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- In relation to this article, we declare that there is no conflict of interest.
- Publication history
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Received November 22, 2022
Revised February 11, 2023
Accepted February 27, 2023
- Acknowledgements
- This research was financially supported by Environmental and Occupational Hazards Control Research Center, Shahid Beheshti University of Medical Sciences, under grant No. 22038
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Enhanced degradation of 2,4-dichlorphenoxyacetic acid herbicide by CaO2 activated by Fe(II) and ultrasound irradiation: Practical insight and mineralization
Akbar Eslami1 2†
Akbar Eslami2
Hajar Sharifi Maleksari2
Gamze Varank3
Seyed Mehdi Ghasemi4
Parisa Nejatian5
Amin Bagheri2
Soheila Madihi-Bidgoli6†
1Environmental and Occupational Hazards Control Research Center, Shahid Beheshti University of Medical Sciences, Tehran, Iran 2Department of Environmental Health Engineering, School of Public Health and Safety, Shahid Beheshti University of Medical Sciences, Tehran, Iran 3Yildiz Technical University, Faculty of Civil Engineering, Department of Environmental Engineering, 34220 Istanbul, Turkey 4Deputy of Health, Babol University of Medical Sciences, Babol, Iran 5Deparment of Agricultral Extension and Education, Bu-Ali Sina University, Hamedan, Iran 6Research Center for Environmental Contaminants (RCEC), Abadan University of Medical Sciences, Abadan, Iran
akbar_eslami@yahoo.com, S.madihi8@gmail.com
Korean Journal of Chemical Engineering, December 2023, 40(12), 2866-2875(10), 10.1007/s11814-023-1405-3
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Abstract
CaO2 was activated by Fe(II) and ultrasound (US) irradiation to degrade 2,4-dichlorphenoxyacetic acid (2,4-
D) for the first time. Among transition metals (Fe, Cu, Mn and Co), Fe(II) had the best performance for the activation of
CaO2. The impact of pH, CaO2 and Fe(II) concentration was studied, and under optimal situation ~91% of 2,4-D was
degraded during 60 min reaction time. The quenching experiments showed that the hydroxyl radical was the main factor for the destruction of 2,4-D while superoxide anions had a minor role. The bicarbonate ions and acid humic exhibited a strong inhibitory effect on the performance of CaO2/US/Fe(II) process. Carbon and chlorine mineralization of 2,4-
D degradation was investigated; around 41% of C and 35% of Cl were mineralized during 60 min reaction time. The
function of CaO2/US/Fe(II) process was studied on real drainage and other organic pollutants, and the results showed
that the CaO2/US/Fe(II) process can be practical for water treatment. Finally, intermediates of 2,4-D degradation were
identified, a pathway was proposed, and the toxicity of intermediates was assessed by ECOSAR software.
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3. N. Jaafarzadeh and G. Barzegar, Process Saf. Environ. Prot., 111,520 (2017).
4. J. Zuo, B. Wang, J. Kang, P. Yan, J. Shen, S. Wang, D. Fu, X. Zhu, T.She, S. Zhao and Z. Chen, Sep. Purif. Technol., 297, 121459 (2022).
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21. A. Hassani, J. Scaria, F. Ghanbari and P. V. Nidheesh, Environ. Res.,217, 114789 (2023).
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45. Y. Zhong, K. Shih, Z. Diao, G. Song, M. Su, L. a. Hou, D. Chen and L. Kong, Chem. Eng. J., 417, 129225 (2021).
