Dark transformation from 17β-estradiol to estrone initiated by hydroxyl radical in dissolved organic matter

The occurrence and fate of 17 beta-estradiol (E2) in natural water have gained extensive attention owing to its high ecotoxic risk to wildlife. Dissolved organic matter (DOM) is a ubiquitous water constituent and contributes significantly to E-2 removal, although the reaction mechanism is rarely clarified. The present study aims to investigate E-2 transformation in water containing fresh or aged DOM surrogates at environmentally relevant concentrations in the dark. Experiments along with radical probes of benzene and furfuryl alcohol reveal that reactive radicals, particularly hydroxyl radical (.OH), formed non-photochemically at higher concentrations in aged DOM than in fresh DOM. The contribution of .OH in E-2 removal is indicated by the decreases in the removal of radical probes in the presence of E-2; moreover, E-2 removal is inhibited in the presence of radical scavengers. The dose-dependent inhibitive effect of substrate concentrations, including E-2 and coexistent propylparaben, shows that the radical concentration is a limiting factor for E-2 removal, which could be enhanced by increasing DOM concentration, dissolved oxygen, and light supply. As the main byproduct, estrone (E-1) is persistent in the current DOM water in the dark, but it can be easily photodegraded when exposed to light. Theoretical analysis reveals that the initial step is .OH-initiated H- abstraction on the hydroxyl group in the cyclopentane ring of E-2. The formed singlet excited state of E-2 undergoes further intramolecular rearrangement and oxidative dehydro-genation to generate E-1 and the hydroperoxy radical (.HO2). Considering the universal occurrence of E-2 in DOM-rich aquatic matrices, the present findings have special implications for the biogeochemical cycle and risk assessment of this pollutant in natural aquatic environments, particularly those beyond the photic zone.

Automated summary

This study aims to investigate the transformation of E2 in water containing fresh or aged DOM surrogates. The results showed that aged DOM produced higher concentrations of hydroxyl radicals, which contributed to the removal of E2. Additionally, the removal of E2 was enhanced by increasing DOM concentration, dissolved oxygen, and light supply. These findings have important implications for understanding the biogeochemical cycle and risk assessment of E2 in natural aquatic environments.