Ali Babeker Tawasul Mohammed, Khalil Mohamed N, Fayad Eman, Alshaya Dalal Sulaiman, Elsaid Fahmy Gad, Elhassan Itmad Awad
Department of Chemistry, Industrial Research and Consultancy Center, Ministry of Industry, Khartoum 11111, Sudan.
School of Environment Science and Engineering, Donghua University, Shanghai 201620, P.R. China.
Environ Res. 2025 Jul 3:122282. doi: 10.1016/j.envres.2025.122282.
Biochar is a remarkable adsorbent for environmental pollutants. However, their applicability is hindered by specific deficiencies, including restricted adsorption capacity, inadequate selectivity, and low reusability. For instance, carrageenan gum pure biochar (BC CA300) exhibits inadequate Cu (II) adsorption performance owing to the weakly binding surface functional groups. Physical modification consumes energy, while chemical modification heavily uses chemicals, causing environmental harm. Herein, a novel modifying agent was developed that can selectively and efficiently adsorb Cu (II). The BC CA300 surface was grafted with olivine mineral (Mg, Fe) SiO through a one-pot hydrothermal carbonization (HTC) technique. The engineered biochar (BC CAOL) was investigated for the synergistic effect of K(I), Mg (II), Fe (II), Fe (III), and Si (IV) from the viewpoints of adsorption kinetics, isotherm, and thermodynamics alongside DFT calculations and electrostatic potential (ESP) mapping. The surface structure of BC CA300 and BC CAOL was examined and compared through BET, FTIR, XPS, and SEM-EDS. It was found that engineered biochar adsorption capacity (340.98 mg g) was 4.7 times greater than that of pure biochar (72.51 mg g). The adsorption energy of engineered biochar is 2.5 times greater than that of pure biochar. The synergistic effect is indicative of the following sequence: K > Fe > O > Si > Mg. Hence, the Cu (II) adsorption mechanism is primarily driven by precipitation > complexation > chelation > ion exchange, beside the pore-filling mechanism. This research highlights the potential of gum-mineral composite biochar as a green, effective, and selective alternative for Cu (II)-laden wastewater decontamination.
生物炭是一种用于吸附环境污染物的卓越吸附剂。然而,其应用受到一些特定缺陷的阻碍,包括吸附容量受限、选择性不足和可重复使用性低。例如,由于表面官能团结合力较弱,卡拉胶纯生物炭(BC CA300)对铜(II)的吸附性能不足。物理改性消耗能源,而化学改性大量使用化学物质,会对环境造成危害。在此,开发了一种新型改性剂,它能够选择性且高效地吸附铜(II)。通过一锅水热碳化(HTC)技术将橄榄石矿物(Mg, Fe)SiO接枝到BC CA300表面。从吸附动力学、等温线和热力学的角度,结合密度泛函理论(DFT)计算和静电势(ESP)映射,研究了工程生物炭(BC CAOL)中钾(I)、镁(II)、铁(II)、铁(III)和硅(IV)的协同效应。通过比表面积分析仪(BET)、傅里叶变换红外光谱仪(FTIR)、X射线光电子能谱仪(XPS)和扫描电子显微镜 - 能谱仪(SEM - EDS)对BC CA300和BC CAOL的表面结构进行了检测和比较。结果发现,工程生物炭的吸附容量(340.98 mg/g)是纯生物炭(72.51 mg/g)的4.7倍。工程生物炭的吸附能比纯生物炭大2.5倍。协同效应的顺序如下:K > Fe > O > Si > Mg。因此除了孔隙填充机制外,铜(II)的吸附机制主要由沉淀 > 络合 > 螯合 > 离子交换驱动。本研究突出了胶 - 矿物复合生物炭作为处理含铜(II)废水的绿色、有效且选择性的替代品的潜力。