Key Laboratory of Environmental Remediation and Ecological Health, Ministry of Industry and Information Technology, School of Environmental and Biological Engineering, Nanjing University of Science and Technology, Nanjing, 210094, China.
CAS Key Laboratory of Urban Pollutant Conversion, Department of Environmental Science and Engineering, University of Science and Technology of China, Hefei 230026, China.
Water Res. 2024 Sep 15;262:122090. doi: 10.1016/j.watres.2024.122090. Epub 2024 Jul 14.
Ammonia monooxygenase (AMO)-mediated cometabolism of organic pollutants has been widely observed in biological nitrogen removal process. However, its molecular mechanism remains unclear, hindering its practical application. Furthermore, conventional nitrification systems encounter significant challenges such as air pollution and the loss of ammonia-oxidizing bacteria, when dealing with wastewater containing volatile organic pollutants. This study developed a nitrifying membrane-aerated biofilm reactor (MABR) to enhance the biodegradation of volatile 4-chlorophenol (4-CP). Results showed that 4-CP was primarily removed via Nitrosomonas nitrosa-mediated cometabolism in the presence of NH-N, supported by the increased nicotinamide adenine dinucleotide (NADH) and adenosine triphosphate (ATP) content, AMO activity and the related genes abundance. Hydroquinone, detected for the first time and produced via oxidative dechlorination, as well as 4-chlorocatechol was primary transformation products of 4-CP. Nitrosomonas nitrosa AMO structural model was constructed for the first time using homology modeling. Molecular dynamics simulation suggested that the ortho-carbon in the benzene ring of 4-CP was more prone to metabolismcompared to the ipso-carbon. Density functional theory calculation revealed that 4-CP was metabolized by AMO via H-abstraction-OH-rebound reaction, with a significantly higher rebound barrier at the ipso-carbon (16.37 kcal·mol) as compared to the ortho-carbon (6.7 kcal·mol). This study fills the knowledge gap on the molecular mechanism of AMO-mediated cometabolism of organic pollutants, providing practical and theoretical foundations for improving volatile organic pollutants removal through nitrifying MABR.
氨单加氧酶(AMO)介导的有机污染物共代谢在生物脱氮过程中被广泛观察到。然而,其分子机制尚不清楚,阻碍了其实际应用。此外,传统的硝化系统在处理含有挥发性有机污染物的废水时,会遇到空气污染和氨氧化细菌损失等重大挑战。本研究开发了硝化膜曝气生物膜反应器(MABR)来增强挥发性 4-氯苯酚(4-CP)的生物降解。结果表明,在 NH-N 的存在下,通过 Nitrosomonas nitrosa 介导的共代谢主要去除 4-CP,这得到了烟酰胺腺嘌呤二核苷酸(NADH)和三磷酸腺苷(ATP)含量、AMO 活性和相关基因丰度增加的支持。氢醌,首次检测到并通过氧化脱氯产生,以及 4-氯邻苯二酚是 4-CP 的主要转化产物。首次使用同源建模构建了 Nitrosomonas nitrosa AMO 结构模型。分子动力学模拟表明,4-CP 苯环中的邻位碳原子比对位碳原子更容易代谢。密度泛函理论计算表明,4-CP 通过 AMO 经 H 提取-OH-回跳反应进行代谢,对位碳原子(16.37 kcal·mol)的回跳势垒明显高于邻位碳原子(6.7 kcal·mol)。本研究填补了 AMO 介导的有机污染物共代谢分子机制的知识空白,为通过硝化 MABR 提高挥发性有机污染物去除提供了实践和理论基础。