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Removal of Microcystis aeruginosa and control of algal organic matters by potassium ferrate(Ⅵ) pre-oxidation enhanced Fe(Ⅱ) coagulation

机译:高铁酸钾(Ⅵ)预氧化增强Fe(Ⅱ)混凝去除铜绿微囊藻及控制藻类有机物

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The problem of cyanobacteria blooms during potable water production has generated wide concern. Ferrate(VI) serving as a pre-oxidation tactic was first applied to enhance conventional Fe(II) coagulation for Microcystis aeruginosa-laden water treatment at lab scale. Results demonstrated that ferrate(VI) pre-oxidation could successfully destabilize algae cells through destroying the protective organic layer. The residual ferrate(VI) together with post-added Fe(II) could provoke a comproportionation reaction, where large amounts of Fe hydrolyzates [Fe(OH)(3)] are formed. The in-situ Fe(OH)(3) with abundant reactive surface is responsible for the promotion of flocs growth by facilitating the clustering and cross-linking of algal organic matters (AOM) and cyanobacteria cells, simultaneously resulting in satisfactory reductions in OD680, turbidity and UV254. Overdose of ferrate(VI) could cause severe cell destruction along with the release of intracellular organic matter (IOM), which may impair the water quality by increasing the concentration of dissolved organic carbon (DOC) and the disinfection by-products formation potential (DBPFP). Meanwhile, considering the Fe residual in settled water, the optimal ferrate(VI) dose (20 mu M) and Fe(II) dose (80 mu M) were proposed. Besides, the synergistic effect of both the degradation by ferrate(VI) and the adsorption by in-situ Fe(OH)(3) contributed to the removal of DOC and Microcystin-LR. This study suggests that ferrate(VI) might be a potential candidate for pre-treatment to assist Fe(II) coagulation when addressing algae-laden water.
机译:饮用水生产过程中的蓝细菌开花问题已引起广泛关注。首先采用高铁酸盐(VI)作为预氧化策略,以增强实验室规模的铜绿微囊藻负载水处理的常规Fe(II)混凝。结果表明高铁酸盐(VI)的预氧化可以通过破坏保护性有机层来成功破坏藻类细胞的稳定性。残留的高铁酸盐(VI)与后添加的铁(II)可能会引起歧化反应,从而形成大量的铁水解物[Fe(OH)(3)]。具有丰富活性表面的原位Fe(OH)(3)通过促进藻类有机物(AOM)和蓝细菌细胞的聚集和交联,促进絮凝物的生长,同时导致OD680的降低令人满意,浊度和UV254。高剂量的高铁酸盐(VI)可能导致严重的细胞破坏以及细胞内有机质(IOM)的释放,这可能通过增加溶解有机碳(DOC)的浓度和消毒副产物的形成潜力(DBPFP)来损害水质。 )。同时,考虑到沉淀水中的铁残留,提出了最佳铁酸盐(VI)剂量(20μM)和铁(II)剂量(80μM)。此外,高铁酸盐(VI)降解和原位Fe(OH)(3)吸附的协同作用有助于去除DOC和微囊藻毒素-LR。这项研究表明,高铁酸盐(VI)可能是预处理的潜在候选物,当处理含藻类的水时有助于铁(II)的凝结。

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