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污水污泥生物沥滤过程中重金属形态的转化

Transformation of heavy metal forms during sewage sludge bioleaching.

作者信息

Chen Ying-Xu, Hua Yu-Mei, Zhang Shao-Hui, Tian Guang-Ming

机构信息

Department of Environmental Engineering, Zhejiang University, Hangzhou 310029, PR China.

出版信息

J Hazard Mater. 2005 Aug 31;123(1-3):196-202. doi: 10.1016/j.jhazmat.2005.03.047.

Abstract

The transformation of heavy metal forms during sewage sludge bioleaching with elemental sulfur as substrate was investigated. The sequential selective extraction procedure was an effective way to reflect the variation in heavy metal forms. The exchangeable form of Cu, Pb and Zn after bioleaching accounted for 81.6, 40.2 and 75.8%, respectively. Cu at initial sludge mainly existed as sulfide precipitate form, most of which turned to exchangeable form during bioleaching, and was solubilized mostly by direct mechanism. The original forms of Pb and Zn were mainly carbonate precipitate and organically bound. Most of the carbonate precipitate Pb transformed into exchangeable form but a little of organically bound Pb. Pb was dissolved from the sludge due to transformation of carbonate precipitated and sulfide precipitated to exchangeable form by cooperation of both direct and indirect mechanisms. A majority of exchangeable Zn was transformed from organically bound and carbonate precipitated forms, and the bioleaching mechanism of Zn was mainly indirect. After bioleaching, the sewage sludge could be applied to land more safely because the heavy metals mainly existed in stable forms. The exchangeable Cu and Pb achieved an obvious increase at pH about 2, while exchangeable Zn showed higher percentage at pH about 3. The transformation of chemical forms for Cu had good relationship with ORP during bioleaching, but Zn was not influenced by ORP of sludge, which appeared to have high bioleaching efficiency at ORP less than 200 mV.

摘要

研究了以元素硫为底物进行污泥生物沥浸过程中重金属形态的变化。连续选择性提取法是反映重金属形态变化的有效方法。生物沥浸后,铜、铅和锌的可交换态分别占81.6%、40.2%和75.8%。初始污泥中的铜主要以硫化物沉淀形式存在,生物沥浸过程中大部分转化为可交换态,且大多通过直接机制溶解。铅和锌的原始形态主要是碳酸盐沉淀和有机结合态。大部分碳酸盐沉淀态铅转化为可交换态,而有机结合态铅只有少量转化。由于碳酸盐沉淀和硫化物沉淀通过直接和间接机制协同作用转化为可交换态,铅从污泥中溶解出来。大部分可交换态锌由有机结合态和碳酸盐沉淀态转化而来,锌的生物沥浸机制主要是间接机制。生物沥浸后,污泥中的重金属主要以稳定形态存在,因此可更安全地用于土地。在pH约为2时,可交换态铜和铅明显增加,而在pH约为3时,可交换态锌的比例更高。生物沥浸过程中铜的化学形态转化与氧化还原电位有良好的关系,但锌不受污泥氧化还原电位的影响,在氧化还原电位小于200 mV时生物沥浸效率较高。

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