Groupe de Physico-Chimie de l'Atmosphère-ICPEES (UMR 7515 CNRS Université de Strasbourg), 1, rue Blessig, 67084, Strasbourg CEDEX, France.
Environ Sci Pollut Res Int. 2015 Feb;22(4):2726-34. doi: 10.1007/s11356-014-3534-z. Epub 2014 Sep 11.
An analytical methodology using automatic thermal desorption (ATD) and GC/MS was developed for the determination of 28 pesticides of different chemical classes (dichlobenil, carbofuran, trifluralin, clopyralid, carbaryl, flazasulfuron, mecoprop-P, dicamba, 2,4-MCPA, dichlorprop, 2,4-D, triclopyr, cyprodinil, bromoxynil, fluroxypyr, oxadiazon, myclobutanil, buprofezin, picloram, trinexapac-p-ethyl, ioxynil, diflufenican, tebuconazole, bifenthrin, isoxaben, alphacypermethrin, fenoxaprop and tau-fluvalinate) commonly used in nonagricultural areas in atmospheric samples. This methodology was developed to evaluate the indoor and outdoor atmospheric contamination by nonagricultural pesticides. Pesticides were sampled passive sampling tubes containing Tenax® adsorbent. Since most of these pesticides are polar (clopyralid, mecoprop-P, dicamba, 2,4-MCPA, dichlorprop, 2,4-D, triclopyr, bromoxynil, fluroxypyr, picloram, trinexapac-p-ethyl and ioxynil), a derivatisation step is required. For this purpose, a silylation step using N-(t-butyldimethylsilyl)-N-methyltrifluoroacetamide (MtBSTFA) was added before thermal desorption. This agent was chosen since it delivers very specific ions on electronic impact (m/z = M-57). This method was established with special consideration for optimal thermal desorption conditions (desorption temperature, desorb flow and duration; trap heating duration and flow; outlet split), linear ranges, limits of quantification and detection which varied from 0.005 to 10 ng and from 0.001 to 2.5 ng, respectively, for an uncertainty varied from 8 to 30 %. The method was applied in situ to the analysis of passive tubes exposed during herbicide application to an industrial site in east of France.
开发了一种使用自动热解吸(ATD)和 GC/MS 的分析方法,用于测定 28 种不同化学类别的农药(二氯苯腈、克百威、氟乐灵、氯吡丙醚、甲萘威、唑嘧磺草胺、麦草畏、2,4-MCPA、二氯丙酸、2,4-D、三氯吡氧乙酸、吡虫啉、溴苯腈、氟草烟、恶唑酮、灭草烟、丙硫菌唑、丁醚脲、氯氟吡氧乙酸、噻酮隆、乙氧氟草醚、异噁唑草酮、高效氯氟氰菊酯、溴氰菊酯、异氰戊菊酯、氟氰戊菊酯)。这些农药常用于非农地区的大气样本中。该方法旨在评估非农用农药的室内和室外大气污染。农药通过装有 Tenax®吸附剂的被动采样管进行采样。由于大多数这些农药是极性的(氯吡丙醚、麦草畏、2,4-MCPA、二氯丙酸、2,4-D、三氯吡氧乙酸、溴苯腈、氟草烟、氯氟吡氧乙酸、乙氧氟草醚、异噁唑草酮),需要进行衍生化步骤。为此,在热解吸前添加了使用 N-(叔丁基二甲基硅基)-N-甲基三氟乙酰胺(MtBSTFA)的硅烷化步骤。选择这种试剂是因为它在电子冲击下产生非常特定的离子(m/z= M-57)。该方法的建立特别考虑了最佳热解吸条件(解吸温度、解吸流量和持续时间;阱加热持续时间和流量;出口分流)、线性范围、定量下限和检测下限,其变化范围分别为 0.005 至 10ng 和 0.001 至 2.5ng,不确定度变化范围为 8 至 30%。该方法应用于法国东部一个工业现场施药期间暴露的被动管的原位分析。