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Layer-by-layer coated imidazolium - Styrene copolymers fibers for improved headspace-solid phase microextraction analysis of aromatic compounds

机译:分层涂覆的咪唑鎓-苯乙烯共聚物纤维,用于改进芳族化合物的顶空-固相微萃取

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The design of poly(ionic liquids) (PILs) and their application as solid phase microextraction (SPME) fibers has been attracting enormous attention mainly due to the need for new SPME coating materials with improved analytical sensitivity. In this work, the tunability of Pits is explored by preparing different imidazolium monomers bearing benzyl, naphtylmethyl or pentyl pending groups that were subsequently co-polymerized, by reversible addition-fragmentation chain transfer (RAFT) polymerization with styrene. The obtained co-polymers showed excellent thermal stability up to 275 degrees C, with no melting point up to 250 degrees C. SPME fibers were prepared by an innovative approach based on layer-by-layer spray coating. The thin ( 10 mu m) SPME coatings were tested in GC-FID for the detection of volatile aromatic compounds such as benzene (B), toluene (T), ethylbenzene (E) and xylene (X) present in aqueous samples and the extraction parameters optimized. Superior results were obtained when comparing these LbL PILS-based SPME fibers with a commercial fiber composed of poly(dimethylsiloxane), with an increase in the detectable areas of 83%, 69%, 57% and 58% for B, T, E and X, respectively. Low relative standard deviations were obtained for the same fiber ( 5.6%) and also for different fibers ( 9.8%). Furthermore, a spiked soil sample was used to mimic a real contaminated soil sample and excellent recovery results, ranging from 67.0% to 102.2%, were obtained.
机译:聚离子液体(PIL)的设计及其作为固相微萃取(SPME)纤维的应用已经引起了极大的关注,这主要是由于需要具有改进的分析灵敏度的新型SPME涂层材料。在这项工作中,通过制备带有苄基,萘甲基或戊基未决基团的不同咪唑鎓单体来探索基坑的可调谐性,这些单体随后通过与苯乙烯的可逆加成-断裂链转移(RAFT)聚合而共聚。所获得的共聚物在高达275摄氏度的温度下显示出优异的热稳定性,在高达250摄氏度的温度下没有熔点。通过基于逐层喷涂的创新方法制备了SPME纤维。薄(<10μm)SPME涂层在GC-FID中进行了测试,用于检测水性样品中存在的挥发性芳族化合物,例如苯(B),甲苯(T),乙苯(E)和二甲苯(X)。优化提取参数。将这些基于LbL PILS的SPME纤维与由聚(二甲基硅氧烷)组成的商用纤维进行比较,可获得卓越的结果,其中B,T,E和B的可检测区域分别增加了83%,69%,57%和58%。 X,分别。对于相同的纤维(<5.6%)和不同的纤维(<9.8%),获得较低的相对标准偏差。此外,使用加标土壤样品来模拟实际污染的土壤样品,并获得了67.0%至102.2%的极佳回收率。

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