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Selective removal of chromium (VI) from sulphates andother metal anions using an ion-imprinted polymer

机译:从硫酸盐和硫酸盐中选择性除去铬(VI)使用离子印迹聚合物的其他金属阴离子

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摘要

A linear copolymer was prepared from 4-vinylpyridine and styrene. An ion-imprinted polymer (IIP) specific for Cr (VI)adsorption was prepared by copolymerisation of the quaternised linear copolymer (quaternised with 1,4-chlorobutane),2-vinylpyridine functional monomer and ethylene glycol dimethacrylate (EGDMA), as the cross-linking monomer, in thepresence of 1,1’-azobis(cyclohexanecarbonitrile) as initiator. Ammonium dichromate and aqueous methanol were used as atemplate and porogenic solvent, respectively. Leaching of the chromate template from the polymer particles was achievedwith successive stirring of the ion-imprinted polymer (IIP) particles in 4 M HNO3 solutions to obtain leached materials,which were then used for selective rebinding of Cr (VI) ions from aqueous solutions. Similarly, the non-imprinted polymer/control polymer (NIP/CP) material was also prepared under exactly the same conditions as the IIP but without the chromateanion template. Various parameters, such as solution pH, initial concentration, aqueous phase volume, sorbent dosage,contact time and leaching solution volumes, were investigated. Scanning electron microscopy (SEM), Fourier TransformInfrared (FTIR) spectroscopy, BET surface area and pore size analysis were used for the characterisation of IIP (bothunleached and leached) and CP materials. Optimal parameters were as follows: solution pH, 3; contact time, 120 min; eluent,20 mℓ of 0.1 M NaOH; and sorbent amount, 125 mg. Maximum retention capacity of IIP and CP was 37.58 and 25.44mg∙g-1, respectively. The extraction efficiencies of the IIP and CP were compared using a batch and SPE mode of extraction.In the absence of high concentrations of ions, especially sulphate ions, both CP and IIP demonstrated no differences inbinding of Cr (VI), which was almost 100%. However, in the presence of high concentrations of sulphate ions, the selectivityon the CP completely collapsed. The study clearly demonstrates the suitably of the developed IIP for selective extractionof Cr (VI) in complex samples such as those from acid mine drainage. The selectivity was also compared by direct injectionof the real-world sample, both spiked and non-spiked, into that obtained after IIP selective extraction. Despite the method’svery low detection limits for direct injection (below 1 μg∙ℓ-1), no Cr (VI) was obtained. However, after IIP selective extraction,spiked Cr (VI) was detected in the spiked sample.
机译:由4-乙烯基吡啶和苯乙烯制备线性共聚物。通过将季铵化的线性共聚物(与1,4-氯丁烷季铵化),2-乙烯基吡啶官能单体和乙二醇二甲基丙烯酸酯(EGDMA)进行共聚,制备了一种特定的Cr(VI)吸附离子印迹聚合物(IIP)。 -1,1'-偶氮二(环己烷甲腈)为引发剂时生成的-连接单体。重铬酸铵和甲醇水溶液分别用作模板剂和成孔剂。通过在4 M HNO3溶液中连续搅拌离子印迹聚合物(IIP)颗粒以获得铬酸盐模板从聚合物颗粒中的浸出,以获得浸出的材料,然后将其用于从水溶液中选择性地重新结合Cr(VI)离子。同样,非压印聚合物/对照聚合物(NIP / CP)材料也是在与IIP完全相同的条件下制备的,但没有铬酸根模板。研究了各种参数,例如溶液pH,初始浓度,水相体积,吸附剂用量,接触时间和浸出溶液体积。扫描电子显微镜(SEM),傅立叶变换红外(FTIR)光谱,BET表面积和孔径分析用于表征IIP(底部浸出和浸出)和CP材料。最佳参数如下:溶液pH 3;接触时间120分钟;洗脱液:20 ml 0.1 M NaOH;和吸附量125 mg。 IIP和CP的最大保留容量分别为37.58和25.44mg∙g-1。通过分批和SPE萃取方式对IIP和CP的萃取效率进行了比较。在没有高浓度离子(尤其是硫酸根离子)的情况下,CP和IIP均未显示出Cr(VI)的结合率几乎为100 %。但是,在高浓度硫酸根离子存在下,CP的选择性完全崩溃了。该研究清楚地证明了开发的IIP适用于选择性提取复杂样品(例如酸性矿山排水中的样品)中的Cr(VI)。还通过直接注入加标样品和未加标样品的实际样品与IIP选择性萃取后获得的样品进行了比较。尽管该方法的直接进样检测限非常低(低于1μg∙ℓ-1),但仍未获得Cr(VI)。但是,经过IIP选择性萃取后,在加标样品中检测到了加标的Cr(VI)。

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