Guangdong Provincial Engineering Technology Research Center for Urban Water Cycle and Water Environment Safety, Tsinghua Shenzhen International Graduate School, Tsinghua University, Shenzhen, 518055, PR China; State Environmental Protection Key Laboratory of Microorganism Application and Risk Control, School of Environment, Tsinghua University, Beijing, 100084, PR China.
Guangdong Provincial Engineering Technology Research Center for Urban Water Cycle and Water Environment Safety, Tsinghua Shenzhen International Graduate School, Tsinghua University, Shenzhen, 518055, PR China; State Environmental Protection Key Laboratory of Microorganism Application and Risk Control, School of Environment, Tsinghua University, Beijing, 100084, PR China; Department of Civil and Environmental Engineering, University of California, Irvine, CA, 92612, United States.
Chemosphere. 2022 Apr;292:133391. doi: 10.1016/j.chemosphere.2021.133391. Epub 2021 Dec 20.
The preparation of easily synthesized and cheap composite materials for the efficient removal of toxic oxoanions still remains challenging in sewage treatment. Herein, a new carbonized manganese-crosslinked sodium alginate (Mn/SA-C) was fabricated for the removal of arsenite (As(III)), arsenate (As(V)) and hexavalent chromium (Cr(VI)) in water. The results indicated that the Mn/SA-C pretreated with MnSO solution (Mn/SA-C-S) exhibited a rapid adsorption toward As(III) and As(V) with the removal efficiency of >98% within 10 min, and had a high adsorption capacity toward As(III), As(V), and Cr(VI) with the maximum value of 189.29, 193.29, and 104.50 mg/g based on the Langmuir model, respectively. The removal efficiency of As(III), As(V), and Cr(VI) could be further significantly enhanced by coupling a photocatalytic process. For example, the time in which >98% of Cr(VI) (10 mg/L) was removed dramatically shortened from 360 min (adsorption) to 45 min (adsorption-photocatalysis), and the removal efficiency of As(III) increased by ∼10% within initial 5 min. This was primarily attributed to the Mn-catalyzed production of the photocatalytic excitons for Cr(VI) reduction, and the superoxide (•O) and hydroxyl (•OH) radicals for As(III) oxidation. The adsorption removal of arsenic (As) was primarily ascribed to surface complexation with MnO and precipitation by MnS, and oxidative adsorption because of Mn valence cycle. The removal mechanisms of Cr(VI) mainly contained reduction by MnO and MnS, complexation with MnO and carboxyl/hydroxyl groups as well as Cr(OH) precipitation. Our research provides a promising Mn/SA-C-S material for rapid and efficient removal of As(III), As(V), and Cr(VI) in contaminated water through an adsorption-photocatalysis synergistic strategy.
用于高效去除污水中毒性氧阴离子的易于合成和廉价的复合材料的制备仍然具有挑战性。在此,制备了一种新的碳化锰交联海藻酸钠(Mn/SA-C),用于去除水中的亚砷酸盐(As(III))、砷酸盐(As(V)) 和六价铬(Cr(VI))。结果表明,用 MnSO 溶液预处理的 Mn/SA-C(Mn/SA-C-S)对 As(III) 和 As(V) 具有快速吸附作用,在 10 分钟内去除效率超过 98%,并且对 As(III)、As(V) 和 Cr(VI) 具有高吸附能力,基于 Langmuir 模型,最大吸附值分别为 189.29、193.29 和 104.50mg/g。通过耦合光催化过程,可以进一步显著提高去除 As(III)、As(V) 和 Cr(VI) 的效率。例如,将 >98%的 Cr(VI)(10mg/L)去除所需的时间从 360 分钟(吸附)缩短到 45 分钟(吸附-光催化),并且在前 5 分钟内,As(III)的去除效率提高了约 10%。这主要归因于 Mn 催化产生光催化激子还原 Cr(VI),以及超氧化物(•O)和羟基(•OH)自由基氧化 As(III)。砷(As)的吸附去除主要归因于 MnO 的表面络合和 MnS 的沉淀,以及由于 Mn 价循环而发生的氧化吸附。Cr(VI)的去除机制主要包括 MnO 和 MnS 的还原、MnO 和羧基/羟基的络合以及 Cr(OH)的沉淀。我们的研究提供了一种有前途的 Mn/SA-C-S 材料,用于通过吸附-光催化协同策略快速高效地去除受污染水中的 As(III)、As(V) 和 Cr(VI)。