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芬顿试剂氧化苯酚的化学途径及动力学

Chemical pathway and kinetics of phenol oxidation by Fenton's reagent.

作者信息

Zazo J A, Casas J A, Mohedano A F, Gilarranz M A, Rodríguez J J

机构信息

Ingeniería Química, Universidad Autónoma de Madrid, Spain.

出版信息

Environ Sci Technol. 2005 Dec 1;39(23):9295-302. doi: 10.1021/es050452h.

Abstract

Phenol oxidation by Fenton's reagent (H2O2 + Fe2+) in aqueous solution has been studied in depth for the purpose of learning more about the reactions involved and the extent of the oxidation process, under various operating conditions. An initial phenol concentration of 100 mg/L was used as representative of a phenolic industrial wastewater. Working temperatures of 25 and 50 degrees C were tested, and the initial pH was set at 3. The H2O2 and the Fe2+ doses were varied in the range of 500-5000 and 1-100 mg/L, respectively, corresponding to 1-10 times the stoichiometric ratio. A series of intermediates were identified, corresponding mainly to ring compounds and short-chain organic acids. Most significant among the former were catechol, hydroquinone, and p-benzoquinone; the main organic acids were maleic, acetic, oxalic, and formic, with substantially lower amounts of muconic, fumaric, and malonic acids. Under milder operating conditions (H2O2 and Fe2+ at lower concentrations), a great difference was found between the measured total organic carbon (TOC) and the amount of carbon in all analyzed species in the reaction medium. This difference decreased as the doses of H2O2 and Fe2+ increased, indicating that the unidentified compounds must correspond to oxidation intermediates between phenol and the organic acids. To establish a complete oxidation pathway, experiments were carried out using each of the identified intermediates as starting compounds. Dihydroxybenzenes were identified in the earlier oxidation stages. Muconic acid was detected in catechol but not in the hydroquinone and p-benzoquinone oxidation runs; the last two compounds were oxidized to maleic acid. Oxalic and acetic acid appeared to be fairly refractory to this oxidation treatment. A detailed knowledge of the time evolution of the oxidation intermediates is of environmental interest particularly in the case of hydroquinone and p-benzoquinone because their toxicities are several orders of magnitudes higher than that of phenol itself. The time evolution of the intermediates and TOC was fitted to a simple second-order kinetic equation, and the values of the kinetic constants were determined. This provides a simplified approach useful for design purposes.

摘要

为了更深入了解水溶液中芬顿试剂(H₂O₂ + Fe²⁺)氧化苯酚所涉及的反应以及氧化过程的程度,在各种操作条件下对此进行了深入研究。初始苯酚浓度为100 mg/L,用作酚类工业废水的代表。测试了25℃和50℃的工作温度,初始pH值设定为3。H₂O₂和Fe²⁺的剂量分别在500 - 5000 mg/L和1 - 100 mg/L范围内变化,分别对应化学计量比的1 - 10倍。鉴定出了一系列中间体,主要对应于环状化合物和短链有机酸。前者中最主要的是邻苯二酚、对苯二酚和对苯醌;主要的有机酸是马来酸、乙酸、草酸和甲酸,粘康酸、富马酸和丙二酸的含量则低得多。在较温和的操作条件下(H₂O₂和Fe²⁺浓度较低),发现反应介质中测得的总有机碳(TOC)与所有分析物种中的碳含量之间存在很大差异。随着H₂O₂和Fe²⁺剂量的增加,这种差异减小,表明未鉴定的化合物必定对应于苯酚和有机酸之间的氧化中间体。为了建立完整的氧化途径,使用每种鉴定出的中间体作为起始化合物进行了实验。在早期氧化阶段鉴定出了二羟基苯。在邻苯二酚氧化过程中检测到了粘康酸,但在对苯二酚和对苯醌氧化过程中未检测到;后两种化合物被氧化为马来酸。草酸和乙酸似乎对这种氧化处理相当耐受。氧化中间体随时间演变的详细知识具有环境意义,特别是对于对苯二酚和对苯醌而言,因为它们的毒性比苯酚本身高出几个数量级。中间体和TOC随时间的演变拟合为一个简单的二级动力学方程,并确定了动力学常数的值。这提供了一种对设计目的有用的简化方法。

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