Guangdong Industrial Contaminated Site Remediation Technology and Equipment, Engineering Research Center, School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China.
Guangdong Industrial Contaminated Site Remediation Technology and Equipment, Engineering Research Center, School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China.
J Environ Sci (China). 2023 Mar;125:14-25. doi: 10.1016/j.jes.2022.01.023. Epub 2022 Jan 23.
Simultaneous elimination of As(III) and Pb(II) from wastewater is still a great challenge. In this work, an iron-sulfur codoped biochar (Fe/S-BC) was successfully fabricated in a simplified way and was applied to the remediate the co-pollution of As(III) and Pb(II). The positive enthalpy indicated that the adsorption in As-Pb co-pollution was an endothermic reaction. The mechanism of As(III) removal could be illustrated by surface complexation, oxidation and precipitation. In addition to precipitation and complexation, the elimination mechanism of Pb(II) also contained ion exchange and electrostatic interactions. Competitive and synergistic effects existed simultaneously in the co-contamination system. The suppression of As(III) was ascribed to competitive complexation of the two metals on Fe/S-BC, while the synergy of Pb(II) was attributed to the formation of the PbFe(AsO)(OH). Batch experiments revealed that Fe/S-BC had outstanding ability to remove As(III) and Pb(II), regardless of pH dependency and interference by various coexisting ions. The maximum adsorption capacities of the Fe/S-BC for As(III) and Pb(II) were 91.2 mg/g and 631.7 mg/g, respectively. Fe/S-BC could be treated as a novel candidate for the elimination of As(III)-Pb(II) combined pollution.
同时去除废水中的 As(III) 和 Pb(II) 仍然是一个巨大的挑战。在这项工作中,以一种简化的方式成功制备了铁硫共掺杂生物炭 (Fe/S-BC),并将其应用于修复 As(III) 和 Pb(II) 的复合污染。正焓表明,As-Pb 复合污染中的吸附是一个吸热反应。As(III) 的去除机制可以通过表面络合、氧化和沉淀来解释。除沉淀和络合外,Pb(II) 的去除机制还包括离子交换和静电相互作用。在共存体系中,同时存在竞争和协同效应。As(III) 的抑制归因于两种金属在 Fe/S-BC 上的竞争络合,而 Pb(II) 的协同作用归因于 PbFe(AsO)(OH) 的形成。批量实验表明,无论 pH 值依赖性和各种共存离子的干扰如何,Fe/S-BC 都具有出色的去除 As(III) 和 Pb(II) 的能力。Fe/S-BC 对 As(III) 和 Pb(II) 的最大吸附容量分别为 91.2 mg/g 和 631.7 mg/g。Fe/S-BC 可作为一种新型的去除 As(III)-Pb(II) 复合污染的候选材料。