Key Laboratory of Yangtze River Water Environment, Ministry of Education, College of Environmental Science and Engineering, Institute of Eco-Environmental Engineering, Tongji University, Shanghai 200092, China.
Power China Huadong Engineering Corporation Limited, Hangzhou 311122, China.
J Hazard Mater. 2024 Nov 5;479:135746. doi: 10.1016/j.jhazmat.2024.135746. Epub 2024 Sep 4.
Heavy metal contamination in sediment has become a significant global environmental challenge. Numerous studies have demonstrated the effectiveness of modified biochar to solve heavy metal contamination in sediment. However, the modification process with complex methods and expensive modifiers prevented its large-scale application. In this study, an N self-doped biochar was obtained by pyrolysis of Spirulina sp. (SBC). Meanwhile, the KCO impregnation method was utilized to prepare Spirulina sp. biochar (KSBC), which demonstrated a higher specific surface area (874 m/g) and richer O, N functional groups. The adsorption capacity of KSBC550-120 for Cu (Ⅱ), Zn (Ⅱ), and Cd (Ⅱ) was 57.9 ± 0.3 mg/g, 43.6 ± 0.7 mg/g, and 63.9 ± 0.6 mg/g, respectively. The adsorption process is primarily governed by chemical processes, mainly through ion exchange, surface complexation, dissolution-precipitation, electrostatic interactions, adsorption-reduction, and cation-π interactions. Moreover, utilizing KSBC550-120 for mixing or capping effectively reduced heavy metal concentrations in both the overlying and pore water of the sediments. 1.0 wt% KSBC550-120 with capping treatment significantly reduced the release of heavy metals from the sediment by 80.3-91.9%. This study provides effective theoretical support for re-utilizing waste algal residues and remediation of the heavy metal-contaminated river and lake sediments using microalgae biochar.
重金属污染在沉积物中已经成为一个全球性的重大环境挑战。大量研究表明,改性生物炭可以有效地解决沉积物中的重金属污染问题。然而,由于改性过程涉及复杂的方法和昂贵的改性剂,限制了其大规模应用。本研究利用螺旋藻(SBC)热解制备了一种 N 自掺杂生物炭(SBC)。同时,采用 KCO 浸渍法制备了螺旋藻生物炭(KSBC),其比表面积更高(874 m/g),富含 O、N 官能团。KSBC550-120 对 Cu(Ⅱ)、Zn(Ⅱ)和 Cd(Ⅱ)的吸附容量分别为 57.9 ± 0.3、43.6 ± 0.7 和 63.9 ± 0.6 mg/g。吸附过程主要由化学过程控制,主要通过离子交换、表面络合、溶解沉淀、静电相互作用、吸附还原和阳离子-π 相互作用等方式进行。此外,利用 KSBC550-120 进行混合或包膜处理可以有效地降低沉积物中上层和孔隙水中的重金属浓度。1.0 wt% KSBC550-120 包膜处理可使重金属从沉积物中的释放量降低 80.3-91.9%。本研究为利用微藻生物炭再利用废藻渣和修复受重金属污染的河流和湖泊沉积物提供了有效的理论支持。