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铜离子选择性电极与荧光滴定法联用测定腐殖质中铜(II)离子的条件稳定常数

Combination of a Copper-Ion Selective Electrode and Fluorometric Titration for the Determination of Copper(II) Ion Conditional Stability Constants of Humic Substances.

作者信息

Chen Juan, Chen Hao, Zhang Xing-wen, Lei Kun, Kenny Jonathan E

机构信息

Dalian University of Technology, School of Environmental Science and Technology, Dalian 116024, China.

出版信息

Appl Spectrosc. 2015 Nov;69(11):1293-302. doi: 10.1366/14-07835.

Abstract

A fluorescence quenching model using copper(II) ion (Cu(2+)) ion selective electrode (Cu-ISE) is developed. It uses parallel factor analysis (PARAFAC) to model fluorescence excitation-emission matrices (EEMs) of humic acid (HA) samples titrated with Cu(2+) to resolve fluorescence response of fluorescent components to Cu(2+) titration. Meanwhile, Cu-ISE is employed to monitor free Cu(2+) concentration ([Cu]) at each titration step. The fluorescence response of each component is fit individually to a nonlinear function of [Cu] to find the Cu(2+) conditional stability constant for that component. This approach differs from other fluorescence quenching models, including the most up-to-date multi-response model that has a problematic assumption on Cu(2+) speciation, i.e., an assumption that total Cu(2+) present in samples is a sum of [Cu] and those bound by fluorescent components without taking into consideration the contribution of non-fluorescent organic ligands and inorganic ligands to speciation of Cu(2+). This paper employs the new approach to investigate Cu(2+) binding by Pahokee peat HA (PPHA) at pH values of 6.0, 7.0, and 8.0 buffered by phosphate or without buffer. Two fluorescent components (C1 and C2) were identified by PARAFAC. For the new quenching model, the conditional stability constants (logK1 and logK2) of the two components all increased with increasing pH. In buffered solutions, the new quenching model reported logK1 = 7.11, 7.89, 8.04 for C1 and logK2 = 7.04, 7.64, 8.11 for C2 at pH 6.0, 7.0, and 8.0, respectively, nearly two log units higher than the results of the multi-response model. Without buffer, logK1 and logK2 decreased but were still high (>7) at pH 8.0 (logK1 = 7.54, logK2 = 7.95), and all the values were at least 0.5 log unit higher than those (4.83 ~ 5.55) of the multi-response model. These observations indicate that the new quenching model is more intrinsically sensitive than the multi-response model in revealing strong fluorescent binding sites of PPHA in different experimental conditions. The new model was validated by testing it with a mixture of two fluorescing Cu(2+) chelating organic compounds, i.e., l-tryptophan and salicylic acid mixed with one non-fluorescent binding compound oxalic acid titrated with Cu(2+) at pH 5.0.

摘要

建立了一种使用铜(II)离子(Cu(2+))离子选择性电极(Cu-ISE)的荧光猝灭模型。该模型利用平行因子分析(PARAFAC)对用Cu(2+)滴定的腐殖酸(HA)样品的荧光激发-发射矩阵(EEMs)进行建模,以解析荧光成分对Cu(2+)滴定的荧光响应。同时,使用Cu-ISE监测每个滴定步骤的游离Cu(2+)浓度([Cu])。将各成分的荧光响应分别拟合为[Cu]的非线性函数,以求出该成分的Cu(2+)条件稳定常数。这种方法不同于其他荧光猝灭模型,包括最新的多响应模型,该模型对Cu(2+)的形态有一个有问题的假设,即假设样品中存在的总Cu(2+)是[Cu]与那些与荧光成分结合的Cu(2+)之和,而没有考虑非荧光有机配体和无机配体对Cu(2+)形态的贡献。本文采用这种新方法研究了在磷酸盐缓冲或无缓冲条件下,pH值为6.0、7.0和8.0时,帕霍基泥炭腐殖酸(PPHA)与Cu(2+)的结合情况。通过PARAFAC鉴定出两种荧光成分(C1和C2)。对于新的猝灭模型,两种成分的条件稳定常数(logK1和logK2)均随pH值的升高而增加。在缓冲溶液中,新的猝灭模型在pH 6.0、7.0和8.0时分别报告C1的logK1 = 7.11、7.89、8.04,C2的logK2 = 7.04、7.64、8.11,比多响应模型的结果高出近两个对数单位。在无缓冲条件下,logK1和logK2降低,但在pH 8.0时仍较高(>7)(logK1 = 7.54,logK2 = 7.95),所有值至少比多响应模型的值(4.83 ~ 5.55)高0.5个对数单位。这些观察结果表明,在揭示不同实验条件下PPHA的强荧光结合位点方面,新的猝灭模型比多响应模型更具内在敏感性。通过用两种荧光Cu(2+)螯合有机化合物(即l-色氨酸和水杨酸)与一种非荧光结合化合物草酸在pH 5.0下用Cu(2+)滴定的混合物对新模型进行测试,验证了该新模型。

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