水中利谷隆氯化降解动力学和消毒副产物生成特性

Degradation Kinetics and Formation of Disinfection By-products During Linuron Chlorination in Drinking Water

采用常用消毒剂次氯酸钠对含氮除草剂利谷隆开展了氯化降解实验研究,系统考察了加氯量、p H值、加Br-量以及温度对降解效果的影响,分析了氯化反应过程中消毒副产物生成特性.结果表明,次氯酸钠对利谷隆的氧化降解过程符合二级反应动力学;p H值对该降解反应影响较大,当p H值为7时反应速率最快,其中HOCl、OCl-与利谷隆的基元反应速率常数分别为4.84×102L·(mol·h)-1和3.80×102L·(mol·h)-1.在添加溴离子时,反应速率随着溴离子的加入逐渐减小.改变温度时,反应速率随着温度的增加而逐渐增大.利谷隆在氯化降解过程中可产生三氯甲烷、二氯乙腈、三氯硝基甲烷、卤代丙酮等多类型消毒副产物.在不同p H值和添加溴离子条件下,消毒副产物种类与浓度会出现显著差异.

Chlorination degradation of linuron was studied using the common disinfectant sodium hypochlorite, the effects of chlorine dosage, pH value, bromine ion concentrationand temperature were systematically investigated, and the formation characteristics of disinfection by-products (DBPs) during the chlorination reaction was analyzed. The results showed that the chlorination degradation kinetics of linuron by sodium hypochlorite could be well described by the second-order kinetic model. Moreover, pH values had a great impact on the degradation reaction, and the rate constant reached the maximum level at pH 7, and the base elementary reaction rate constants of HOCl and OCl - with linuron were 4. 84 × 102 L?(mol?h) - 1 and 3. 80 × 102 L?(mol?h) - 1 , respectively. The reaction rate decreased with the addition of bromide ion and increased with increasing temperature. Furthermore, many kinds of disinfection by-products were produced during the chlorination degradation of linuron, including CF, DCAN, TCNM and halogen acetone. Under conditions of different solution pH and different bromide ion concentrations, there would be significant difference in the types and concentrations of disinfection by-products.