Institute of Soil and Environmental Sciences, University of Agriculture Faisalabad, Faisalabad, 38040, Pakistan.
State Key Laboratory for Modification of Chemical Fibers and Polymer Materials, College of Environmental Science and Engineering, Donghua University, 2999 Ren'min North Road, Shanghai, 201620, China.
Environ Sci Pollut Res Int. 2024 Aug;31(39):52293-52305. doi: 10.1007/s11356-024-34661-4. Epub 2024 Aug 15.
The utilization of biowastes for producing biochar to remove potentially toxic elements from water represents an important pathway for aquatic ecosystem decontamination. Here we explored the significance of thiol-functionalization on sugarcane bagasse biochar (Th/SCB-BC) and rice husk biochar (Th/RH-BC) to enhance arsenite (As(III)) removal capacity from water and compared their efficiency with both pristine biochars (SCB-BC and RH-BC). The maximum As(III) sorption was found on Th/SCB-BC and Th/RH-BC (2.88 and 2.51 mg g, respectively) compared to the SCB-BC and RH-BC (1.51 and 1.40 mg g). Relatively, a greater percentage of As(III) removal was obtained with Th/SCB-BC and Th/RH-BC (92% and 83%, respectively) at a pH 7 compared to pristine SCB-BC and RH-BC (65% and 55%) at 6 mg L initial As(III) concentration, 2 h contact time and 1 g L sorbent dose. Langmuir (R = 0.99) isotherm and pseudo-second-order kinetic (R = 0.99) models provided the best fits to As(III) sorption data. Desorption experiments indicated that the regeneration ability of biochars decreased and it was in the order of Th/SCB-BC (88%) > Th/RH-BC (82%) > SCB-BC (77%) > RH-BC (69%) up to three sorption-desorption cycles. Fourier-transform infrared spectroscopy and X-ray photoelectron spectroscopy results demonstrated that the thiol (-S-H) functional groups were successfully grafted on the surface of two biochars and as such contributed to enhance As(III) removal from water. Spectroscopic data indicated that the surface functional moieties, such as -S-H, - OH, - COOH, and C = O were involved to increase As(III) sorption on thiol-functionalized biochars. This study highlights that thiol-grafting on both biochars, notably on SCB-BC, enhanced their ability to remove As(III) from water, which can be used as an effective technique for the treatment of As from drinking water.
利用生物废弃物生产生物炭来去除水中的潜在有毒元素,代表了水生生态系统净化的一个重要途径。在这里,我们探索了巯基功能化对甘蔗渣生物炭(Th/SCB-BC)和稻壳生物炭(Th/RH-BC)的重要性,以增强它们从水中去除亚砷酸盐(As(III))的能力,并将其与原始生物炭(SCB-BC 和 RH-BC)的效率进行了比较。与 SCB-BC 和 RH-BC(分别为 1.51 和 1.40 mg g)相比,Th/SCB-BC 和 Th/RH-BC 的最大 As(III)吸附量分别为 2.88 和 2.51 mg g。相对地,在 pH 7 时,Th/SCB-BC 和 Th/RH-BC 的 As(III)去除率分别为 92%和 83%,而在初始 As(III)浓度为 6 mg L、接触时间为 2 h 和 1 g L 吸附剂剂量时,原始 SCB-BC 和 RH-BC 的去除率分别为 65%和 55%。Langmuir(R = 0.99)等温线和准二级动力学(R = 0.99)模型对 As(III)吸附数据提供了最佳拟合。解吸实验表明,生物炭的再生能力降低,其顺序为 Th/SCB-BC(88%)>Th/RH-BC(82%)>SCB-BC(77%)>RH-BC(69%),可达三个吸附-解吸循环。傅里叶变换红外光谱和 X 射线光电子能谱结果表明,巯基(-S-H)官能团成功地接枝在两种生物炭的表面上,从而有助于增强水中 As(III)的去除。光谱数据表明,表面官能团,如-S-H、-OH、-COOH 和 C = O,参与了增加巯基功能化生物炭对 As(III)的吸附。这项研究强调了在两种生物炭上,特别是在 SCB-BC 上进行巯基接枝,增强了它们从水中去除 As(III)的能力,这可以作为一种从饮用水中去除 As 的有效技术。