镍(ii)与2.4-噻唑烷酮配合物及其衍生物的反应研究

A. Zalov, K. A. Kuliyev, K. Aliyeva
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引用次数: 0

摘要

采用分光光度法研究了镍配合物与2.4-噻唑基茚二酮(L)及其衍生物{5-(气化硅基)-2,4-噻唑基茚二酮(L1)、5-(2-氯苄基)-2,4-噻唑基茚二酮(L2)、5-(2-羟基苄基)-2,4-噻唑烯二酮(L3)、5-(4-羟基苄基)-2,4-噻唑烯二酮(L4)、5-(2-溴-5-甲氧基苄基)-2,4-噻唑烯二酮(L5)的反应。一次提取,氯仿的镍提取率为97.8% ~ 98.4%。络合作用对pH的依赖性研究表明,pH 2.3 ~ 8.0是光密度最大且恒定的最佳酸度范围。这些化合物的镍配合物形成和萃取的最佳条件为(2.0 ~ 2.5)× 10-4 M浓度L,含L的镍配合物在水和有机溶剂中稳定,萃取3天不分解,萃取1个月以上。5分钟内达到最大光密度。在470 ~ 482 nm/摩尔吸收系数(1.37 ~ 1.61)×104处观察到镍L络合物的最大分析信号。镍的综合形式是Ni2+,而它从一个分子L中取代的质子数等于1。镍及其配合物在有机相中不聚合,以单体形式存在(γ = 1.01-1.07)。在已建立的最佳条件下,所提出的方法可用于测定废水、底部沉积物以及石油和石油产品中的Ni (II)。
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STUDY OF REACTION OF NICKEL (II) WITH 2.4-TYAZOLIDINDYON COMPLEX AND ITS DERIVATIVES
Spectrophotometric methods are used to study the reaction of the nickel complex with 2.4- tyazolidindico (L) and its derivatives {5- (gasilysiliden) -2,4-tyazolidindio (L1), 5- (2-chlorbenzyliden) -2,4- tyazolidindion (L2), 5-(2-hydroxybenzylide) -2,4-tiazoleader (L3), 5- (4-hydroxybenzylide)-2,4- tyazolidindion(L4),5-(2-Brom-5-methoxybenzyiliden)-2,4-tiazolyidinedion (L5). With a single extraction, the chloroform is extracted by 97.8-98.4 % of the nickel. The study of the dependence of complexation on pH showed that the optimal range of acidity, at which the optical density is maximum and constant, is at pH 2.3- 8.0. The optimal condition for the formation and extraction of the nickel complex of these compounds is (2.0- 2.5) × 10-4 M concentration L. Nickel complexes with L are stable in water and organic solvents and do not decompose for three days, and after extraction for more than a month. The maximum optical density is achieved within 5 minutes. The maximum analytical signal during the complex of nickel L is observed at 470-482 nm/ molar absorption coefficients (1.37-1.61)×104 . The comprehensive form of nickel is Ni2+while the number of protons supplanted by it from one molecule L turned out to be equal to 1. Nickel and its complexes in the organic phase are not polymerized and are in a monomeric form (γ = 1.01-1.07). The proposed method under already established optimal conditions is used to determine Ni (II) in wastewater, bottom deposits, as well as in oil and oil products.
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