Yao Jianmei, Zhang Lingxue, Ran Jinfeng, Wang Shasha, Dong Nan
School of Chemistry and Chemical Engineering, Guizhou University, Guiyang, 550025, China.
Key Laboratory of Macrocyclic and Supramolecular Chemistry of Guizhou Province, Guiyang, 550025, China.
Mikrochim Acta. 2020 Sep 25;187(10):578. doi: 10.1007/s00604-020-04491-5.
Molecularly imprinted stir-bar coatings were created based on a hydroxylcucurbit[7]uril-paraquat inclusion complex. The inclusion complex that contained paraquat (PQ) as a template and monohydroxylcucurbit[7]uril ((OH)Q[7]) as a monomer was preassembled mainly through cavity inclusion interaction of (OH)Q[7] to form a one-dimensional self-assembly structure. The inclusion complex was anchored chemically on the surface of a glass stir bar with hydroxy-terminated poly(dimethylsiloxane) by the sol-gel technique to obtain a molecularly imprinted polymer-coated stir bar (MIP-SB). The molecularly imprinted coating showed specific adsorption for cationic PQ in aqueous media. Other quaternary amine compounds with a similar structure that coexisted in the solution, such as ethyl-viologen, diquat, and difenzoquat, were almost not extracted by the prepared MIP-SB. The sorptive capacity of the MIP-SB for PQ was nearly four times that of the non-imprinted stir bar (NIP-SB). The recognition mechanism indicated that the selectivity and extraction capacity resulted mainly from the imprinted cavity in the polymer that was formed by a one-dimensional assembly structure consisting of the (OH)Q[7]-PQ inclusion complex. The imprinted cavity was complementary to the PQ in shape, size, and functionality. A method to determine PQ in environmental water and vegetable samples was developed by combining MIP-SB sorptive extraction with HPLC-UV. The linear range was from 100 to 10,000 ng L with a 8.2 ng L detection limit for water samples and 0.02-0.85 mg kg with a 0.005 mg kg detection limit for vegetable samples. The limit of detection for both samples was lower than the EU-established maximum residual levels and that of other previously reported methods. The average recoveries were 70.0-96.1% with a relative standard deviation ≤ 7.6%, which showed the successful application in real sample analysis. Molecularly imprinted stir-bar coatings were created based on a hydroxylcucurbit[7]uril-paraquat (PQ) inclusion complex, which showed a specific recognition toward cationic PQ. A method to determine PQ in environmental water and vegetable samples was established by combining MIP-SB sorptive extraction with HPLC-UV.
基于羟基葫芦[7]脲 - 百草枯包合物制备了分子印迹搅拌棒涂层。以百草枯(PQ)为模板、单羟基葫芦[7]脲((OH)Q[7])为单体的包合物主要通过(OH)Q[7]的空腔包合作用预组装形成一维自组装结构。通过溶胶 - 凝胶技术将该包合物与羟基封端的聚二甲基硅氧烷化学锚定在玻璃搅拌棒表面,得到分子印迹聚合物涂层搅拌棒(MIP - SB)。该分子印迹涂层在水介质中对阳离子型PQ表现出特异性吸附。溶液中共存的其他结构相似的季铵盐化合物,如乙基紫精、敌草快和野燕枯,几乎不被制备的MIP - SB萃取。MIP - SB对PQ的吸附容量几乎是非印迹搅拌棒(NIP - SB)的四倍。识别机制表明,选择性和萃取能力主要源于聚合物中由(OH)Q[7] - PQ包合物组成的一维组装结构形成的印迹空腔。该印迹空腔在形状、尺寸和功能上与PQ互补。通过将MIP - SB吸附萃取与HPLC - UV联用,建立了一种测定环境水样和蔬菜样品中PQ的方法。水样品的线性范围为100至10,000 ng/L,检测限为8.2 ng/L;蔬菜样品的线性范围为0.02至0.85 mg/kg,检测限为0.005 mg/kg。两种样品的检测限均低于欧盟规定的最大残留限量以及其他先前报道方法的检测限。平均回收率为70.0 - 96.1%,相对标准偏差≤7.6%,表明该方法在实际样品分析中成功应用。基于羟基葫芦[7]脲 - 百草枯(PQ)包合物制备了分子印迹搅拌棒涂层,其对阳离子型PQ表现出特异性识别。通过将MIP - SB吸附萃取与HPLC - UV联用,建立了一种测定环境水样和蔬菜样品中PQ的方法。