Graphical'/> The process of atrazine degradation, its mechanism, and the formation of metabolites using UV and UV/MW photolysis
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The process of atrazine degradation, its mechanism, and the formation of metabolites using UV and UV/MW photolysis

机译:使用UV和UV / MW光解的阿特拉津降解,其机制和代谢物的形成

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Graphical abstract Display Omitted Highlights ? Degradation mechanism process and metabolites/products using different energies. ? Photolytic oxidation of atrazine was studied using different energies. ? Degradation rates of atrazine were quantitatively better and more fast using UV/MW system. ? Degradation products, were identified using liquid chromatography and standard solution of the formed metobolites/products. Abstract The photolytic degradationmechanism of atrazine using a UV reactor andUV/MW (electrodeless discharge lamp (Hg-EDL)) was investigated. After 120s of UV photolysis partial degradation of atrazine had been observed and a subsequent formation of degradation products of atrazine-2-hydroxy, therefore, defining the path of atrazine degradation through UV photolysis. This system after 1200s of exposure to UV radiation had not reached full degradation of atrazine, and its metabolite (atrazine-2-hydroxy), was the main by-product obtained for the process. When performing photolysis through the UV/Microwave combined methodcomplete atrazine degradation was obtained within a 5s interval, besides the formation of five (5) degradation products, which are HAT, DEAT, DIAT, DEHAT and DIHAT. Therefore, defining the path of the photolytic degradation process through the UV/Microwave combined method. The total degradation of its metabolite (HAT) was observed for the period of 120s of exposure to UV/MW radiation, and after that time there had been no signcorresponding to the respective compounds. The tests with the isolated microwave radiation were not efficient in the degradation of the atrazine and, therefore, the respective isolated energy is not applicable.The control of atrazine degradation and consequent formation of metabolites were accompanied by a high-performance liquid chromatography with a UV/Vis detector. ]]>
机译:<![cdata [ 图形抽象 显示省略 亮点 使用不同能量的降级机制过程和代谢物/产品。 使用不同的能量研究了阿特拉嗪的光解氧化。 使用UV / MW系统定量更好地逐步更好地逐渐变得更快。 劣化产品,使用液相色谱和所形成的茂化硼酸盐/产品的标准溶液识别。 抽象 使用UV反应器Anduv / MW(无电极放电灯(HG-EDL)的光解劣化机制)被调查了。在120℃以下之后,已经观察到尿嘧啶的UV光解偏降解的UV光解偏降解,并且随后形成尿嘧啶-2-羟基的降解产物,从而定义通过UV光解的尿嘧啶降解的路径。该系统在1200℃以下的暴露于紫外线辐射的 S均未达到阿特拉嗪的全面降解,其代谢物(阿特拉津-2-羟基)是用于该过程的主要副产物。当通过UV /微波组合方法允许的尿嘧啶降解在5 S的间隔内,除了形成五(5)个降解产物的情况下,提供了帽子,鹿,DIAT, dehat和dihat。因此,通过UV /微波组合方法定义光解劣化过程的路径。观察到其代谢物(帽子)的总劣化为120 暴露于UV / MW辐射的时期,并且在此之后没有对相应的化合物进行映射。与分离的微波辐射的试验在尿嘧啶的降解中不有效,因此,相应的隔离能量是不适用的。亚唑嗪降解和随后的代谢物形成的控制伴有紫外线的高效液相色谱法/ VIS检测器。 ]]>

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