Wu Hai-suo, Zhang Ai-qiang, Wang Lian-sheng
State Key Laboratory of Pollution Control and Resources Reuse, School of the Environment, Nanjing University, Nanjing 210093, China.
J Environ Sci (China). 2004;16(4):640-5.
Activated sludge was immobilized into Ca-alginate beads via entrapment, and biosorption of three heavy metal ions, copper(II), zinc(II), and chromimum(II), from aqueous solution in the concentration range of 10-100 mg/L was studied by using both entrapped activated sludge and inactivated free biomass at pH < or = 5. A biphasic metal adsorption pattern was observed in all immobilized biomass experiments. The biosorption of metal ions by the biosorbents increased with the initial concentration increased in the medium. The adsorption rate of immobilized pretreated activated sludge(PAS) was much lower than that of free PAS due to the increase in mass transfer resistance resulting from the polymeric matrix. Biosorption equilibrium of beads was established in about 20 h and the adsorbed heavy metal ions did not change further with time. No significant effect of temperature was observed in the test for free biomass while immobilized PAS appeared to be strong temperature dependent in the test range of 10 and 40 degrees C. Besides, the content of activated sludge in the calcium alginate bead has an influence on the uptake of heavy metals. The sorption equilibrium was well modeled by Langmuir isotherm, implying monomolecular adsorption mechanism. Carboxyl group in cell wall played an important role in surface adsorption of heavy metal ions on PAS.
通过包埋法将活性污泥固定在海藻酸钙珠粒中,在pH≤5的条件下,使用固定化活性污泥和灭活的游离生物质研究了从浓度范围为10 - 100 mg/L的水溶液中对三种重金属离子铜(II)、锌(II)和铬(II)的生物吸附。在所有固定化生物质实验中均观察到双相金属吸附模式。生物吸附剂对金属离子的生物吸附随着培养基中初始浓度的增加而增加。由于聚合物基质导致传质阻力增加,固定化预处理活性污泥(PAS)的吸附速率远低于游离PAS。珠粒的生物吸附平衡在约20小时内建立,吸附的重金属离子不会随时间进一步变化。在游离生物质的测试中未观察到温度的显著影响,而在10至40摄氏度的测试范围内,固定化PAS似乎强烈依赖温度。此外,海藻酸钙珠粒中活性污泥的含量对重金属的吸收有影响。吸附平衡通过朗缪尔等温线得到很好的模拟,这意味着单分子吸附机制。细胞壁中的羧基在PAS上重金属离子的表面吸附中起重要作用。