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Simultaneous Cr (Vi) Reduction and Diazinon Oxidation With Organometallic Sludge Formation Under Photolysis: Kinetics, Degradation Pathways, and Mechanism Publisher Pubmed



Karimi P1 ; Azarpira H2 ; Rasolevandi T3 ; Sarkhosh M4, 5, 6 ; Azizi S5, 6 ; Mohseni SM1, 7 ; Sadani M7
Authors
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Authors Affiliations
  1. 1. Student Research Committee, School of Public Health and Safety, Shahid Beheshti University of Medical Sciences, Tehran, Iran
  2. 2. Environmental Health Engineering Department, Social Determinants of Health Research Center, Saveh University of Medical Sciences, Saveh, Iran
  3. 3. Environmental Health Engineering Department, School of Public Health, Tehran University of Medical Sciences, Tehran, Iran
  4. 4. Environmental Health Engineering Department, School of Public Health, Mashhad University of Medical Sciences, Mashhad, Iran
  5. 5. UNESCO�UNISA Africa Chair in Nanosciences and Nanotechnology, College of Graduate Studies, University of South Africa, Muckleneuk Ridge, PO Box 392, Pretoria, 0002, South Africa
  6. 6. Nanosciences African Network (NANOAFNET), iThemba LABS-National Research Foundation, 1 Old Faure Road, Somerset West 7129, Western Cape, PO Box 722, Somerset West, 7131, South Africa
  7. 7. Environmental Health Engineering Department, School of Public Health and Safety, Shahid Beheshti University of Medical Sciences, Tehran, Iran

Source: Environmental Science and Pollution Research Published:2023


Abstract

In this study, simultaneous removal of an organic matter (diazinon, DIZ) and an inorganic substance (chromium, Cr) was used. Breaking down of organic matter by UV irradiation produces various radicals, including sulfides, carboxyl, hydroxyl, hydrated electrons, and various organic radicals that are highly reactive and help us to precipitation inorganic substance (Cr). The optimal condition was 30:1 DIZ:Cr molar ratio, pH 9, and about 100% and 82.3% of DIZ and Cr were obtained in 30 min. Cr deposition was very slow at first. After the destruction of the DIZ structure, Cr deposition began, and various types of sludge with disturbed properties were formed. These sledges were analyzed by FTIR analysis and showed that green sludge could be chromium (III) hydroxide; brown sludge due to chromium (III) hydroxide, tiny green crystals from chromium (III) oxide, red brick from chromium (II) acetate chromium trioxide, as well as black sludge caused by chromium oxide were identified. In UV/DIZ/Cr process, kobs and robs range obtained 0.33–0.15 and 16.8–23.4 $ with both Cr and DIZ concentration increased from 50 to 150 mg L−1. Also, EEO for Cr precipitation was 24.65 to 5.74 and for DIZ 12.54 to 4.73 (kwh m−3). Depending on the amount of energy consumption, TCS was 37.19 to 10.47 for Cr precipitation and 4.46 to 1.25 $. It is important to note that when both pollutants are exposed to ultraviolet light, more energy and cost are generally required from UV/DIZ process and less than of UV/Cr process. But it should be noted that in fact 50 mg L−1 of chromium and 50 mg L−1 of DIZ are being removed at the same time. In UV/DIZ and UV/Cr processes that are exposed to ultraviolet radiation alone, only one of them is removed. Also, when these two pollutants are being removed at the same time, the total amount of energy is much less than the total energy consumption of the pollutants one by one. © 2022, The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature.