Literature DB >> 15926568

Formation of chloroform and chlorinated organics by free-chlorine-mediated oxidation of triclosan.

Krista L Rule1, Virginia R Ebbett, Peter J Vikesland.   

Abstract

The widely used antimicrobial agent triclosan (5-chloro-2-(2,4-dichlorophenoxy)phenol) readily reacts with free chlorine under drinking water treatment conditions. Overall second-order kinetics were observed, first-order in free chlorine and first-order in triclosan. Over the pH range of 4-11.5, the kinetics were pH sensitive as a result of the pH dependent speciation of both triclosan and free chlorine. Using a Marquardt-Levenberg routine, it was determined that this pH effect indicates that the dominant reaction in this system is between the ionized phenolate form of triclosan and hypochlorous acid (HOCl). The overall second-order rate coefficient was determined to be kArO- = 5.40 (+/- 1.82) x 10(3) M(-1) s(-1). Three chlorophenoxyphenols and two chlorophenols were identified by gas chromatographic-mass spectroscopic analysis. The chlorophenoxyphenol compounds include two monochlorinated triclosan derivatives (5,6-dichloro-2-(2,4-dichlorophenoy)phenol and 4,5-dichloro-2-(2,4-dichlorophenoxy)phenol) and one dichlorinated derivative (4,5,6-trichloro-(2,4-dichlorophenoxy)phenol); these species form via bimolecular electrophilic substitution of triclosan. 2,4-Dichlorophenol was detected under all reaction conditions and forms via ether cleavage of triclosan. In experiments with excess free chlorine, 2,4,6-trichlorophenol was formed via electrophilic substitution of 2,4-dichlorophenol. Chloroform formation was observed when an excess of free chlorine was present. A Hammett-type linear free-energy relationship (LFER) using Brown-Okamoto parameters (sigma+) was established to correlate the reactivity of HOCI and the phenolate forms of triclosan and other chlorophenols (log kArO- = -(10.7 +/- 2.2)Sigmasigma(+)o,m,p + 4.43). This LFER was used to obtain estimates of rate coefficients describing the reactivity of the intermediates 5,6-dichloro-2-(2,4-dichlorophenoy)phenol (kArO- approximately equal to 6 x 10(2)), 4,5-dichloro-2-(2,4-dichlorophenoxy)phenol (kArO- approximately equal to 3 x 10(2)), and 4,5,6-trichloro-(2,4-dichlorophenoxy)phenol (kArO- approximately equal to 4 x 10(1)).

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Year:  2005        PMID: 15926568     DOI: 10.1021/es048943+

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  18 in total

1.  Occurrence of triclosan in the tropical rivers receiving the effluents from the hospital wastewater treatment plant.

Authors:  Gordon C C Yang; Hsin-Jen Tsai; Fu-Kuei Chang
Journal:  Environ Monit Assess       Date:  2015-02-28       Impact factor: 2.513

2.  Deodorants--need for caution.

Authors:  K Peter Prasanth Kumar; Kala Ebenezer; Indira Agarwal
Journal:  Indian J Pediatr       Date:  2007-09       Impact factor: 1.967

3.  Degradation of triclosan in the presence of p-aminobenzoic acid under simulated sunlight irradiation.

Authors:  Pingping Zhai; Xuan Chen; Wenbo Dong; Hongjing Li; Jean-Marc Chovelon
Journal:  Environ Sci Pollut Res Int       Date:  2016-10-13       Impact factor: 4.223

Review 4.  Occurrence and toxicity of antimicrobial triclosan and by-products in the environment.

Authors:  Gilles Bedoux; Benoit Roig; Olivier Thomas; Virginie Dupont; Barbara Le Bot
Journal:  Environ Sci Pollut Res Int       Date:  2011-11-05       Impact factor: 4.223

Review 5.  Triclosan exposure, transformation, and human health effects.

Authors:  Lisa M Weatherly; Julie A Gosse
Journal:  J Toxicol Environ Health B Crit Rev       Date:  2017       Impact factor: 6.393

6.  Enhanced degradation of Orange G by permanganate with the employment of iron anode.

Authors:  Lingjun Bu; Zhou Shi; Shiqing Zhou
Journal:  Environ Sci Pollut Res Int       Date:  2016-10-10       Impact factor: 4.223

7.  Spectroscopic, kinetic and dosimetric features of the radical species produced after radiodegradation of solid triclosan.

Authors:  Ilknur Ozkirim Ustündağ; Mustafa Korkmaz
Journal:  Radiat Environ Biophys       Date:  2009-02-14       Impact factor: 1.925

8.  Selected chloro and bromo derivatives of triclosan--syntheses and their occurrence in Canadian sewage and biosolid samples.

Authors:  Hing-Biu Lee; Jagmohan Kohli; Thomas E Peart; Nien Nguyen
Journal:  Environ Sci Pollut Res Int       Date:  2013-06-14       Impact factor: 4.223

9.  Degradation behavior of triclosan by co-exposure to chlorine dioxide and UV irradiation: influencing factors and toxicity changes.

Authors:  Qing-Song Li; Hui-Wen Cai; Guo-Xin Li; Guo-Yuan Chen; Xiao-Yan Ma; Wen-Long He
Journal:  Environ Sci Pollut Res Int       Date:  2018-01-18       Impact factor: 4.223

10.  Effectiveness of zinc oxide-assisted photocatalysis for concerned constituents in reclaimed wastewater: 1,4-Dioxane, trihalomethanes, antibiotics, antibiotic resistant bacteria (ARB), and antibiotic resistance genes (ARGs).

Authors:  Myung Hwangbo; Everett Caleb Claycomb; Yina Liu; Theodore E G Alivio; Sarbajit Banerjee; Kung-Hui Chu
Journal:  Sci Total Environ       Date:  2018-08-27       Impact factor: 7.963

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