Department of Environmental Engineering, College of Environmental Sciences and Engineering, Peking University, The Key Laboratory of Water and Sediment Sciences, Ministry of Education, Beijing 100871, China.
Water Res. 2013 Feb 1;47(2):588-96. doi: 10.1016/j.watres.2012.10.020. Epub 2012 Oct 22.
This study examined the binding of copper(II) by Suwannee River fulvic acid (SRFA) using the method of differential absorbance that was used at environmentally-relevant concentrations of copper and SRFA. The pH- and metal-differential spectra were processed via numeric deconvolution to establish commonalities seen in the changes of absorbance caused by deprotonation of SRFA and its interactions with copper(II) ions. Six Gaussian bands were determined to be present in both the pH- and Cu-differential spectra. Their maxima were located, in the order of increasing wavelengths at 208 nm, 242 nm, 276 nm, 314 nm, 378 nm and 551 nm. The bands with these maxima were denoted as A0, A1, A2, A3, A4 and A5, respectively. Properties of these bands were compared with those existing in the spectra of model compounds such as sulfosalicylic acid (SSA), tannic acid (TA), and polystyrenesulfonic acid-co-maleic acid (PSMA). While none of the features observed in differential spectra of the model compound were identical to those present in the case of SRFA, Gaussian bands A1, A3 and possibly A2 were concluded to be largely attributable to a combination of responses of salicylic- and polyhydroxyphenolic groups. In contrast, bands A4 and A5 were detected in the differential spectra of SRFA only. Their nature remains to be elucidated. To examine correlations between the amount of copper(II) bound by SRFA and changes of its absorbance, differential absorbances measured at indicative wavelengths 250 nm and 400 nm were compared with the total amount of SRFA-bound copper estimated based on Visual MINTEQ calculations. This examination showed that the differential absorbances of SRFA in a wide range of pH values and copper concentrations were strongly correlated with the concentration of SRFA-bound copper. The approach presented in this study can be used to generate in situ information concerning the nature of functional groups in humic substances engaged in interactions with metals ions. This information can be useful for further elaboration and development of detailed theoretic models that describe the complexation of metals in the environment.
本研究采用环境相关浓度的铜和苏万尼河腐殖酸(SRFA)的差分吸收方法研究了铜(II)与苏万尼河腐殖酸的结合。通过数值解卷积处理 pH 和金属差分光谱,以确定 SRFA 去质子化及其与铜(II)离子相互作用引起的吸光度变化中的共同特征。在 pH 和 Cu 差分光谱中确定存在六个高斯带。它们的最大值按波长增加的顺序分别位于 208nm、242nm、276nm、314nm、378nm 和 551nm。具有这些最大值的带分别表示为 A0、A1、A2、A3、A4 和 A5。将这些带的性质与模型化合物(如磺基水杨酸(SSA)、单宁酸(TA)和聚苯乙烯磺酸-马来酸共聚物(PSMA))的光谱中的性质进行了比较。虽然在模型化合物的差分光谱中观察到的特征与 SRFA 中存在的特征没有一个完全相同,但高斯带 A1、A3 并且可能 A2 被认为主要归因于水杨酸和多羟基酚基团的组合响应。相比之下,仅在 SRFA 的差分光谱中检测到带 A4 和 A5。它们的性质仍有待阐明。为了研究 SRFA 结合的铜(II)量与吸光度变化之间的相关性,比较了在指示波长 250nm 和 400nm 测量的差分吸光度与基于 Visual MINTEQ 计算估计的 SRFA 结合的铜总量。该检查表明,在广泛的 pH 值和铜浓度范围内,SRFA 的差分吸光度与 SRFA 结合的铜浓度强烈相关。本研究中提出的方法可用于生成有关参与与金属离子相互作用的腐殖质中官能团性质的原位信息。该信息对于进一步阐述和开发描述环境中金属络合的详细理论模型非常有用。