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Degradation mechanism of alachlor during direct ozonation and O-3/H2O2 advanced oxidation process

机译:直接臭氧化和O-3 / H2O2高级氧化过程中甲草胺的降解机理

摘要

The degradation of alachlor by direct ozonation and advanced oxidation process O-3/H2O2 was investigated in this study with focus on identification of degradation byproducts. The second-order reaction rate constant between ozone and alachlor was determined to be 2.5 +/- 0.1 M-1 s(-1) at pH 7.0 and 20 degrees C. Twelve and eight high-molecular-weight byproducts (with the benzene ring intact) from alachlor degradation were identified during direct ozonation and O-3/H2O2, respectively. The common degradation byproducts included N-(2,6-diethylphenyl)-methyleneamine, 8-ethyl-3,4-dihydro-quinoline, 8-ethyl-quinoline, 1-chloroacetyl-2-hydro-3-ketone-7-acetyl-indole, 2-chloro-2',6'-diacetyl-N-(methoxymethyl)acetanilide, 2-chloro-2'-acetyl-6'-ethyl-N-(methoxymethyl)-acetanilide, and two hydroxylated alachlor isomers. In direct ozonation, four more byproducts were also identified including 1-chloroacetyl-2,3-dihydro-7-ethyl-indole, 2-chloro-2',6'-ethyl-acetanilide, 2-chloro-2',6'-acetyl-acetanilide and 2-chloro-2'-ethyl-6'-acetyl-N-(methoxymethyl)-acetanilide. Degradation of alachlor by O-3 and O-3/H2O2 also led to the formation of low-molecular-weight byproducts including formic, acetic, propionic, monochloroacetic and oxalic acids as well as chloride ion (only detected in O-3/H2O2). Nitrite and nitrate formation was negligible. Alachlor degradation occurred via oxidation of the arylethyl group, N-dealkylation, cyclization and cleavage of benzene ring. After O-3 or O-3/H2O2 treatment. the toxicity of alachlor solution examined by the Daphnia magna bioassay was slightly reduced. (C) 2009 Elsevier Ltd. All rights reserved.
机译:本研究研究了直接臭氧化和高级氧化过程O-3 / H2O2降解甲草胺的方法,重点是鉴定降解副产物。在pH 7.0和20摄氏度下,臭氧与甲草胺之间的二级反应速率常数确定为2.5 +/- 0.1 M-1 s(-1)。十二和八种高分子量副产物(带有苯环完整)分别从甲草胺降解和O-3 / H2O2中鉴定出来。常见的降解副产物包括N-(2,6-二乙基苯基)-亚甲基胺,8-乙基-3,4-二氢喹啉,8-乙基喹啉,1-氯乙酰基-2-氢-3-酮-7-乙酰基-吲哚,2-氯-2',6'-二乙酰基-N-(甲氧基甲基)乙酰苯胺,2-氯-2'-乙酰基-6'-乙基-N-(甲氧基甲基)-乙酰苯胺和两种羟基化的甲草胺异构体。在直接臭氧化中,还鉴定出另外四种副产物,包括1-氯乙酰基-2,3-二氢-7-乙基吲哚,2-氯-2',6'-乙基乙酰苯胺,2-氯-2',6' -乙酰基-乙酰苯胺和2-氯-2'-乙基-6'-乙酰基-N-(甲氧基甲基)-乙酰苯胺。 O-3和O-3 / H2O2对甲草胺的降解还导致形成低分子量副产物,包括甲酸,乙酸,丙酸,一氯乙酸和草酸以及氯离子(仅在O-3 / H2O2中检测到) )。亚硝酸盐和硝酸盐的形成可以忽略不计。甲草胺的降解是通过芳基乙基的氧化,N-脱烷基化,环化和苯环的裂解而发生的。经过O-3或O-3 / H2O2处理。通过水蚤(Daphnia magna)生物测定法检测的甲草胺溶液的毒性略有降低。 (C)2009 Elsevier Ltd.保留所有权利。

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