期刊文献+

手性有机磷农药在土壤中对映体选择性降解特征 被引量:5

Enantioselective degradation characteristics of chiral organophosphorous insecticides in soil
下载PDF
导出
摘要 马拉硫磷和丙溴磷是2种常用的有机磷杀虫剂,均有一个手性中心存在2个对映体。采用室内避光培养的方法,在对映体水平上研究了马拉硫磷和丙溴磷在2种土壤中的降解情况。结果表明,2种农药在土壤中的降解均较快,马拉硫磷和丙溴磷的降解半衰期分别为:黄土中3.5h和21.5h,红土中4.3h和29.4h。进一步的手性测定表明2种农药的降解均存在一定的对映体差异,丙溴磷对映体的选择性明显高于马拉硫磷,在2种土壤中马拉硫磷的左旋对映体降解快于右旋对映体,丙溴磷的右旋体降解快于左旋体。研究有助于深入认识2种有机磷农药在环境中的归趋,并对其生态风险性进行更合理的评估。 Malathion and profenophos are widely used as organophosphorous insecticides. Either of the two insecticides has one chiral center in stereostructure, and therefore they exist as two enantiomers respectively. In this paper, the enantioselective degradation of malathion and profenophos in two typical soils were studied in details. Our results showed that the two pesticides were degraded fast in the two soils. The half-lives of malathion and profenophos were 3.5 and 21.5 h in huabei yellow soil, and 4.3 and 29.4 h in hubei red soil, respectively. Further chiral analysis demonstrated their enantioselectivities during the degradation of the two pesticides. It was further observed obviously that the enantiosclectivity of profenophos was much higher than that of malathion. Moreover, the (-)-enantiomer of malathion was degraded faster than the (+)-enantiomer in the two soils. As for profenophos, the (+)-enantiomer was degraded faster than its corresponding (-)-enantiomer in the two soils. The study results are useful for better understanding the environmental profiles of malathion and profenophos as well as further ecological risk evaluation of the two pesticides.
出处 《生态环境学报》 CSCD 北大核心 2009年第4期1247-1250,共4页 Ecology and Environmental Sciences
基金 国家自然科学基金青年基金项目(20707005)
关键词 马拉硫磷 丙溴磷 手性 对映体选择性降解 生态风险 农药 土壤 Malathion profenophos chiral enantioselective degradation ecological risk pesticide soil
  • 相关文献

参考文献15

  • 1KURIHARA N, MIYAMOTO J, PAULSON G D, et al. Chirality's in synthetic agrochemicals: bioactivity and safety consideration[J]. Pure andApplied Chemistry, 1997, 69(6): 1335-1348.
  • 2MULLER T A, KOHLER H-P E. Chirality's of pollutants effects on metabolism and fate[J]. Applied Microbiology and Biotechnology, 2004, 64(3): 300-316.
  • 3LEWIS D L, GARRISON A W, WOMMACK K E, et al. Influence of environmental changes on degradation of chiral pollutants in soils[J]. Nature, 1999, 401(28): 898-901.
  • 4LERDER H, CASIDA J E. Resolution and biological activity of the chiral isomers of O-(4-bromo-2-chlorophenyl) O-ethyl S-propyl phosphorothioate (profenofos insecticide)[J]. Journal of Agricultural and Food Chemistry, 1982, 30(3): 546-551.
  • 5MIYAZAKI A. Progress and prospects of optically active pesticides[J]. Journal of Pesticide Science,1997, 22: 136-155.
  • 6MILES C J, TAKASHIMA S. Fate of malathion and O,O,S-trimethyl phosphorothioate by-product in Hawaiian soil and water[J]. Archives of Environmental Contamination and Toxicology, 1991, 20(3): 325-329.
  • 7GETENGAZ M, JONDIKO J I O, WANDIGA S O, et al. Dissipation behavior of malathion and dimethoate residues from the soil and their uptake by garden pea ( Pisum sativum )[J]. Bulletin of Environmental Contamination and Toxicology, 2000, 64: 359-367.
  • 8RADWAN M A, ABU-ELAMAYEM M M, SHIBOOB M H, et al. Residual behavior of profenofos on some field-grown vegetables and its removal using various washing solutions and household processing[J]. Food and Chemical Toxicology, 2005, 43: 553-557.
  • 9李朝阳,张智超,张玲,冷连.土壤中高效氟氯氰菊酯对映体选择性降解的研究[J].农业环境科学学报,2006,25(6):1640-1643. 被引量:9
  • 10ABHILASH P C, SINGH V, S1NGH N. Simplified determination of combined residues of lindane and other HCH isomers in vegetables, fruits, wheat, pulses and medicinal plants by matrix solid-phase dispersion(MSPD) followed by GC-ECD[J]. Food Chemistry, 2009, 113: 267-271.

二级参考文献11

  • 1Li Z Y,Zhang Z C,Zhou Q L,et al.Fast and precise determination of phenthoate and its enantiomeric ratio in soil by the matrix solid-phase dispersion method and liquid chromatography[J].J Chromatography A,2002,977:12-25.
  • 2Liu W,Qin S,Gan J Y.Chiral stability of synthetic pyrethroid insecticides[J].J Agri Food Chem,2005,53:3814-3820.
  • 3Lewis D L,Garrison A W,Wommack K E,et al.Influence of soils[J].Nature,1999,401(28):898-901.
  • 4Müller T A,Kohler H-P E.Chirality of pollutants-effects on metabolism and fate[J].Appl Microbiol Biotechnol,2004,64(3):300-316.
  • 5Muller M D,Buser H R.Conversion reactions of varous phenoxyalkanoic acid herbicides in soil.1.Enantiomerization and enantioselective degradation of the chiral 2-phenoxypro-ionic acid herbicides[J].Environ Sci Technol,1997,31:1953-1959.
  • 6Leicht W,Fuchs R,Londershausen M.Stability and biologic-al activity of cyfluthrin isomers[J].Pestic Sci,1996,48:325-332.
  • 7Smith S Jr,Willis G H,Cooper C M.Cyfluthrin persistence in soil as affected by moisture,organic matter and redox potential[J].Bull Environ Contam Toxicol,1995,55(1):142-148.
  • 8Lodhi A,Naqvi S H M,Fuhr F,et al.Degradation of 14C -lab-eled cyfluthrin in soil and incorporation of 14C into humic fractions as affected by wheat[J].Pak J Sci Ind Res,1996,39(5-8):128-131.
  • 9Barker S A.Matrix solid-phase dispersion[J].J Chromatography A,2000,885:115-127.
  • 10徐逸楣.光学活性农药开发的现状与展望(上)[J].农药译丛,1998,20(1):6-16. 被引量:27

共引文献8

同被引文献51

引证文献5

二级引证文献11

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部