4.6 Article

Kinetics of the photolysis of pyridaben and its main photoproduct in aqueous environments under simulated solar irradiation

Journal

RSC ADVANCES
Volume 12, Issue 33, Pages 21647-21654

Publisher

ROYAL SOC CHEMISTRY
DOI: 10.1039/d2ra02601e

Keywords

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Funding

  1. National Key Research and Development Program of China [2021YFD1700104]
  2. National Natural Science Foundation of China [21866009]

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The photolytic fate of pyridaben and its main photolysis product was studied in various aqueous solutions. The results showed that the pH, organic compound concentration, as well as the concentration of nitrate and Fe(iii), significantly influenced the photolysis of pyridaben. The photolysis rate of pyridaben was much higher in rainwater, tap water, and river water compared to distilled water.
The photolytic fate of pyridaben and its main photolysis product was investigated in different aqueous solutions. Results showed that the photolysis of pyridaben followed pseudo first-order kinetics or the hockey-stick model. In buffer solutions, the half-life of pyridaben was the shortest at pH 4, while the degradation rate within 24 h was the highest at pH 9. Humic acids (HA) at concentrations of 1-20 mg L-1 favored the photolysis of pyridaben while fulvic acids (FA) did not have a significant effect. Nitrate at low concentrations (0.01 mM) accelerated the photolysis and Fe(iii) at high concentrations (0.01 and 0.1 mM) significantly inhibited the photolysis. The photolysis rate of pyridaben in rainwater, tap water, and river water was significantly higher than that in distilled water. The half-lives in distilled water, rainwater, tap water, river water, and pond water were 2.36, 1.36, 1.61, 1.77, and 2.68 h, respectively. Ultra-high-performance liquid chromatography/high-resolution mass spectrometry identified M328 as a photolysis product. The degradation of M328 followed pseudo first-order kinetics in distilled water, buffer solutions and aqueous solutions fortified with HA. The half-lives of M328 were in the range of 7.07-13.95 h. These results are essential for further environmental risk assessment of pyridaben.

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