4.7 Article

Constant oxidation of atrazine in Fe(III)/PDS system by enhancing Fe(III)/Fe(II) cycle with quinones: Reaction mechanism, degradation pathway and DFT calculation

Journal

CHEMOSPHERE
Volume 317, Issue -, Pages -

Publisher

PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.chemosphere.2023.137883

Keywords

quinones; persulfate; Fe(II) regeneration; Fe(IV); DFT calculation; toxicity assessment

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Quinones such as methyl-p-benzoquinone (MBQ) are widely distributed potential pollutants in the environment. This study introduced MBQ into the Fe(III)/peroxydisulfate system (Fe(III)/PDS) to enhance the conversion of Fe(III) to Fe(II) and the degradation of atrazine (ATZ), establishing an environmentally friendly system for treating pollution. The MBQ/Fe(III)/PDS system showed better performance than the traditional Fe(II)/PDS system within a pH range of 2-7. Sulfate radical (SO4 center dot-) and hydroxyl radical ((OH)-O-center dot) were detected in the MBQ/Fe(III)/PDS system, indicating their involvement in the degradation process.
Quinones are potential pollutants and redox active compounds widely distributed in environmental media. In this study, methyl-p-benzoquinone (MBQ) was introduced into Fe(III)/peroxydisulfate system (Fe(III)/PDS) to expedite the conversion of Fe(III) to Fe(II) and the degradation of atrazine (ATZ), ultimately establishing an environmentally friendly system of treating pollution with pollution. MBQ/Fe(III)/PDS system showed superior performance to traditional Fe(II)/PDS system in pH range of 2-7. Sulfate radical (SO4 center dot-) and hydroxyl radical ((OH)-O-center dot) were confirmed to exist in MBQ/Fe(III)/PDS system according to alcohol quenching experiments and ESR tests. Meanwhile, stable 80% of eta[PMSO2] (i.e., the molar ratio of PMSO2 generation to PMSO consumption) was achieved and manifested that highly reactive substance Fe(IV) also participated in MBQ/Fe(III)/PDS system. The spontaneous transformation of MBQ and methyl-hydroquinone (MHQ) drove Fe(III)/Fe(II) cycle, during which MHQ induced Fe(III) reduction and Fe(II) regeneration. Transformation pathways of ATZ were proposed based on HPLC-MS detection and DFT calculation and ATZ degradation could be initiated by lateral chain oxidation and dechlorination-hydroxylation. The acute toxicity, bioaccumulation factor, developmental toxicity and mutagenicity of ATZ and its degradation intermediates were evaluated by Toxicity Estimation Software Tool, and the luminescent bacteria test was conducted to investigate the acute toxicity variation of the reaction solution. Cl obviously inhibited ATZ degradation and three main by-products generation, while humic acid (HA) had little effect on them probably due to the established balance between inhibition (some components in HA competed to consume reactive species) and acceleration (quinone units in HA also facilitated Fe(III)/Fe(II) cycle).

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