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Effects of Energy Source Concentration on Bioleaching of Heavy Metals from Undigested Sewage Sludge by Using Iron-Oxidizing Bacterium

机译:能源浓度对铁氧化细菌对未消化污水污泥中重金属生物浸出的影响

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摘要

The objective of the present study was to optimize the energy source addition required for bioleaching of heavy metals from undigested sewage sludge after secondary treatment. Bioleaching was conducted in a batch system with both inoculation of iron-oxidizing bacteria and the addition of FeSO_4·7H_2O in the range of 0-17.5 g L~(-1). The results showed that the pH of the sludge decreased with an increase in the ferrous iron concentrations and reached the maximum acidity of pH 2.1-3.0 for treatments receiving both bacterial inoculation and substrate addition. This led to a significant solubilization of metals from the solids fraction of sewage sludge. However, solubilization behavior differed for different metal species. Solubilization of Zn was not affected by the concentration of the substrate in the range of 7.5-17.5 gL~(-1), whereas solubilization of Cu and Cr was highly dependent on substrate concentration. After 10 days of bioleaching the following heavy metal solubilization efficiencies were obtained: Zn 100%, Cu 83-98%, and Cr 9-75%. In contrast, no obvious solubilization of Cu and Cr occurred except that less than 20% of Zn was leached out in the control without substrate addition. The result from the present study showed that 10 g L~(-1) of substrate was sufficient to provide an optimum bioleaching condition. However, the biomass reduction rate was far below the criteria for sludge stabilization and thus, a further stabilization process is necessary prior to land application of the bioleached sludge.
机译:本研究的目的是优化二次处理后从未消化的污水污泥中生物浸出重金属所需的能源补充。在分批系统中进行生物浸提,同时接种铁氧化细菌并添加0-17.5 g L〜(-1)范围的FeSO_4·7H_2O。结果表明,污泥的pH值随着亚铁浓度的增加而降低,并且在接受细菌接种和添加底物的处理中,其最大酸度达到pH 2.1-3.0。这导致金属从污水污泥的固体部分中大量溶解。但是,对于不同的金属种类,增溶行为不同。锌的增溶不受基质浓度在7.5-17.5 gL〜(-1)范围内的影响,而铜和铬的增溶高度依赖于基质浓度。经过10天的生物浸提后,获得了以下重金属溶解效率:Zn 100%,Cu 83-98%和Cr 9-75%。相反,除了在没有添加底物的对照中浸出少于20%的Zn外,没有发生明显的Cu和Cr的溶解。本研究的结果表明,10 g L〜(-1)的底物足以提供最佳的生物浸出条件。然而,生物量的减少率远低于污泥稳定的标准,因此,在土地上施用生物浸出污泥之前,需要进一步的稳定过程。

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