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鞣革废水中碱性沉淀后铬的形态:分离与特性分析。

Chromium speciation in tannery effluent after alkaline precipitation: Isolation and characterization.

机构信息

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210023, China; School of Chemistry & Chemical Engineering, Yancheng Institute of Technology, Yancheng 224051, China.

State Key Laboratory of Pollution Control and Resource Reuse, School of the Environment, Nanjing University, Nanjing 210023, China.

出版信息

J Hazard Mater. 2016 Oct 5;316:169-77. doi: 10.1016/j.jhazmat.2016.05.021. Epub 2016 May 9.

Abstract

It is difficult to completely remove Cr(III) from tannery effluent by alkaline precipitation due to the abundance of strong organic ligands. Thereby, the speciation of the residual Cr after alkaline precipitation is of crucial significance to guide the selection and design of further treatment process. For the first time, we revealed the speciation of the residual Cr with the aid of comprehensive analytical techniques. Results showed that the residual Cr(III) mostly located in two size ranges, i.e. the 13-100nm fraction and the <4nm fraction. Combined spectral analyses demonstrated Cr(III) was coordinated by carboxyl groups or hydroxyl groups in both fractions, while the complexation by nitrogen-containing groups was excluded by the total nitrogen and UPLC-MS analysis in the two fractions, respectively. Based on the comprehensive analyses, the structures of Cr(III) complexes in both fractions were proposed. Cr(III) cross-linked the carboxyl groups from polyacrylic acid chains to form the network gel structure in the 13-100nm fraction, while the complex structure of Cr(III) in the <4nm fraction was formed through hydroxyl-carboxyl chelation by masking agents such as tartrate and citrate. Although polyoxyethylene ether was abundantly present, it was responsible for the complexation of Cr(III) in neither fraction.

摘要

由于强有机配体的丰富存在,通过碱性沉淀很难将鞣革废水中的 Cr(III) 完全去除。因此,碱性沉淀后残留 Cr 的形态对于指导进一步处理过程的选择和设计具有重要意义。我们首次借助综合分析技术揭示了残留 Cr 的形态。结果表明,残留的 Cr(III) 主要分布在两个粒径范围内,即 13-100nm 部分和 <4nm 部分。结合光谱分析表明,Cr(III) 在两个部分中均通过羧基或羟基与配体配位,而通过总氮和 UPLC-MS 分析排除了两个部分中含氮基团的配位。基于综合分析,提出了两个部分中 Cr(III) 配合物的结构。Cr(III) 在 13-100nm 部分中通过交联聚丙烯酸链上的羧基形成网络凝胶结构,而在 <4nm 部分中 Cr(III) 的配合物结构则是通过掩蔽剂(如酒石酸和柠檬酸)的羟基-羧基螯合形成的。尽管聚氧乙烯醚大量存在,但它既不是这两个部分中 Cr(III) 配合物形成的原因。

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