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远紫外线光解硝酸盐产生的活性氮物种有助于农药降解和含氮副产物的形成。

Reactive Nitrogen Species Generated from Far-UVC Photolysis of Nitrate Contribute to Pesticide Degradation and Nitrogenous Byproduct Formation.

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210023, China.

Institute for the Environment and Health, Nanjing University Suzhou Campus, Suzhou 215163, China.

出版信息

Environ Sci Technol. 2024 Nov 19;58(46):20676-20686. doi: 10.1021/acs.est.4c05332. Epub 2024 Nov 6.

Abstract

Climate change has resulted in increased use of pesticides and fertilizers in agriculture, leading to elevated pesticide and nitrate levels in aquatic ecosystems that receive agricultural runoff. In this study, we demonstrate that far-UVC (UV) photolysis of nitrate rapidly degrades four pesticides in surface water, with a degradation rate constant 37.1-144.75 times higher than that achieved by UV photolysis of nitrate. The improved pesticide degradation is due not only to the enhanced direct photolysis by UV compared to UV but also to the increased generation of hydroxyl radicals (HO) and reactive nitrogen species (e.g., NO and ONOO) in the UV/nitrate process. We determined the innate quantum yields of nitrate photolysis at 222 nm and incorporated these values into a kinetic model, allowing for the accurate prediction of nitrate photodecay and reactive species generation. While reactive nitrogen species predominantly contribute to pesticide degradation in the UV/nitrate process, they also lead to the formation of nitration byproducts. Using stable isotope-labeled nitrate (NO) combined with mass spectrometry, we confirmed that the nitration byproducts are formed from the reactive nitrogen species generated from nitrate photolysis. Additionally, we demonstrate that the UV/nitrate process increases the formation potential of highly toxic nitrogenous chlorinated products (e.g., trichloronitromethane) during postchlorination in real surface water.

摘要

气候变化导致农业中农药和化肥的使用增加,导致接收农业径流的水生生态系统中的农药和硝酸盐水平升高。在这项研究中,我们证明了远紫外线(UV)光解硝酸盐可迅速降解地表水中的四种农药,其降解速率常数比单独 UV 光解硝酸盐高 37.1-144.75 倍。这种改进的农药降解不仅归因于与 UV 相比,UV 增强的直接光解,而且归因于在 UV/硝酸盐过程中生成更多的羟基自由基(HO)和反应性氮物种(例如,NO 和 ONOO)。我们测定了 222nm 处硝酸盐光解的固有量子产率,并将这些值纳入动力学模型中,从而可以准确预测硝酸盐光降解和反应性物种的生成。虽然反应性氮物种在 UV/硝酸盐过程中主要有助于农药降解,但它们也会导致硝化副产物的形成。使用稳定同位素标记的硝酸盐(NO)结合质谱,我们证实硝化副产物是由硝酸盐光解产生的反应性氮物种形成的。此外,我们证明了在实际地表水中进行后氯化时,UV/硝酸盐过程会增加高度有毒的含氮氯化产物(例如三氯硝基甲烷)的形成潜力。

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