hplc - pda法检测美国东德克萨斯州某城市污水处理厂中卡马西平、双氯芬酸和酮洛芬的含量

K. K. Onchoke, Gary Lopez, Anthony M. Broom
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引用次数: 0

摘要

对水的再利用、再循环和回收的需求增加,提高了对污水处理厂设计的改进需求,以最大限度地减少或去除有毒污染物或其代谢物。本研究采用固相萃取(SPE)技术对废水样品中的卡马西平(CBZ)、双氯芬酸(DF)和酮洛芬(KT)三种常用药物进行分离。采用高效液相色谱-光电二极管阵列检测器(HPLC-PDA)方法对美国东德克萨斯州纳科多奇斯污水处理厂(NWWTP)各处理阶段(曝气、澄清池、原活性污泥(RAS)、氯接触室(CCC)和二氧化硫室)中的CBZ、DF和KT进行了检测。在RAS阶段浓度最高,其次是进水曝气阶段。CBZ、KT和DF的检测浓度分别为2.115 × 10−3 mg/L、8.95 × 10−4 mg/L和8.55 × 10−4 mg/L。药物总检测浓度最高的为卡马西平(1.285 ~ 2.117 μg/L)、双氯芬酸(0.600 ~ 0.865 μg/L)、酮洛芬(0.815 ~ 0.885 μg/L)。计算得到的各处理阶段的去除率依次为:CBZ: RAS > SO2 >澄清剂≈曝气> CCC;KT: RAS > SO2 >曝气> CCC >澄清器;DF: RAS≈曝气≈CCC >澄清剂> SO2。测定的去除率顺序为卡马西平(~ 39.2%)>双氯芬酸(~ 30.6%)>酮洛芬(~ 8.8%)。NWWTP中药物的去除效率可能受到人体的影响,通过活化废水处理过程的过渡,以及它们的代谢和/或被人类使用。图形抽象
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Detection of Carbamazepine, Diclofenac, and Ketoprofen via a SPE-HPLC-PDA Method in a Municipal Wastewater Treatment Plant in East Texas, USA
Abstract Increased demand for water reuse, recycling and reclamation heightens the need for improvements in the design of wastewater treatment plants that minimize or remove toxic pollutants or their metabolites. In this study, solid-phase extraction (SPE) technique utilizing C-18 cartridge was used for separation of three commonly used pharmaceuticals, namely, carbamazepine (CBZ), diclofenac (DF), and ketoprofen (KT) in wastewater samples. High performance liquid chromatography-photodiode array detector (HPLC-PDA) method was used for detection of CBZ, DF, and KT along the treatment stages (aeration, clarifier, raw activated sludge (RAS), chlorine contact chamber (CCC), and sulfur dioxide chamber) from Nacogdoches wastewater treatment plant (NWWTP), in East Texas, USA. Highest concentrations were found in the RAS followed by influent aeration stage. Pharmaceutical concentrations detected from the influent or RAS samples were 2.115 × 10−3 mg/L, 8.95 × 10−4 mg/L and 8.55 × 10−4 mg/L for CBZ, KT and DF, respectively. Highest detected total concentrations of pharmaceuticals were: carbamazepine (1.285 – 2.117 μg/L), diclofenac (0.600 – 0.865 μg/L), and ketoprofen (0.815 – 0.885 μg/L). The calculated % removal efficiencies along the treatment stages follow the order; CBZ: RAS > SO2 > clarifier ≈ aeration > CCC; KT: RAS > SO2 > aeration > CCC > clarifier; DF: RAS ≈ aeration ≈ CCC > clarifier > SO2. Determined removal efficiencies follow the order carbamazepine (∼ 39.2%) > diclofenac (∼ 30.6%) > ketoprofen (∼8.8%). Removal efficiencies of pharmaceuticals in the NWWTP may be affected by the human body, transition through activated wastewater treatment processes, and their metabolism and/or usage by humans. GRAPHICAL ABSTRACT
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