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首页> 外文期刊>Environmental Science & Technology >Kinetics and Mechanistic Aspects of As(lll)Oxidation by Aqueous Chlorine,Chloramines,and Ozone:Relevance to Drinking Water Treatment
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Kinetics and Mechanistic Aspects of As(lll)Oxidation by Aqueous Chlorine,Chloramines,and Ozone:Relevance to Drinking Water Treatment

机译:氯,氯胺和臭氧对As(III)氧化的动力学和力学方面:与饮用水处理的相关性

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摘要

Kinetics and mechanisms of As(lll)oxidation by free available chlorine (FAC-the sum of HOCl and OCl~(-1)),ozone (O_3),and monochloramine (NH_2CI)were investigated in buffered reagent solutions.Each reaction was found to befirstorderin oxidant and in As(lll),with 1:1 stoichiometry.FAC-As(lll)and O_3-As(III)reactions were extremely fast,with pH-dependent,apparent second-order rate constants,K"_app of 2.6 (+-0.1)x 10~5 M~(-1)s~(-1)and 1.5 (+-0.1)x 10~6 M~(-1)s~(-1)at pH 7,whereas the NH_2CI-As(lll)reaction was relatively slow (k"_(app) = 4.3 (+-1.7)x 10~(-1)M~(-1)s~(-1)at pH 7).Experiments conducted in real water samples spiked with 50 mu g/L As(III)(6.7 x 10~(-7)M)showed that a 0.1 mg/L Cl_2 (1.4 x 10~(-6)M)dose as FAC was sufficient to achieve depletion of As(III)to <1 mu g/L As(III)within 10 s of oxidant addition to waters containing negligible NH_3 concentrations and DOC concentrations <2 mg-C/L Even in a water containing 1 mg-N/L (7.1 x 10~(-5)M)as NH_3,>75% As(III)oxidation could be achieved within 10 s of dosing 1-2 mg/L Cl_2 (1.4-2.8 x 10~(-5)M)as FAC.As(III)residuals remaining in NH_3-containing waters 10 s after dosing FAC were slowly oxidized (f_1/_2 >= 4 h)in the presence of NH_2CI formed by the FAC-NH3 reaction.Ozonation was sufficient to yield >99% depletion of 50 mu g/L As(III)within 10 s of dosing 0.25 mg/L 0_3 (5.2 x 10(-6)M)to real waters containing <2 mg-C/L of DOC,while 0.8 mg/L O_3 (1.7 x 10~(-5)M)was sufficientfor a water containing 5.4 mg-C/L of DOC.NH_3 had negligible effect on the efficiency of As(III)oxidation by 0_3,due to the slow kinetics of the O_3-NH_3 reaction at circumneutral pH.Time-resolved measurements of As(III)loss during chlorinationdegradation in combination with low bioaccessibility of heavier PAHs is proposed to lead to a likely increase in concentration of heavier PAHs over time.These residues are,however,likely to be of low biological significance.
机译:在缓冲试剂溶液中研究了游离氯(FAC-HOCl和OCl〜(-1)之和),臭氧(O_3)和一氯胺(NH_2Cl)氧化As(III)的动力学和机理。在氧化剂和As(III)中是一阶的,化学计量比为1:1。FAC-As(III)和O_3-As(III)反应非常快,具有pH依赖性,表观二阶速率常数,K“ _app在pH 7时为2.6(+ -0.1)x 10〜5 M〜(-1)s〜(-1)和1.5(+ -0.1)x 10〜6 M〜(-1)s〜(-1) NH_2Cl-As(III)反应相对较慢(在pH 7时k“ _(app)= 4.3(+ -1.7)x 10〜(-1)M〜(-1)s〜(-1))。在掺有50μg / L As(III)(6.7 x 10〜(-7)M)的真实水样中进行的实验表明,0.1 mg / L Cl_2(1.4 x 10〜(-6)M)的FAC剂量为即使在含有1 mg-L的NH_3浓度和DOC浓度<2 mg-C / L的水中添加氧化剂,在10秒钟内足以将As(III)消耗至<1μg/ L As(III) N / L(7.1 x 10〜(-5)M)NH_3,> 75%As(III)氧化剂量为1-2 mg / L Cl_2(1.4-2.8 x 10〜(-5)M)的FAC剂量在10 s内达到.FAC剂量10 s后残留在NH_3水中的As(III)残留物被缓慢氧化(f_1 / _2> = 4 h)在FAC-NH3反应形成的NH_2Cl存在下进行臭氧处理,足以在0.25 mg / L 0_3的10 s内消耗> 99%的50μg/ L As(III)耗尽( DOC小于2 mg-C / L的真实水为5.2 x 10(-6)M),而5.4 mg-C / L的水为0.8 mg / L O_3(1.7 x 10〜(-5)M)就足够了DOC.NH_3的L对在0〜3的O_3-NH_3反应的动力学很慢,对As(III)氧化效率的影响可忽略不计。氯化物降解过程中As(III)损失的时间分辨测量与有人提出,较重的PAHs的生物利用度低会导致较重的PAHs的浓度随时间升高。这些残基可能具有较低的生物学意义。

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  • 来源
    《Environmental Science & Technology》 |2006年第10期|p.3285-3292|共8页
  • 作者单位

    Swiss Federal Institute of Aquatic Science and Technology (EAWAG),8600 Duebendorf,Switzerland,Center for Environmental Technology and Sustainable Development (CETASD),Hanoi University of Science,Nguyen Trai Street 334,Hanoi,Vietnam,and Laboratory of;

    Swiss Federal Institute of Aquatic Science and Technology (EAWAG),8600 Duebendorf,Switzerland,Center for Environmental Technology and Sustainable Development (CETASD),Hanoi University of Science,Nguyen Trai Street 334,Hanoi,Vietnam,and Laboratory of;

    Swiss Federal Institute of Aquatic Science and Technology (EAWAG),8600 Duebendorf,Switzerland,Center for Environmental Technology and Sustainable Development (CETASD),Hanoi University of Science,Nguyen Trai Street 334,Hanoi,Vietnam,and Laboratory of;

    Swiss Federal Institute of Aquatic Science and Technology (EAWAG),8600 Duebendorf,Switzerland,Center for Environmental Technology and Sustainable Development (CETASD),Hanoi University of Science,Nguyen Trai Street 334,Hanoi,Vietnam,and Laboratory of;

    Swiss Federal Institute of Aquatic Science and Technology (EAWAG),8600 Duebendorf,Switzerland,Center for Environmental Technology and Sustainable Development (CETASD),Hanoi University of Science,Nguyen Trai Street 334,Hanoi,Vietnam,and Laboratory of;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 环境化学;
  • 关键词

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