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Semiconducting mineral induced photochemical conversion of PAHs in aquatic environment: Mechanism study and fate prediction. | LitMetric

Semiconducting mineral induced photochemical conversion of PAHs in aquatic environment: Mechanism study and fate prediction.

Sci Total Environ

National Engineering Research Center of Industrial Wastewater Detoxication and Resource Recovery, East China University of Science and Technology, Shanghai 200237, China. Electronic address:

Published: February 2023

AI Article Synopsis

  • - The study investigates how semiconducting minerals, like iron sulfides, influence the breakdown of anthracene (a common pollutant) in freshwater and seawater when exposed to sunlight, revealing significant degradation mechanisms.
  • - Key findings indicate that natural pyrite enhances anthracene degradation through processes like photocatalytic degradation and the Fenton reaction, with different reactive intermediates contributing to the breakdown in freshwater vs. seawater.
  • - The research also highlights a proposed degradation pathway for anthracene, which includes toxicity assessments, suggesting that these minerals can impact the behavior and environmental risks of contaminants in aquatic ecosystems.

Article Abstract

Semiconducting minerals (such as iron sulfides) are highly abundant in surface water, but their influences on the natural photochemical process of contaminants are still unknown. By simulating the natural water environment under solar irradiation, this work comprehensively investigated the photochemical processes of anthracene (a typical Polycyclic Aromatic Hydrocarbons) in both freshwater and seawater. The results show that the natural pyrite (NP) significantly promotes the degradation of anthracene under solar illumination via 1) NP induced photocatalytic degradation of anthracene, and 2) Fenton reaction due to the NP induced photocatalytic generation of HO. The material characterization and theoretical calculation reveal that the natural impurity in NP enlarges its band gap, which limits the utilization of solar spectra to shorter wavelength. The contribution of generated reactive intermediates on anthracene degradation follows the order of O >OH > O in freshwater and O >O >OH in seawater. The photochemically generated HO is a vital source for OH generation (from Fenton reaction). The steady-state concentration of OH, O and O in freshwater were monitored as 3.0 × 10 M, 1.1 × 10 M, and 4.5 × 10 M, respectively. However, the OH concentration in seawater can be negligible due to the quenching effects by halides, and the O and O concentrations are higher than that in freshwater. An anthracene degradation kinetic model was built based on the experimentally determined reactive intermediates concentration and its second order rate constant with anthracene. Moreover, the anthracene degradation pathway was proposed based on intermediates analysis and DFT calculation, and its toxicity evolution during the photochemical process was assessed by quantitative structure-activity relationship (QSAR) based prediction. This finding suggests that the natural semiconducting minerals can affect the fate and environmental risks of contaminants in natural water.

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Source
http://dx.doi.org/10.1016/j.scitotenv.2022.160382DOI Listing

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