School of Ecology and Environment, Inner Mongolia University, Hohhot 010021, China.
School of Ecology and Environment, Inner Mongolia University, Hohhot 010021, China; Institute of Environmental Geology, Inner Mongolia University, Hohhot 010021, China.
Ecotoxicol Environ Saf. 2018 Jun 15;154:59-68. doi: 10.1016/j.ecoenv.2018.02.013. Epub 2018 Feb 22.
The composition and structure of Humic acid (HA) is so heterogeneous that it brings significant barriers to investigate the interaction between HA and heavy metal ions. The isolation of HA with relatively homogeneity is a key to reveal the binding mechanisms between HA and heavy metals. In this work, ten HA fractions (HAs) were obtained by sequential alkali extraction procedure and nature differences of the extracted HAs were considered as explanatory factors for binding characteristics of Cu, Pb and Cd. The results indicate that more large molecular weight (MW) HA subunits, less carboxyl and phenolic group contents, weaker aromaticity and polarity were measured with increasing extractions, inducing weaker binding capacity of HAs. Ligand binding and bi-Langmuir models indicated that the sorption capacity and binding affinity of earlier extracted HAs were higher than the latter ones. The peak area changes at 3427, 1599, and 619 cm pre- and post-adsorption in FTIR spectra suggested carboxyl, phenolic and nitrogen-containing groups were involved in the adsorption process. At the same time, the peak area difference between HAs and HAs-metal (ΔS) of phenolic groups were 8.22-20.50, 6.81-21.11 and 10.66-19.80% for Cu, Pb and Cd, respectively, ΔS of carboxyl groups 6.64-17.03, 8.96-16.82 and 9.45-17.85% for Cu, Pb and Cd, respectively, ΔS of nitrogen-containing groups 0.33-0.48, 0.20-1.38 and 0.31-0.59% for Cu, Pb and Cd, respectively. ΔS of phenolic and carboxyl groups were larger than those of nitrogen-containing groups, implying that these two groups were the predominant binding sites suppliers for metal ions, which were also supported by the results of correlation analysis. This work is helpful to insight the environmental impacts of natural organic matter and the fate of heavy metals in natural environment.
腐殖酸(HA)的组成和结构非常复杂,这给研究腐殖酸与重金属离子的相互作用带来了重大障碍。相对均相的腐殖酸的分离是揭示腐殖酸与重金属结合机制的关键。在这项工作中,通过连续碱提取程序获得了十种腐殖酸(HA)级分,并且提取的 HA 的自然差异被认为是解释 Cu、Pb 和 Cd 结合特性的因素。结果表明,随着提取次数的增加,检测到更多的大分子量(MW)HA 亚基、更少的羧基和酚基含量、较弱的芳香性和极性,导致 HA 的结合能力减弱。配体结合和双朗缪尔模型表明,早期提取的 HA 的吸附容量和结合亲和力高于后期提取的 HA。FTIR 光谱中吸附前后 3427、1599 和 619 cm 处峰面积的变化表明,羧基、酚基和含氮基团参与了吸附过程。同时,HA 和 HAs-金属(ΔS)之间酚基的峰面积差异分别为 8.22-20.50、6.81-21.11 和 10.66-19.80%,对于 Cu、Pb 和 Cd,羧基的峰面积差异分别为 6.64-17.03、8.96-16.82 和 9.45-17.85%,对于 Cu、Pb 和 Cd,含氮基团的峰面积差异分别为 0.33-0.48、0.20-1.38 和 0.31-0.59%。酚基和羧基的ΔS 大于含氮基团的ΔS,这意味着这两组是金属离子的主要结合位点供体,这也得到了相关分析结果的支持。这项工作有助于深入了解天然有机物对环境的影响以及重金属在自然环境中的归宿。