PAHs pollution is a widespread pollution in river basins and wetland water bodies. A Northeast China chemical industry zone was studied, focusing on reclaimed water and sludge from sewage treatment plants. The pollution levels of 16 polycyclic aromatic hydrocarbons (PAHs) were monitored across three water periods. A model comparing pollution levels with sludge and recycled water aroma indices was established and validated. The model revealed interaction relationships among the 16 PAH pollutants. Analysis of bacterial communities identified the mechanism for combined phenanthrene and pyrene degradation, along with nine key enzymes involved. Population responses to 16 PAH pollution stress were explored, highlighting metabolic differences and functional relationships within eukaryotic and prokaryotic microbial communities. Molecular dynamics simulations identified a key enzyme, uncovering pi–pi T-shaped and pi–alkyl forces in the interaction between pyrene dioxygenase and pyrene.
{"title":"Target Fishing and Molecular Docking for Phenanthrene–pyrene Co-degradation of the Niche Effect of Polycyclic Aromatic Hydrocarbons in Reclaimed Water","authors":"Caiyun Sun, Chunlei Xu, Yu Xia, Mengyuan An, Dazhi Sun, Lili Ma, Shixu Zhang, Yue Ma, Yuhan Zhou, Zihan Hao, Liang Xu","doi":"10.1007/s11270-025-07802-9","DOIUrl":"10.1007/s11270-025-07802-9","url":null,"abstract":"<div><p>PAHs pollution is a widespread pollution in river basins and wetland water bodies. A Northeast China chemical industry zone was studied, focusing on reclaimed water and sludge from sewage treatment plants. The pollution levels of 16 polycyclic aromatic hydrocarbons (PAHs) were monitored across three water periods. A model comparing pollution levels with sludge and recycled water aroma indices was established and validated. The model revealed interaction relationships among the 16 PAH pollutants. Analysis of bacterial communities identified the mechanism for combined phenanthrene and pyrene degradation, along with nine key enzymes involved. Population responses to 16 PAH pollution stress were explored, highlighting metabolic differences and functional relationships within eukaryotic and prokaryotic microbial communities. Molecular dynamics simulations identified a key enzyme, uncovering pi–pi T-shaped and pi–alkyl forces in the interaction between pyrene dioxygenase and pyrene.</p></div>","PeriodicalId":808,"journal":{"name":"Water, Air, & Soil Pollution","volume":"236 3","pages":""},"PeriodicalIF":3.8,"publicationDate":"2025-03-04","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":null,"resultStr":null,"platform":"Semanticscholar","paperid":"143533003","PeriodicalName":null,"FirstCategoryId":null,"ListUrlMain":null,"RegionNum":4,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":"","EPubDate":null,"PubModel":null,"JCR":null,"JCRName":null,"Score":null,"Total":0}
Pub Date : 2025-03-04DOI: 10.1007/s11270-025-07822-5
Bishwatma Biswas, Sudha Goel
The removal of pesticides from water sources is critically important for safe and clean drinking water. We investigated atrazine (ATZ) removal from various natural water sources using electrooxidation (EO) to cater to the need for safe drinking water. Under optimum operating conditions, 99% ATZ and ~ 70% TOC removal was achieved in 120 min of electrolysis time. Radical scavenging study and Electron Spin Paramagnetic Resonance (EPR) test showed that OH radicals and singlet oxygen were primarily responsible for the ATZ removal. ATZ removal was studied using synthetic water, filtered water, and river water, and the highest removal efficiencies observed were 98.30 ± 1.02%, 84.57 ± 1.18%, and 72.51 ± 1.34%, respectively. The phytotoxicity of EO-treated water was assessed using Vigna radiata seeds. The seed germination percentages observed at 0, 30, 90, and 120 min of EO treatment were 30, 50, 70, and 90%, respectively, compared to 100% obtained in the control (i.e., water without ATZ). Using solar energy as a power source instead of DC power reduced the total cost of the EO process by 12.78%. The EO process can effectively treat contaminated water, aiming to improve water quality and contributing to achieve sustainable development goals.