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影响水介质中磺胺甲恶唑超声降解的因素。

Factors affecting sonolytic degradation of sulfamethazine in water.

机构信息

State Key Laboratory of Pollution Control and Resources Reuse, Ministry of Education, College of Environmental Science and Engineering, Tongji University, Shanghai 200092, PR China.

出版信息

Ultrason Sonochem. 2013 Nov;20(6):1401-7. doi: 10.1016/j.ultsonch.2013.04.007. Epub 2013 Apr 28.

Abstract

In this study, the major factors affecting sonolytic degradation of sulfamethazine (SMT), a typical pharmaceutically active compound, in water were evaluated. The factors tested included two operational parameters (i.e. initial SMT concentration and ultrasonic power), three dissolved gases (i.e. Ar, O2 and N2), five most frequently found anions in water (NO3(-),Cl(-),SO4(2-),HCO3(-)andBr(-)), ferrous ion (Fe(2+)), and four alcohols (methanol, ethanol, isopropyl alcohol, tert-butyl alcohol). Typically, the degradation rate was increased with the increasing initial SMT concentration and power. The degradation rate was accelerated in the presence of argon or oxygen, but inhibited by nitrogen. Effects of anions on the ultrasonic treatment were species-dependent. The SMT degradation rate was slightly inhibited by NO3(-),Cl(-),and,SO4(2-) but significantly improved by HCO3(-)andBr(-). The negative effects of alcohols acted as hydroxyl radicals scavengers with the following order: tert-butyl alcohol>isopropyl alcohol>ethanol>methanol. The synergetic effect of ferrous ion was mainly due to production of additional hydroxyl radicals (·OH) through Fenton chemistry. LC/MS/MS analysis indicated that the degradation of SMT by ultrasonic irradiation is mainly ascribed to ·OH oxidation. Of interest, although the SMT could be rapidly degraded by ultrasonic irradiation, the degradation products were rarely mineralized. For example, ~100% of 180 μM SMT was decomposed, but only 8.31% TOC was reduced, within 2h at an irradiation frequency of 800 kHz and a power of 100 W. However, the products became much biodegradable (BOD5/COD was increased from 0.04 to 0.45). Therefore, an aerobic biological treatment may be an appropriate post-treatment to further decompose the SMT degradation products.

摘要

在这项研究中,评估了影响水中磺胺甲噁唑(SMT)超声降解的主要因素。测试的因素包括两个操作参数(即初始 SMT 浓度和超声功率)、三种溶解气体(即 Ar、O2 和 N2)、水中最常见的五种阴离子(NO3(-)、Cl(-)、SO4(2-)、HCO3(-)和 Br(-))、亚铁离子(Fe(2+))和四种醇(甲醇、乙醇、异丙醇、叔丁醇)。通常,随着初始 SMT 浓度和功率的增加,降解速率也会增加。在氩气或氧气存在下,降解速率会加快,但氮气会抑制降解速率。阴离子对超声处理的影响取决于物质种类。NO3(-)、Cl(-)和 SO4(2-)对 SMT 降解的抑制作用较小,但 HCO3(-)和 Br(-)对其降解有明显促进作用。醇类的负面影响表现为作为羟基自由基清除剂,其顺序为:叔丁醇>异丙醇>乙醇>甲醇。亚铁离子的协同作用主要是由于芬顿化学产生了额外的羟基自由基(·OH)。LC/MS/MS 分析表明,超声辐照下 SMT 的降解主要归因于·OH 氧化。有趣的是,尽管 SMT 可以被超声辐照快速降解,但降解产物很少被矿化。例如,在 800 kHz 辐照频率和 100 W 功率下,180 μM SMT 在 2 小时内迅速分解,但仅减少了 8.31% 的 TOC。然而,产物变得更容易生物降解(BOD5/COD 从 0.04 增加到 0.45)。因此,有氧生物处理可能是进一步分解 SMT 降解产物的合适后处理方法。

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