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三氯生通过游离氯介导的氧化作用形成氯仿和氯化有机物。

Formation of chloroform and chlorinated organics by free-chlorine-mediated oxidation of triclosan.

作者信息

Rule Krista L, Ebbett Virginia R, Vikesland Peter J

机构信息

Department of Civil and Environmental Engineering, 418 Durham Hall, Virginia Polytechnic and State University, Blacksburg, Virginia 24060-0361, USA.

出版信息

Environ Sci Technol. 2005 May 1;39(9):3176-85. doi: 10.1021/es048943+.

Abstract

The widely used antimicrobial agent triclosan (5-chloro-2-(2,4-dichlorophenoxy)phenol) readily reacts with free chlorine under drinking water treatment conditions. Overall second-order kinetics were observed, first-order in free chlorine and first-order in triclosan. Over the pH range of 4-11.5, the kinetics were pH sensitive as a result of the pH dependent speciation of both triclosan and free chlorine. Using a Marquardt-Levenberg routine, it was determined that this pH effect indicates that the dominant reaction in this system is between the ionized phenolate form of triclosan and hypochlorous acid (HOCl). The overall second-order rate coefficient was determined to be kArO- = 5.40 (+/- 1.82) x 10(3) M(-1) s(-1). Three chlorophenoxyphenols and two chlorophenols were identified by gas chromatographic-mass spectroscopic analysis. The chlorophenoxyphenol compounds include two monochlorinated triclosan derivatives (5,6-dichloro-2-(2,4-dichlorophenoy)phenol and 4,5-dichloro-2-(2,4-dichlorophenoxy)phenol) and one dichlorinated derivative (4,5,6-trichloro-(2,4-dichlorophenoxy)phenol); these species form via bimolecular electrophilic substitution of triclosan. 2,4-Dichlorophenol was detected under all reaction conditions and forms via ether cleavage of triclosan. In experiments with excess free chlorine, 2,4,6-trichlorophenol was formed via electrophilic substitution of 2,4-dichlorophenol. Chloroform formation was observed when an excess of free chlorine was present. A Hammett-type linear free-energy relationship (LFER) using Brown-Okamoto parameters (sigma+) was established to correlate the reactivity of HOCI and the phenolate forms of triclosan and other chlorophenols (log kArO- = -(10.7 +/- 2.2)Sigmasigma(+)o,m,p + 4.43). This LFER was used to obtain estimates of rate coefficients describing the reactivity of the intermediates 5,6-dichloro-2-(2,4-dichlorophenoy)phenol (kArO- approximately equal to 6 x 10(2)), 4,5-dichloro-2-(2,4-dichlorophenoxy)phenol (kArO- approximately equal to 3 x 10(2)), and 4,5,6-trichloro-(2,4-dichlorophenoxy)phenol (kArO- approximately equal to 4 x 10(1)).

摘要

广泛使用的抗菌剂三氯生(5-氯-2-(2,4-二氯苯氧基)苯酚)在饮用水处理条件下很容易与游离氯发生反应。观察到该反应符合总二级动力学,即对游离氯为一级反应,对三氯生也为一级反应。在pH值4 - 11.5范围内,由于三氯生和游离氯的形态随pH值变化,该反应动力学对pH敏感。使用Marquardt-Levenberg程序确定,这种pH效应表明该体系中的主要反应是三氯生的离子化酚盐形式与次氯酸(HOCl)之间的反应。确定总二级反应速率系数为kArO- = 5.40(±1.82)×10³ M⁻¹ s⁻¹。通过气相色谱 - 质谱分析鉴定出三种氯苯氧基苯酚和两种氯酚。氯苯氧基苯酚化合物包括两种一氯代三氯生衍生物(5,6 - 二氯 - 2-(2,4 - 二氯苯甲酰基)苯酚和4,5 - 二氯 - 2-(2,4 - 二氯苯氧基)苯酚)和一种二氯代衍生物(4,5,6 - 三氯-(2,4 - 二氯苯氧基)苯酚);这些物质通过三氯生的双分子亲电取代形成。在所有反应条件下均检测到2,4 - 二氯苯酚,它通过三氯生的醚键断裂形成。在游离氯过量的实验中,2,4,6 - 三氯苯酚通过2,4 - 二氯苯酚的亲电取代形成。当存在过量游离氯时,观察到有氯仿生成。利用Brown-Okamoto参数(σ⁺)建立了Hammett型线性自由能关系(LFER),以关联HOCl与三氯生及其他氯酚的酚盐形式的反应活性(log kArO- = -(10.7 ± 2.2)σ⁺o,m,p + 4.43)。该LFER用于获得描述中间体反应活性的速率系数估计值,这些中间体包括5,6 - 二氯 - 2-(2,4 - 二氯苯甲酰基)苯酚(kArO-约等于6×l0²)、4,5 - 二氯 - 2-(2,4 - 二氯苯氧基)苯酚(kArO-约等于3×10²)和4,5,6 - 三氯-(2,4 - 二氯苯氧基)苯酚(kArO-约等于4×10¹)。

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