利用聚乙烯醇和海藻酸钠制备了硫酸盐还原菌微球,探讨了Zn2+、Cu2+、乙酸钠、草酸钠和柠檬酸钠对其还原U(Ⅵ)的影响,考察了其选择性去除U(Ⅵ)的工艺。实验结果表明,当Zn2+或Cu2+浓度低于100mg/L时,U(Ⅵ)还原未受显著影响,但当其增至150mg/L时,U(Ⅵ)还原被完全抑制。当单齿配体有机物(乙酸钠)存在时,U(Ⅵ)可被彻底还原;而多齿配体有机物(草酸钠和柠檬酸钠)存在时,会延缓甚至完全抑制U(Ⅵ)的还原。对于无机-U(Ⅵ)-重金属体系,可利用U(Ⅵ)和硫酸盐还原自由能的差异,适当降低COD/SO2-4比值直接选择性去除U(Ⅵ);对于有机-U(Ⅵ)-重金属体系,可通过多齿配体有机物络合U(Ⅵ),同时利用硫化物选择性沉淀重金属,间接实现U(Ⅵ)的选择性去除。
The sulfate-reducing bacteria immobilized in polyvinyl alcohol-sodium alginate beads were prepared .The impacts of Zn2+ ,Cu2+ ,acetate ,oxalate and citrate on the reduction of U (Ⅵ ) were investigated .Furthermore ,selective removal of U (Ⅵ ) or heavy metals was assessed .The results indicate that the existing of Zn2+ or Cu2+doesn’t affect U (Ⅵ) removal appreciably w hen their concentrations are less than 100 mg/L ,but they can inhibit U (Ⅵ) removal completely w hile their concentrations reach 150 mg/L .In the presence of monodentate ligand (acetate) ,U (Ⅵ) can be removed readily ,w hereas multidentate ligands (oxalate and citrate ) impose an inhibition on U (Ⅵ ) removal .In organic-free wastewater ,direct selective removal of U (Ⅵ ) can be achieved based on thermodynamic considerations and optimized by appropriately lowering COD/SO2 -4 .In wastewater containing multidentate organics ,U(Ⅵ) can be firstly complexed during precipitation of Zn2+ and Cu2+ , and then removed directively after degradation of organic ligands .