首页> 外文期刊>Journal of Environmental Science and Health, Part B: Pesticides, Food Contaminants, and Agricultural Wastes >Photolysis of the herbicide bispyribac sodium in aqueous medium under the influence of UV and sunlight in presence or absence of sensitizers
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Photolysis of the herbicide bispyribac sodium in aqueous medium under the influence of UV and sunlight in presence or absence of sensitizers

机译:在存在或不存在敏化剂的情况下,在紫外线和日光的影响下,水介质中除草剂双嘧菌钠的光解

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The photolysis of a rice herbicide Bispyribac sodium (Sodium 2, 6-bis [(4, 6-dimethoxypyrimidin-2-yl) oxy] benzoate) has been studied in different aqueous medium (distilled water, pond water and Irrigation water) under the influence of UV (λ max ≥ 250 nm) and sunlight in presence or absence of sensitizers (TiO2 and KNO3). The study was conducted under laboratory simulated condition which made it possible to evaluate the contribution of different factors viz. source of irradiation, solvent and sensitizers towards the photolysis of bispyribac sodium. The photodegradation proceeds via first order reaction Kinetics in all the cases. Five photo metabolites (M1-M5) were isolated in pure form by column chromatographic method from the irradiation system under UV influenced and TiO2 as sensitizer. From the different spectral data (IR, NMR, UV-VIS, Mass) the structure of these five metabolites were assigned as M1 (Phenol), M2 [2, 6-Dihydroxy benzoic acid], M3 [2, 6-bis [(4, 6 dimethoxypyrimidin-2yl) oxy] benzoic acid], M4 [2-(3-Hydroxy-phenoxy)-pyrimidine-4, 6-diol] and M5 as [2,4-Dihydroxy-3, 5-dimethoxy-6-(4-methoxy pyrimidine-2-yloxy)-benzoic acid]. Moreover, another six photometabolites (M6-M11) were identified from the different irradiation system on the basis of Micromass analysis. On the basis of MS/MS data analysis, the structure of these six photometabolites were assigned as M6 [2-(4, 6-Dimethoxy-pyrimidin-2-yloxy)-6-hydroxy-benzoic acid], M7 [2-Hydroxy-6-(4-hydroxy-6-methoxy-pyrimidin-2-yloxy)-benzoic acid], M8 [4, 6-Dimethoxy-pyrimidin-2-ol], M9 [6-Methoxy-pyrimidine-2, 4-diol], M10 [2-Hydroxy-6-(pyrimidin-2-yloxy)-benzoic acid] and M11 [2, 4, 6-Trimethoxy-pyrimidine]. The plausible Photodegradation pathways of bispyribac sodium in the present investigation were portrayed which proceeds via hydrolysis, hydrolytic cleavage, O-dealkylation, decarboxylation, dehydroxylation, O-alkylation and hydroxylation.
机译:在不同的水介质(蒸馏水,池塘水和灌溉水)下,研究了水稻除草剂双嘧菌钠(2,6-双[(4,6-二甲氧基嘧啶-2-基)氧基]苯甲酸钠)的光解作用。 UV的影响(最大≥250 nm)和存在或不存在敏化剂(TiO 2 和KNO 3 )的阳光。该研究是在实验室模拟条件下进行的,这使得有可能评估不同因素的贡献。辐射源,溶剂和敏化剂对双嘧菌钠的光解作用。在所有情况下,光降解都是通过一级反应动力学进行的。在紫外光和TiO 2 影响下,通过柱色谱法从照射系统中分离出五种光代谢产物(M 1 -M 5 )。作为敏化剂。根据不同的光谱数据(IR,NMR,UV-VIS,质谱),这五个代谢物的结构分别为M 1 (苯酚),M 2 [2, 6-二羟基苯甲酸],M 3 [2,6-双[(4,6二甲氧基嘧啶-2基)氧基]苯甲酸],M 4 [2-( 3-羟基-苯氧基)-嘧啶-4,6-二醇]和M 5 为[2,4-二羟基-3,5-二甲氧基-6-(4-甲氧基嘧啶-2-基氧基) )-苯甲酸]。此外,在微质量分析的基础上,从不同的照射系统中鉴定出另外六种光代谢产物(M 6 -M 11 )。在MS / MS数据分析的基础上,将这六种光代谢物的结构指定为M 6 [2-(4,6-二甲氧基-嘧啶-2-基氧基)-6-羟基-苯甲酸酸],M 7 [2-羟基-6-(4-羟基-6-甲氧基-嘧啶-2-基氧基)-苯甲酸],M 8 [4 ,6-二甲氧基-嘧啶-2-醇],M 9 [6-甲氧基-嘧啶-2、4-二醇],M 10 [2-羟基-6 -(嘧啶-2-基氧基)-苯甲酸]和M 11 [2,4,6-三甲氧基-嘧啶]。描绘了在本研究中可能存在的双嘧菌钠的光降解途径,其通过水解,水解裂解,O-脱烷基,脱羧,脱羟基,O-烷基化和羟基化而进行。

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    Pesticide Residue Laboratory, Department of Agricultural Chemicals, Bidhan Chandra Krishi Viswavidyalaya, Mohanpur, Nadia, West Bengal, India;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
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  • 入库时间 2022-08-18 00:58:02

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