Han Jie, Huang Xin, Yang Kun-Lun, Song Chao-Fan, Miao Heng-Feng
School of Environmental & Civil Engineering, Jiangnan University, Wuxi 214122, China.
Jiangsu Key Laboratory of Anaerobic Biotechnology, Wuxi 214122, China.
Huan Jing Ke Xue. 2023 Nov 8;44(11):6181-6193. doi: 10.13227/j.hjkx.202212092.
To alleviate the problems of eutrophication and blue algae accumulation in water, biochar was prepared from blue algae dehydrated using polymerized ferrous sulfate(PFS) to absorb phosphate in water, and the biochar was activated using steam to adjust the pore structure. The preparation conditions of blue algae biochar were optimized using the response surface method. The optimal results were as follows:the dosage of PFS was 458 mg·L, the carbonization temperature was 433℃, and the mass ratio of biochar precursor to steam was 1:11. Biochar without PFS(FH-433) and biochar with PFS(FH-433) were characterized using X-ray diffraction(XRD), Fourier-transform infrared spectroscopy(FTIR), zeta potential, and Raman spectra(Raman) were used to study whether blue algae biochar and PFS had a synergic effect on phosphate removal. The results showed that:compared with FH-433, iron oxide appeared on the surface, the zero point of charge(pH) increased from 4.41 to 6.19, and the disorder and defect degree of biochar was increased in FH-433. The pseudo-second-order model and Langmuir model were suitable for describing the adsorption process of FH-433, and the saturated adsorption capacity was 31.97 mg·g. FH-433 had excellent phosphorus removal efficiency in actual lake water, and the residual phosphate content of effluent was less than 0.025 mg·L. In the presence of several common anions, it still showed excellent selective adsorption. After five cycles, the phosphate removal of FH-433 still reached 75.78%, indicating that FH-433 had the characteristic of being renewable. Combined with the material characterization results before and after adsorption, the phosphorus removal mechanism of FH-433 mainly involved electrostatic attraction and ligand exchange.
为缓解水体富营养化和蓝藻堆积问题,利用聚合硫酸铁(PFS)对蓝藻进行脱水处理以制备生物炭,用于吸附水中的磷酸盐,并用蒸汽对生物炭进行活化以调节其孔隙结构。采用响应面法优化蓝藻生物炭的制备条件。优化结果如下:PFS投加量为458 mg·L,碳化温度为433℃,生物炭前驱体与蒸汽的质量比为1:11。采用X射线衍射(XRD)、傅里叶变换红外光谱(FTIR)、zeta电位和拉曼光谱(Raman)对未添加PFS的生物炭(FH - 433)和添加PFS的生物炭(FH - 433)进行表征,研究蓝藻生物炭与PFS对磷酸盐去除是否具有协同作用。结果表明:与FH - 433相比,FH - 433表面出现了氧化铁,电荷零点(pH)从4.41增加到6.19,生物炭的无序度和缺陷度增加。准二级模型和朗缪尔模型适用于描述FH - 433的吸附过程,饱和吸附容量为31.97 mg·g。FH - 433在实际湖水中具有优异的除磷效率,出水残余磷酸盐含量小于0.025 mg·L。在几种常见阴离子存在的情况下,它仍表现出优异的选择性吸附。经过五个循环后,FH - 433的磷酸盐去除率仍达到75.78%,表明FH - 433具有可再生的特性。结合吸附前后的材料表征结果,FH - 433的除磷机理主要涉及静电吸引和配体交换。