曹俊丽, 刘新刚, 董丰收, 徐军, 吴小虎, 郑永权, 郭平毅, 宋喜娥. 噻呋酰胺在稻田中的残留及消解动态[J]. 农药学学报, 2017, 19(1): 84-92. DOI: 10.16801/j.issn.1008-7303.2017.0012
    引用本文: 曹俊丽, 刘新刚, 董丰收, 徐军, 吴小虎, 郑永权, 郭平毅, 宋喜娥. 噻呋酰胺在稻田中的残留及消解动态[J]. 农药学学报, 2017, 19(1): 84-92. DOI: 10.16801/j.issn.1008-7303.2017.0012
    CAO Junli, LIU Xingang, DONG Fengshou, XU Jun, WU Xiaohu, ZHENG Yongquan, GUO Pingyi, SONG Xi'e. Residues and decline dynamics of thifluzamide in rice field[J]. Chinese Journal of Pesticide Science, 2017, 19(1): 84-92. DOI: 10.16801/j.issn.1008-7303.2017.0012
    Citation: CAO Junli, LIU Xingang, DONG Fengshou, XU Jun, WU Xiaohu, ZHENG Yongquan, GUO Pingyi, SONG Xi'e. Residues and decline dynamics of thifluzamide in rice field[J]. Chinese Journal of Pesticide Science, 2017, 19(1): 84-92. DOI: 10.16801/j.issn.1008-7303.2017.0012

    噻呋酰胺在稻田中的残留及消解动态

    Residues and decline dynamics of thifluzamide in rice field

    • 摘要: 建立了气相色谱-离子阱质谱(GC-ITMS)检测稻田水、土壤、糙米、稻壳和植株中噻呋酰胺残留的分析方法,通过田间试验研究了噻呋酰胺在稻田中的残留及消解动态。结果表明:在0.03~6 mg/L范围内,噻呋酰胺的进样质量浓度与色谱峰面积间呈良好的线性关系;在添加水平为0.03、0.3和3 mg/L时,噻呋酰胺在田水、土壤、糙米、稻壳和水稻植株中的平均回收率在71%~100%之间,相对标准偏差(RSD)在1.8%~11.4%之间。噻呋酰胺在以上基质中的方法定量限(LOQ)为0.03 mg/kg,检出限(LOD)为0.01 mg/kg。分别用一级动力学方程和二级动力学方程对消解动态试验数据进行了拟合,田水中噻呋酰胺的消解半衰期为2.4~9.2 d,土壤中的为1.8~10.3 d,植株中的为1.3~4.1 d。本研究结果表明,在有效使用剂量不高于169.2 g/hm2,水稻生育期施药次数不超过3次的条件下,稻谷成熟收获时噻呋酰胺在稻谷中的残留量远低于中国国家标准中规定的3 mg/kg。

       

      Abstract: An analysis method using gaschromatography-ion trap mass spectrometry (GC-ITMS) was developed for the determination of thifluzamide residues in water, soil, rice, plants and hulls. The residues and decline dynamics of thifluzamide in paddy field were conducted by field experiments. The calibration curve showed a good linearity in the range of 0.03-6 mg/L with the correlation coefficient above 0.99. The average recoveries of thifluzamide in five samples at three spiked levels of 0.03, 0.3 and 3 mg/kg all ranged from 71% to 100%, with the relative standard deviation (RSD) of 1.8% to11.4%. The limits of quantitation (LOQ) in those samples were 0.03 mg/kg. The limit of detection (LOD) was 0.01 mg/kg. The dynamic data were fitted by the first-order kinetics equation and second-order kinetics equation. Results show that the half-lives of thifluzamide were 2.4 to 9.2 d in paddy water, 1.8 to 10.3 d in the soil, and 1.3 to 4.1 d in the plant. And this study demonstrated that if the application rate of thifluzamide was below 169.2 g (a.i)/hm2 with no more than three times application, the thifluzamide residues in rice at harvest time were below Chinese maximum residue limit (3 mg/kg).

       

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