School of Environment and Energy, South China University of Technology, Guangzhou, Guangdong, 510006, People's Republic of China; The Key Lab of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, South China University of Technology, Guangzhou, Guangdong, 510006, People's Republic of China.
Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River) Ministry of Agriculture, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, People's Republic of China.
Chemosphere. 2020 Apr;244:125517. doi: 10.1016/j.chemosphere.2019.125517. Epub 2019 Dec 2.
The speciation and mobility of As are controlled by both Fe and Mn (oxyhydr)oxides through a series of surface complexation and redox reactions occurring in the environment, which is also complicated by the solution chemistry conditions. However, there is still a lack of quantitative tools for predicting the coupled kinetic processes of As reactions with Fe and Mn (oxyhydr)oxides. In this study, we developed a quantitative model for the coupled kinetics of As adsorption/desorption and oxidation in ferrihydrite-Mn (oxyhydr)oxides and ferrihydrite-Mn(II)-O systems. This model also accounted for the variations in solution chemistry conditions and binding site heterogeneity. Our model suggested that Mn (oxyhydr)oxide and ferrihydrite mainly served as an oxidant and an adsorbent, respectively, when they coexisted. Among the three types of binding sites of ferrihydrite, the adsorbed As(V) was mainly distributed on the nonprotonated bidentate sites. Our model quantitatively showed that the oxidation rates of different reaction systems varied significantly. The rates of As(III) oxidation were enhanced with higher pH values and higher molar ratios of Mn(II)/As(III) in the ferrihydrite-Mn(II)-O system. This study provides a modeling framework for predicting the kinetic behavior of As when multiple adsorption/desorption and oxidation reactions are coupled in the environment.
砷的形态和迁移受到铁和锰(氢氧)氧化物的控制,这是通过一系列在环境中发生的表面络合和氧化还原反应来实现的,而这些反应也受到溶液化学条件的影响。然而,目前仍然缺乏用于预测砷与铁和锰(氢氧)氧化物的耦合动力学过程的定量工具。在这项研究中,我们开发了一个用于铁氢氧化物-锰(氢氧)氧化物和铁氢氧化物-Mn(II)-O 系统中砷吸附/解吸和氧化的耦合动力学的定量模型。该模型还考虑了溶液化学条件和结合位点异质性的变化。我们的模型表明,当锰(氢氧)氧化物和铁氢氧化物共存时,它们主要分别作为氧化剂和吸附剂。在铁氢氧化物的三种结合位点中,吸附的 As(V) 主要分布在非质子化的双齿位点上。我们的模型定量地表明,不同反应体系的氧化速率有很大差异。在铁氢氧化物-Mn(II)-O 体系中,随着 pH 值的升高和 Mn(II)/As(III)摩尔比的升高,As(III)的氧化速率也随之提高。本研究为预测环境中多种吸附/解吸和氧化反应耦合时砷的动力学行为提供了一个建模框架。