Department of Chemistry and Institute for Coatings and Surface Chemistry, Niederrhein University of Applied Sciences, Adlerstr. 32, 47798, Krefeld, Germany; Institute of Physical Chemistry and CENIDE (Center for Nanointegration), University Duisburg-Essen, Universitätsstraße 5, 45141, Essen, Germany.
Department of Chemistry and Institute for Coatings and Surface Chemistry, Niederrhein University of Applied Sciences, Adlerstr. 32, 47798, Krefeld, Germany.
Chemosphere. 2024 Jun;358:142112. doi: 10.1016/j.chemosphere.2024.142112. Epub 2024 Apr 25.
The treatment of waterborne micropollutants, such as diclofenac, presents a significant challenge to wastewater treatment plants due to their incomplete removal by conventional methods. Ozonation is an effective technique for the degradation of micropollutants. However, incomplete oxidation can lead to the formation of ecotoxic by-products that require a subsequent post-treatment step. In this study, we analyze the susceptibility of micropollutant ozonation products to enzymatic digestion with laccase from Trametes versicolor to evaluate the potential of enzymatic treatment as a post-ozonation step. The omnipresent micropollutant diclofenac is used as an example, and the enzymatic degradation kinetics of all 14 detected ozonation products are analyzed by high-performance liquid chromatography coupled with high-resolution mass spectrometry (HPLC-HRMS) and tandem mass spectrometry (MS). The analysis shows that most of the ozonation products are responsive to chemo-enzymatic treatment but show considerable variation in enzymatic degradation kinetics and efficiencies. Mechanistic investigation of representative transformation products reveals that the hydroxylated aromatic nature of the ozonation products matches the substrate spectrum, facilitating their rapid recognition as substrates by laccase. However, after initiation by laccase, the subsequent chemical pathway of the enzymatically formed radicals determines the global degradability observed in the enzymatic process. Substrates capable of forming stable molecular oxidation products inhibit complete detoxification by oligomerization. This emphasizes that it is not the enzymatic uptake of the substrates but the channelling of the reaction of the substrate radicals towards the oligomerization of the substrate radicals that is the key step in the further development of an enzymatic treatment step for wastewater applications.
水中的微量污染物(如双氯芬酸)的处理对废水处理厂来说是一项重大挑战,因为传统方法无法完全去除这些污染物。臭氧氧化是一种降解微量污染物的有效技术。然而,不完全氧化会导致形成生态毒性的副产物,需要后续的后处理步骤。在这项研究中,我们分析了微量污染物臭氧氧化产物对漆酶(来自变色栓菌)的酶促消化的敏感性,以评估酶处理作为后臭氧氧化步骤的潜力。以普遍存在的微量污染物双氯芬酸为例,通过高效液相色谱-高分辨率质谱联用(HPLC-HRMS)和串联质谱(MS)分析了所有 14 种检测到的臭氧氧化产物的酶促降解动力学。分析表明,大多数臭氧氧化产物对化学-酶处理有反应,但在酶降解动力学和效率方面存在很大差异。对代表性转化产物的机理研究表明,臭氧氧化产物的芳香族羟基化性质与底物谱相匹配,有利于漆酶快速识别它们作为底物。然而,在漆酶引发之后,酶形成的自由基的后续化学途径决定了在酶过程中观察到的整体可降解性。能够形成稳定分子氧化产物的底物通过聚合抑制完全解毒。这强调了不是酶对底物的摄取,而是底物自由基的反应途径朝着底物自由基的聚合方向发展,这是在废水应用中进一步开发酶处理步骤的关键步骤。