4.7 Article

Photochemical transformation of sulfadiazine in UV/Fe(II)/sodium citrate Fenton-like system

期刊

JOURNAL OF ENVIRONMENTAL MANAGEMENT
卷 322, 期 -, 页码 -

出版社

ACADEMIC PRESS LTD- ELSEVIER SCIENCE LTD
DOI: 10.1016/j.jenvman.2022.116112

关键词

Sulfadiazine; Photodegradation; Hydroxyl groups; UV/Fe(II)/SC system; Degradation pathway; Oxidation

资金

  1. General Project of the National Natural Science Foundation of China [41772364]
  2. Grant for Innovative Research Groups of the National Natural Science Foundation of China [41521001]
  3. Fundamental Research Funds for the Central Universities, China University of Geosciences (Wuhan) [122-G1323522145, 1910491T05]
  4. National Students' platform for innovation and entrepreneurship training program [S201910491193, S202010491198]

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This study investigated an enhanced photochemical Fenton-like system for the degradation of antibiotic sulfadiazine (SDZ). The results showed that the UV/Fe(II)/SC system had the highest degradation rate and efficiency. Dissolved substances such as HCO3-, SO42-, and NO3- in the water environment inhibited the degradation of SDZ, and the concentration of SDZ and high concentration of humic acid (HA) decreased the degradation rate of the target compound. Four degradation pathways were proposed based on the identification of photodegradation products of SDZ.
The persistence and potential hazards of antibiotics in the aquatic environment have attracted worldwide attention. Currently, advanced oxidation technology is considered to be an effective way to degrade antibiotics in the water environment. An enhanced photochemical Fenton-like system was investigated in this study for degradation of antibiotic sulfadiazine (SDZ). The degradation kinetics, pathways, and mechanisms of SDZ in four different photocatalytic systems were studied, including ultraviolet (UV), UV/sodium citrate (SC), UV/Fe(II), and UV/Fe(II)/SC. The highest degradation rate of SDZ was observed in UV/Fe(II)/SC system, and the complexation of SC-Fe(II) promoted photocatalytic efficiency and iron cycling. It was proved that hydroxyl radicals (circle OH) were generated in UV/Fe(II)/SC system, but excessive Fe(II) consumed circle OH and produced a UV shielding effect, thus reducing the degradation rate of SDZ. In the UV/Fe(II)/SC system, the degradation of SDZ followed pseudo-firstorder kinetics, and the reaction rate constant of SDZ reached a maximum of 8.49 x 10 3 min 1, with a degradation efficiency of 97.7%. Even in different real water samples, the removal rate of SDZ can reach about 80%. HCO3-, SO42-, and NO3 in the water environment inhibited the degradation of SDZ, and the order of inhibition was as follows: SO42- > HCO3- >NO3-. With the increase of SDZ concentration and high concentration of humic acid (HA), the degradation rate of the target compound decreased. By identifying the photodegradation products of SDZ, four degradation pathways were proposed, and it revealed that the N-C bond and N-S bond were broken by attacking of hydroxyl groups, where a hydroxyl group replaced the H atom, resulting in the decomposition of SDZ into low molecular weight compounds like SO2, CO2, NO3- and H2O. It suggested that the UV/Fe(II)/SC system has good effect and application prospect in SAs treatment.

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