Departamento de Ingeniería Química y Química Física, Universidad de Extremadura, Avda. Elvas s/n, 06006, Badajoz, Spain; School of Architecture, Civil and Environmental Engineering (ENAC), Ecole Polytechnique Fédérale de Lausanne (EPFL), CH-1015, Lausanne, Switzerland.
School of Architecture, Civil and Environmental Engineering (ENAC), Ecole Polytechnique Fédérale de Lausanne (EPFL), CH-1015, Lausanne, Switzerland; Eawag, Swiss Federal Institute of Aquatic Science and Technology, CH-8600, Dübendorf, Switzerland; Swiss Federal Institute of Technology, Institute of Biogeochemistry and Pollutant Dynamics (IBP), Department of Environment Systems (D-USYS), ETH Zurich, Universitätsstrasse 16, CH-8092, Zürich, Switzerland.
Water Res. 2020 Jun 15;177:115691. doi: 10.1016/j.watres.2020.115691. Epub 2020 Mar 6.
The generation of hydroxyl radicals (OH) during the chlorination of air saturated solutions of different hydroxyphenols (hydroquinone, resorcinol, catechol, gallic and tannic acids) at pH 7 has been determined by the formation of phenol (in presence of benzene in excess) or 2-hydroxyterephthalic acid (in presence of terephthalic acid). Formation of OH was only detected during the chlorination of o- or p-hydroxyphenols, compounds that react with chlorine by electron transfer forming the corresponding semiquinones/quinones. In aerated solutions, oxygen is reduced by the semiquinone to the superoxide radical, O, which reacts with HOCl to OH. Compared to the studied o-hydroxyphenols, the lower reactivity of hydroquinone towards chlorine favours the reaction between chlorine and O, and its OH formation potential is ∼50 times higher. The extent of OH generated increased with the concentration of the hydroxyphenol and chlorine, but the OH yield (moles formed per mole of hydroxyphenol eliminated), decreased due to the formation of the quinone, that acts as O scavenger. The yield was almost not affected by the pH (6 ≤ pH ≤ 7.5), whereas a strong impact of dissolved O was observed. The OH production was null in absence of O and 2.5-3 times higher at oxygen saturated conditions compared to air-saturated. Contrary to chlorination, during bromination of hydroquinone OH was not formed, which can be attributable to a much faster consumption of the oxidant, with no chance for O to react with bromine. Formation of OH during the chlorination of different NOM extracts (SRHA, SRFA, PLFA and Nordic Lake NOM) and water from Lake Greifensee (Switzerland) was also studied using terephthalic acid as OH scavenger. For SRHA, SRFA and Nordic Lake NOM (all of allochthonous origin and presenting high electron-donating capacity, EDC), OH yields expressed as moles formed per mole of DOC (%), were between 1.1 and 2.0, similar to that of hydroquinone (∼1.5). For PLFA and Lake Greifensee water (autochthonous, lower EDC) much lower OH yields were observed (0.1-0.3). Both chlorination rate and EDC, the later favouring the formation/stabilization of O, seem to be key factors involved in OH generation during the chlorination of NOM. A mechanism for these findings is proposed based on kinetic simulations of hydroquinone chlorination at pH 7.
在 pH 值为 7 时,通过形成苯酚(在过量苯的存在下)或 2-羟基对苯二甲酸(在对苯二甲酸存在下),测定了不同羟基酚(对苯二酚、间苯二酚、邻苯二酚、没食子酸和鞣酸)在空气饱和溶液中氯化时生成的羟基自由基 (OH)。只有在 o-或 p-羟基酚的氯化过程中才检测到 OH 的形成,这些化合物通过电子转移与氯反应形成相应的半醌/醌。在充气溶液中,半醌将氧还原为超氧自由基 O,O 与 HOCl 反应生成 OH。与所研究的 o-羟基酚相比,对氯的低反应性有利于氯与 O 的反应,其 OH 生成势约高 50 倍。生成的 OH 量随羟基酚和氯的浓度增加而增加,但由于形成了作为 O 清除剂的醌,OH 的产率(每摩尔消除的羟基酚形成的摩尔数)降低。pH 值(6≤pH≤7.5)几乎没有影响,但观察到溶解氧的强烈影响。在没有 O 的情况下,OH 生成为零,而在氧气饱和条件下与空气饱和相比,OH 生成增加了 2.5-3 倍。与氯化相反,在对苯二酚的溴化过程中没有形成 OH,这可能归因于氧化剂的消耗速度更快,没有机会让 O 与溴反应。使用对苯二甲酸作为 OH 清除剂,还研究了不同 NOM 提取物(SRHA、SRFA、PLFA 和北欧湖 NOM)和瑞士 Greifensee 湖的水在氯化过程中的 OH 生成。对于 SRHA、SRFA 和北欧湖 NOM(均为异源来源,具有高电子供体能力 EDC),以每摩尔 DOC(%)形成的摩尔数表示的 OH 产率在 1.1 至 2.0 之间,与对苯二酚(~1.5)相似。对于 PLFA 和 Greifensee 湖的水(自生的,EDC 较低),观察到的 OH 产率要低得多(0.1-0.3)。氯化速率和 EDC,后者有利于 O 的形成/稳定,似乎是 NOM 氯化过程中生成 OH 的关键因素。基于 pH 值为 7 时对苯二酚氯化的动力学模拟,提出了一种对此类发现的解释机制。