Degradation of biotansformation products of nonylphenol ethoxylates by ozonation and UV/TiO2 treatment

The degradation kinetics of biotransformation products of nonylphenol polyethoxylates (NPEOs), nonylphenol (NP), nonylphenol monoethoxylate (NP1EO) and nonylphenoxy carboxylic acid (NP1EC), by ozonation and UV/TiO2 (ultraviolet photocatalytic degradation in the presence of titanium dioxide suspensio...

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Détails bibliographiques
Publié dans:Water science and technology : a journal of the International Association on Water Pollution Research. - 1986. - 46(2002), 11-12 vom: 01., Seite 127-32
Auteur principal: Ike, M (Auteur)
Autres auteurs: Asano, M, Belkada, F D, Tsunoi, S, Tanaka, M, Fujita, M
Format: Article
Langue:English
Publié: 2002
Accès à la collection:Water science and technology : a journal of the International Association on Water Pollution Research
Sujets:Journal Article Coloring Agents Ethylene Glycols Oxidants, Photochemical Phenols titanium dioxide 15FIX9V2JP terics 27986-36-3 Ozone plus... 66H7ZZK23N nonylphenol 79F6A2ILP5 Titanium D1JT611TNE
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245 1 0 |a Degradation of biotansformation products of nonylphenol ethoxylates by ozonation and UV/TiO2 treatment 
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520 |a The degradation kinetics of biotransformation products of nonylphenol polyethoxylates (NPEOs), nonylphenol (NP), nonylphenol monoethoxylate (NP1EO) and nonylphenoxy carboxylic acid (NP1EC), by ozonation and UV/TiO2 (ultraviolet photocatalytic degradation in the presence of titanium dioxide suspension as a catalyst) were investigated using lab-scale reactors. The degradation rate of NP by UV/TiO2 was the highest among the tested NPEOs metabolites, while NP1EC showed the lowest degradation rate. In contrast, ozonation was especially effective for the breakdown of NP1EC. NP could be also degrade efficiently by ozonation, however, it was much less effective for NP1EO decomposition. Degradation of NP by both chemical oxidation processes followed first-order kinetics. The degradation curves of NP1EO and NP1EC could be approximately described by first-order kinetics also, although the degradation of NP1EC by ozonation seemed to follow a second-order kinetic 
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650 7 |a Ethylene Glycols  |2 NLM 
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700 1 |a Asano, M  |e verfasserin  |4 aut 
700 1 |a Belkada, F D  |e verfasserin  |4 aut 
700 1 |a Tsunoi, S  |e verfasserin  |4 aut 
700 1 |a Tanaka, M  |e verfasserin  |4 aut 
700 1 |a Fujita, M  |e verfasserin  |4 aut 
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