首页> 外文期刊>Journal of Atmospheric Chemistry >Physicochemical Transformation and Photochemical Reactions in High-Disperse Substance State: Chemical Decomposition in Aerosols and Thin Films Made from Pesticide Fipronil (Adonis)
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Physicochemical Transformation and Photochemical Reactions in High-Disperse Substance State: Chemical Decomposition in Aerosols and Thin Films Made from Pesticide Fipronil (Adonis)

机译:高分散物质状态下的物理化学转化和光化学反应:农药Fipronil(Adonis)制成的气溶胶和薄膜中的化学分解

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摘要

A chemical substance being in a high-disperse state (fine aerosol particles and very thin films) in the environment reveals specific chemical and physicochemical features which differ from the processes in a relatively coarse disperse object and, even more, in ordinary liquid and solid "test-tube" assays. The kinetics and the mechanism of the direct and sensitized photochemical destruction of pesticide compound fipronil C_(12)H_4Cl_2F_6N_4OS have been experimented as applied to the aerosol particles ≈ 0.12-1.3 μm in diameter and thin films ≈ 0.02-0.6 μm thick on the glass plates. A non-photochemical ("dark") reaction of fipronil molecules with the OH radicals which spontaneously proceeds in the ambient air was also observed. Quantitative estimations based on experimental results show that the fipronil pollutant, observed in the atmosphere in the form of levitated aerosols, can convert chemically in the above reaction with the OH radicals for a very short time (from several minutes for a particle 2 μm in diameter to 12-24 h for a particle of 20-30 μm). The fipronil residues presented on foliage either in the form of 1-20 μm films or as a group of deposited 2-30 μm aerosols react under sunlight by two photochemical pathways (photooxidation and photodecay). The lifetime of these residues in the ambient conditions is expected to be 11-25 days. Besides, adding a small amount of the Shirvanol 2 sensitizer to the fipronil formulation, one can increase the overall decomposition rate to 8-12 days.
机译:在环境中处于高分散状态的化学物质(细小的气溶胶颗粒和非常薄的薄膜)显示出特定的化学和物理化学特征,这些特征与相对较分散的物体(甚至在普通的液体和固体中)不同。试管”试验。已对农药化合物氟虫腈C_(12)H_4Cl_2F_6N_4OS进行直接和敏化光化学破坏的动力学和机理进行了实验,并将其应用于玻璃板上直径约0.12-1.3μm的气溶胶颗粒和玻璃板上约0.02-0.6μm厚的薄膜。还观察到氟虫腈分子与在环境空气中自发进行的OH自由基的非光化学(“暗”)反应。根据实验结果的定量估计表明,在大气中以悬浮气溶胶的形式观察到的氟虫腈污染物可以在很短的时间内(在几分钟内对直径为2μm的颗粒进行化学反应)与OH自由基发生化学转化。对于20-30μm的颗粒,则需要12至24小时)。以1-20μm薄膜的形式或以一组沉积的2-30μm气溶胶形式存在于叶子上的氟虫腈残留物在阳光下通过两种光化学途径(光氧化和光衰变)发生反应。这些残留物在环境条件下的寿命预计为11-25天。此外,在氟虫腈制剂中添加少量的Shirvanol 2敏化剂,可使整体分解速率增加至8-12天。

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