><creator>Hoag, George E</creator><creator>Chheda, Pradeep</creator><creator>Woody, Bernard A</creator><creator>Dobbs, Gregory M</creator><general>Elsevier B.V</general><general>Elsevier</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope></search><sort><creationdate>20011012</creationdate><title>Oxidation of chlorinated ethenes by potassium permanganate: a kinetics study</title><author>Huang, Kun-Chang ; Hoag, George E ; Chheda, Pradeep ; Woody, Bernard A ; Dobbs, Gregory M</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c456t-815fdc2ef5c68da3dda00ae62821e0db4381dcaac11ddad1b43b15a4bf6f5f8a3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2001</creationdate><topic>Activation energy</topic><topic>Applied sciences</topic><topic>Chemistry</topic><topic>Decontamination. Miscellaneous</topic><topic>Earth sciences</topic><topic>Earth, ocean, space</topic><topic>Engineering and environment geology. Geothermics</topic><topic>Exact sciences and technology</topic><topic>Groundwaters</topic><topic>Hydrocarbons, Chlorinated - chemistry</topic><topic>Kinetics</topic><topic>Kinetics and mechanisms</topic><topic>Natural water pollution</topic><topic>Organic chemistry</topic><topic>Oxidation-Reduction</topic><topic>Perchloroethylene</topic><topic>Pollution</topic><topic>Pollution, environment geology</topic><topic>Potassium permanganate</topic><topic>Potassium Permanganate - chemistry</topic><topic>Reactivity and mechanisms</topic><topic>Soil and sediments pollution</topic><topic>Temperature</topic><topic>Trichloroethylene</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Huang, Kun-Chang</creatorcontrib><creatorcontrib>Hoag, George E</creatorcontrib><creatorcontrib>Chheda, Pradeep</creatorcontrib><creatorcontrib>Woody, Bernard A</creatorcontrib><creatorcontrib>Dobbs, Gregory M</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Journal of hazardous materials</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Huang, Kun-Chang</au><au>Hoag, George E</au><au>Chheda, Pradeep</au><au>Woody, Bernard A</au><au>Dobbs, Gregory M</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Oxidation of chlorinated ethenes by potassium permanganate: a kinetics study</atitle><jtitle>Journal of hazardous materials</jtitle><addtitle>J Hazard Mater</addtitle><date>2001-10-12</date><risdate>2001</risdate><volume>87</volume><issue>1</issue><spage>155</spage><epage>169</epage><pages>155-169</pages><issn>0304-3894</issn><eissn>1873-3336</eissn><coden>JHMAD9</coden><abstract>The kinetics of oxidation of perchloroethylene (PCE), trichloroethylene (TCE), three isomers of dichloroethylene (DCE) and vinyl chloride (VC) by potassium permanganate (KMnO 4) were studied in phosphate-buffered solutions of pH 7 and ionic strength ∼0.05 M and under isothermal, completely mixed and zero headspace conditions. Experimental results have shown that the reaction appears to be second order overall and first order individually with respect to both KMnO 4 and all chlorinated ethenes (CEs), except VC. The degradation of VC by KMnO 4 is a two-consecutive-step process. The second step, being the rate-limiting step, is of first order in VC and has an activation energy ( E a) of 7.9±1 kcal mol −1. The second order rate constants at 20°C are 0.035±0.004 M −1 s −1 (PCE), 0.80±0.12 M −1 s −1 (TCE), 1.52±0.05 M −1 s −1 ( cis-DCE), 2.1±0.2 M −1 s −1 (1,1-DCE) and 48.6±0.9 M −1 s −1 ( trans-DCE). The E a and entropy (Δ S ∗) of the reaction between KMnO 4 and CEs (except VC) are in the range of 5.8–9.3 kcal mol −1 and −33 to −36 kcal mol −1 K −1, respectively. Moreover, KMnO 4 is able to completely dechlorinate CEs, and the increase in acidity of the solution due to CE oxidation by KMnO 4 is directly proportional to the number of chlorine atoms in CEs.</abstract><cop>Amsterdam</cop><pub>Elsevier B.V</pub><pmid>11566407</pmid><doi>10.1016/S0304-3894(01)00241-2</doi><tpages>15</tpages></addata></record>
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subjects Activation energy
Applied sciences
Chemistry
Decontamination. Miscellaneous
Earth sciences
Earth, ocean, space
Engineering and environment geology. Geothermics
Exact sciences and technology
Groundwaters
Hydrocarbons, Chlorinated - chemistry
Kinetics
Kinetics and mechanisms
Natural water pollution
Organic chemistry
Oxidation-Reduction
Perchloroethylene
Pollution
Pollution, environment geology
Potassium permanganate
Potassium Permanganate - chemistry
Reactivity and mechanisms
Soil and sediments pollution
Temperature
Trichloroethylene
Water treatment and pollution
title Oxidation of chlorinated ethenes by potassium permanganate: a kinetics study
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