Thermochemistry Laboratory, Chemical Science Division, Faculty of Health and Medical Sciences, University of Surrey, Guildford, Surrey, United Kigdom.
J Phys Chem B. 2011 Jun 2;115(21):6922-34. doi: 10.1021/jp110195f. Epub 2011 May 5.
Materials used in current technological approaches for the removal of mercury lack selectivity. Given that this is one of the main features of supramolecular chemistry, receptors based on calix[4]arene and calix[4]resorcarene containing functional groups able to interact selectively with polluting ions while discriminating against biologically essential ones were designed. Thus two receptors, a partially functionalized calix[4]arene derivative, namely, 5,11,17,23-tetra-tert-butyl [25-27-bis(diethyl thiophosphate amino)dihydroxy] calix[4]arene (1) and a fully functionalized calix[4]resorcarene, 4,6,10,12,16,18,22,24-diethyl thiophosphate calix[4]resorcarene (2) are introduced. Mercury(II) was the identified target due to the environmental and health problems associated with its presence in water Thus following the synthesis and characterization of 1 and 2 in solution ((1)HNMR) and in the solid state (X-ray crystallography) the sequence of experimental events leading to cation complexation studies in acetonitrile and methanol ((1)H NMR, conductance, potentiometric, and calorimetric measurements) with the aim of assessing their behavior as mercury selective receptors are described. The cation selectivity pattern observed in acetonitrile follows the sequence Hg(II) > Cu(II) > Ag(I). In methanol 1 is also selective for Hg(II) relative to Ag(I) but no interaction takes place between this receptor and Cu(II) in this solvent. Based on previous results and experimental facts shown in this paper, it is concluded that the complexation observed with Cu(II) in acetonitrile occurs through the acetonitrile-receptor adduct rather than through the free ligand. Receptor 2 has an enhanced capacity for uptaking Hg(II) but forms metalate complexes with Cu(II). These studies in solution guided the inmobilization of receptor 1 into a silica support to produce a new and recyclable material for the removal of Hg(II) from water. An assessment on its capacity to extract this cation from water relative to Cu(II) and Ag (I) shows that the cation selectivity pattern of the inmobilized receptor is the same as that observed for the free receptor in methanol. These findings demonstrate that fundamental studies play a critical role in the selection of the receptor to be attached to silicates as well as in the reaction medium used for the synthesis of the new decontaminating agent.
用于去除汞的当前技术方法中使用的材料缺乏选择性。鉴于这是超分子化学的主要特征之一,因此设计了基于杯[4]芳烃和杯[4]杯[4]芳烃的受体,这些受体含有能够与污染离子选择性相互作用而又能区分生物必需离子的官能团。因此,介绍了两种受体,一种是部分功能化的杯[4]芳烃衍生物,即 5,11,17,23-四叔丁基[25-27-双(二乙基硫代磷酸基氨基)二羟基]杯[4]芳烃(1)和一种完全功能化的杯[4]杯[4]芳烃,4,6,10,12,16,18,22,24-二乙基硫代磷酸杯[4]杯[4]芳烃(2)。由于汞(II)存在于水中会带来环境和健康问题,因此将其确定为目标。因此,在溶液中(1)HNMR)和固态(X 射线晶体学)中对 1 和 2 的合成和表征后,描述了导致在乙腈和甲醇中进行阳离子络合研究的实验事件序列(1)H NMR、电导率、电位和量热测量),旨在评估它们作为汞选择性受体的行为。在乙腈中观察到的阳离子选择性模式遵循 Hg(II)>Cu(II)>Ag(I)的顺序。在甲醇中,1 相对于 Ag(I)对 Hg(II)也具有选择性,但在该溶剂中,该受体与 Cu(II)之间没有相互作用。基于本文中显示的先前结果和实验事实,得出结论,与 Cu(II)在乙腈中观察到的络合作用是通过乙腈-受体加合物而不是通过游离配体发生的。受体 2 对摄取 Hg(II)的能力增强,但与 Cu(II)形成金属配合物。这些溶液中的研究指导了将受体 1 固定到硅胶载体上,以生产一种从水中去除 Hg(II)的新型可回收材料。对其从水中提取这种阳离子相对于 Cu(II)和 Ag(I)的能力的评估表明,固定化受体的阳离子选择性模式与在甲醇中观察到的游离受体相同。这些发现表明,基础研究在选择要附着到硅酸盐上的受体以及在用于合成新的去污剂的反应介质中起着至关重要的作用。