Department of Integrated Energy and Infra system, Kangwon National University, 1, Kangwondaehak-gil, Chuncheon-si, Gangwon-do, 24341, Republic of Korea.
Radioactive Waste Disposal Research Division, Korea Atomic Energy Research Institute, Daejeon, 34057, Republic of Korea.
Environ Pollut. 2024 Nov 15;361:124850. doi: 10.1016/j.envpol.2024.124850. Epub 2024 Aug 29.
This study evaluated the effects of post-calcination on the charge properties and active sites of Mg/Al layered double hydroxide-decorated spent coffee ground biochars (LDH@SCGB) governing adsorption behaviors and mechanisms of arsenic (As) and antimony (Sb) anions from aqueous phases. Post-calcinated LDH@SCGB (PLDH@SCGB) exhibited higher adsorption capacities for As and Sb compared to spent coffee ground biochars (SCGB) and LDH@SCGB as post-calcination of LDH@SCGB enhanced the charge properties (surface zeta potential at pH 7.0: SCGB = -21.8 mV, LDH@SCGB = 28.5 mV, and PLDH@SCGB = 34.4 mV) and increased active sites by eliminating the anions (i.e., Cl ions) and water molecules at its interlayers. The calculated kinetic, intra-particle diffusion, and isotherm parameters indicated that the chemisorption and intra-particle diffusion were mainly responsible for the adsorption of As and Sb by SCGB, LDH@SCGB, and PLDH@SCGB. Moreover, post-calcination of LDH@SCGB enhanced its selectivity toward As and Sb by reinforcing the electrostatic surface complexation via its improvement of charge properties. Since PLDH@SCGB exhibited the excellent reusability for the adsorption of As (reuse efficiency >63.6%) and Sb (reuse efficiency >52.1%), it can be concluded that post-calcination of LDH@SCGB is a promising method for improving the adsorption capacities for As and Sb in real water matrices.
本研究评估了煅烧后对负载镁/铝水滑石的咖啡渣生物炭电荷特性和活性位的影响,从而控制砷(As)和锑(Sb)阴离子在水溶液中的吸附行为和机制。煅烧后的 LDH@SCGB(PLDH@SCGB)对 As 和 Sb 的吸附容量高于咖啡渣生物炭(SCGB)和 LDH@SCGB,因为 LDH@SCGB 的煅烧增强了其电荷特性(pH 值为 7.0 时的表面zeta 电位:SCGB = -21.8 mV,LDH@SCGB = 28.5 mV,PLDH@SCGB = 34.4 mV),并通过消除层间的阴离子(即 Cl 离子)和水分子增加了活性位。计算的动力学、内扩散和等温线参数表明,化学吸附和内扩散是 SCGB、LDH@SCGB 和 PLDH@SCGB 吸附 As 和 Sb 的主要原因。此外,LDH@SCGB 的煅烧通过增强其电荷特性,加强静电表面络合,提高了对 As 和 Sb 的选择性。由于 PLDH@SCGB 对 As(再利用效率>63.6%)和 Sb(再利用效率>52.1%)的吸附具有优异的可重复使用性,可以得出结论,煅烧 LDH@SCGB 是提高实际水基质中 As 和 Sb 吸附容量的一种很有前途的方法。