School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou 310012, China; Zhejiang Provincial Key Laboratory of Solid Waste Treatment and Recycling, Hangzhou 310012, China.
School of Environmental Science and Engineering, Zhejiang Gongshang University, Hangzhou 310012, China; Zhejiang Provincial Key Laboratory of Solid Waste Treatment and Recycling, Hangzhou 310012, China.
Sci Total Environ. 2023 Jun 1;875:162652. doi: 10.1016/j.scitotenv.2023.162652. Epub 2023 Mar 7.
The char component of biochar can act as an electron shuttle and redox agent to accelerate the transformation of ferrihydrite, but how the silicon component of biochar affects ferrihydrite transformation and pollutant removal remains unclear. In this paper, infrared spectroscopy, electron microscopy, transformation experiments and batch sorption experiments were conducted to examine a 2-line ferrihydrite formed by alkaline precipitation of Fe on a rice straw-derived biochar. Fe-O-Si bonds were developed between the precipitated ferrihydrite particles and biochar silicon component, increasing mesopore volume (for mesopores with diameters of 10-100 nm) and surface area of ferrihydrite as the Fe-O-Si formation probably alleviated the aggregation of ferrihydrite particles. The Fe-O-Si bonding-contributed interactions blocked the transformation to goethite for ferrihydrite precipitated on biochar in a 30-day ageing and a 5-day Fe catalysis ageing. Moreover, there was an increase of oxytetracycline adsorption capacity onto ferrihydrite-loaded biochar, which reached amazingly 3460 mg/g at the maximum, due to the Fe-O-Si bonding-contributed increase of surface area and oxytetracycline coordination sites. Ferrihydrite-loaded biochar as a soil amendment enhanced oxytetracycline adsorption and reduced the bacterial toxicity of dissolved oxytetracycline better than ferrihydrite did. These results provide new perspectives for the role of biochar (especially its silicon component) as an iron-based material carrier and a soil additive in the environmental effects of iron (hydr) oxides in water and soil.
生物炭的碳成分可以作为电子穿梭体和氧化还原试剂,加速水铁矿的转化,但生物炭的硅成分如何影响水铁矿的转化和污染物去除仍不清楚。本文通过红外光谱、电子显微镜、转化实验和批量吸附实验,研究了一种由稻草衍生生物炭上碱性沉淀铁形成的 2 线水铁矿。沉淀的水铁矿颗粒与生物炭硅成分之间形成了 Fe-O-Si 键,增加了中孔体积(中孔直径为 10-100nm)和水铁矿的比表面积,因为 Fe-O-Si 的形成可能缓解了水铁矿颗粒的聚集。Fe-O-Si 键合贡献的相互作用阻止了水铁矿向针铁矿的转化,这在 30 天老化和 5 天 Fe 催化老化过程中都是如此。此外,由于 Fe-O-Si 键合贡献的表面积和土霉素配位位点的增加,负载水铁矿的生物炭对土霉素的吸附容量增加,在最大程度上达到了惊人的 3460mg/g。负载水铁矿的生物炭作为土壤改良剂,增强了土霉素的吸附,降低了溶解土霉素的细菌毒性,效果优于水铁矿。这些结果为生物炭(特别是其硅成分)作为铁基材料载体和土壤添加剂在水和土壤中铁(氢)氧化物的环境效应中提供了新的视角。