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Homogeneous Catalytic Oxidation for the Degradation of Chlorophenoxy Herbicides in Aqueous Media

机译:均相催化氧化降解水性介质中的氯苯氧基除草剂

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Chlorophenoxy herbicides, such as MCPA (4-chloro-2-methylphenoxyacetic acid) and 4-rnCPA (4-chlorophenoxyacetic acid), are employed on a large scale for weed control on cereal crops, grasslands, vines, peas, potatoes and forestry applications. Information on the chronic toxicity on humans due to their extensive and prolonged use in fields and transport into surface waters that are used for drinking purposes is not yet known. These compounds resist biodegradation and have potential toxicity towards humans and animals, being considered as moderately toxic (class Ⅱ or Ⅲ) by the World Health Organization. Their widespread use in industrialized and third-world countries for agricultural and non-agricultural purposes generates continuously rinsate, waste product and contaminated soil at hundreds of thousands of application sites. They are found as pollutants in natural waters, with contamination levels up to 10μg/l in ground and surface waters. In Cyprus, the constructed waters reservoirs constitute the main source of drinking water. In these surface waters a number of herbicides and pesticides have been traced during the current years. Therefore the objective of this research was to investigate the degradation potential or complete mineralization of such chlorinated aromatic compounds in water. Advanced oxidation processes (AOPs) are potentially useful for treating pesticide wastes because they generate hydroxyl radicals (OH), a powerful non-specific oxidant. The hydroxyl radical is able to react with organics yielding dehydrogenated or hydroxylated derivatives. The organic pollutants are oxidized by hydrogen radicals and mineralized to water, carbon dioxide and inorganic ions. Fenton's reagent is a mixture of hydrogen peroxide and ferrous ions which provides a source of hydroxyl radicals. The Fenton reaction has been widely applied in the treatment of non-biodegradable wastewater in the field of AOPs. Hydrogen peroxide is environmentally friendly and it is commonly used as a source of hydroxyl radicals in Fenton's process. The Fenton's process which was applied in this study included the use of ferrous-catalyzed H_2O_2 to provide an oxidizing environment. Batch experiments were performed in duplicate, using H_2O_2 (35% w/v), in the presence of Fe(Ⅱ) as a catalyst to determine the degradation of the herbicides. The Fenton's reaction takes place in pH values ranging between 3 - 3.5. In thesernpH values, the formation of the free hydroxyl radicals is activated. In addition, the low pH values minimize the possible self-decay of hydrogen peroxide and inhibit the formation and precipitation of insoluble ferric iron hydroxide, Fe(OH)_3. Solutions of known concentrations of MCPA, 4-CPA and a mixture of MCPA and 4-CPA were used and the corresponding TOC concentrations were measured in accordance with the Standard Methods. In particular, H_2O_2 was added in various dosages to known sample volumes with the addition of various dosages of Fe(Ⅱ) in order to select the optimum quantities of the reagents for the development of the method. Sixteen different combinations of dosages of oxidant and catalyst were used for each herbicide. The optimum molar ratios obtained were 26.45 [H_2O_2]/[Fe(Ⅱ)] for MCPA , 19.83 [H_2O_2]/[Fe(Ⅱ)] for 4-CPA and 39.64 [H_2O_2]/[Fe(Ⅱ)] for the mixture of the two herbicides. According to the above results, the MCPA and 4-CPA were not completely degraded by Fenton reaction since only 62% and 70% of the TOC was converted into carbon dioxide. The TOC removal achieved for the mixture of MCPA and 4-CPA was 48%. The remaining quantity of each herbicide is considered to be partially degraded to organic by-products. These findings are now used for further examination of the oxidation process and in specific, for the study of kinetics, the mechanisms of the individual reactions that take place as well as for the determination of the main by-products generated through the development of the overall Fenton reaction. In the complet
机译:氯苯氧基除草剂,例如MCPA(4-氯-2-甲基苯氧基乙酸)和4-rnCPA(4-氯苯氧基乙酸)被广泛用于杂草控制谷物作物,草原,葡萄藤,豌豆,马铃薯和林业的除草剂。由于其在田间广泛和长期使用以及运输到用于饮用目的的地表水中而对人类造成的慢性毒性的信息尚不清楚。这些化合物具有抗生物降解性,对人类和动物具有潜在的毒性,被世界卫生组织(WHO)视为中度毒性(Ⅱ级或Ⅲ级)。它们在工业化和第三世界国家中以农业和非农业目的广泛使用,在成千上万个施用地点不断产生冲洗液,废品和受污染的土壤。它们在天然水中被发现为污染物,在地下水和地表水中的污染水平高达10μg/ l。在塞浦路斯,人工水库是饮用水的主要来源。在这些地表水中,近年来已经发现了许多除草剂和农药。因此,本研究的目的是研究这种氯化芳族化合物在水中的降解潜力或完全矿化。先进的氧化过程(AOP)可能用于处理农药废物,因为它们会产生羟基自由基(OH),这是一种强大的非特异性氧化剂。羟基能够与有机物反应,生成脱氢或羟基化的衍生物。有机污染物被氢自由基氧化并矿化为水,二氧化碳和无机离子。 Fenton的试剂是过氧化氢和亚铁离子的混合物,可提供羟基自由基。 Fenton反应已被广泛应用于AOPs领域中不可生物降解废水的处理。过氧化氢对环境友好,在芬顿工艺中通常用作羟基自由基的来源。这项研究中采用的Fenton工艺包括使用铁催化的H_2O_2提供氧化环境。在Fe(Ⅱ)为催化剂的条件下,使用H_2O_2(35%w / v)进行一式两份的分批实验,以确定除草剂的降解。 Fenton反应在pH值介于3-3.5之间的范围内发生。在sernpH值中,游离羟基的形成被激活。此外,低pH值可最大程度地减少过氧化氢的可能自分解,并抑制不溶性氢氧化铁Fe(OH)_3的形成和沉淀。使用已知浓度的MCPA,4-CPA溶液以及MCPA和4-CPA的混合物,并根据标准方法测量相应的TOC浓度。特别是将H_2O_2以各种剂量添加到已知的样品体积中,并添加各种剂量的Fe(Ⅱ),以选择用于该方法开发的最佳试剂量。每种除草剂使用氧化剂和催化剂剂量的十六种不同组合。对于MCPA,最佳摩尔比为26.45 [H_2O_2] / [Fe(Ⅱ)],对于4-CPA为19.83 [H_2O_2] / [Fe(Ⅱ)],对于混合物,最佳摩尔比为39.64 [H_2O_2] / [Fe(Ⅱ)]两种除草剂中的一种。根据以上结果,由于只有62%和70%的TOC转化为二氧化碳,因此Fenton反应不会完全降解MCPA和4-CPA。 MCPA和4-CPA混合物的TOC去除率为48%。每种除草剂的剩余量被认为部分降解为有机副产物。这些发现现在可用于进一步检查氧化过程,特别是用于动力学研究,发生的各个反应机理以及确定通过整体反应过程产生的主要副产物的确定。芬顿反应。在完成

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  • 来源
  • 会议地点 Frankfurt(DE)
  • 作者单位

    Department of Civil and Environmental Engineering, School of Engineering, University of Cyprus, 75 Kallipoleos Str., 1678 Nicosia, Cyprus;

    School of Chemical Engineering, National Technical University of Athens, 15773, Zografou, Athens, Greece;

    Department of Civil and Environmental Engineering, School of Engineering, University of Cyprus, 75 Kallipoleos Str., 1678 Nicosia, Cyprus;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 水资源调2查与水利规划;
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