Ye Maoyou, Yan Pingfang, Sun Shuiyu, Han Dajian, Xiao Xiao, Zheng Li, Huang Shaosong, Chen Yun, Zhuang Shengwei
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China; Key Laboratory of Mining and Metallurgy Industry Heavy Metals Pollution Control of Environmental Protection of Guangdong Province, Guangzhou 510006, China.
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, China; Guangdong Polytechnic College of Environmental Protection Engineering, Foshan 528216, China; Key Laboratory of Mining and Metallurgy Industry Heavy Metals Pollution Control of Environmental Protection of Guangdong Province, Guangzhou 510006, China.
Chemosphere. 2017 Feb;168:1115-1125. doi: 10.1016/j.chemosphere.2016.10.095. Epub 2016 Nov 22.
During the process of bioleaching, lead (Pb) recovery is low. This low recovery is caused by a problem with the bioleaching technique. This research investigated the bioleaching combination of bioleaching with brine leaching to remove heavy metals from lead-zinc mine tailings. The impact of different parameters were studied, including the effects of initial pH (1.5-3.0) and solid concentration (5-20%) for bioleaching, and the effects of sodium chloride (NaCl) concentration (10-200 g/L) and temperature (25 and 50 °C) for brine leaching. Complementary characterization experiments (Sequential extraction, X-ray diffractometer (XRD), scanning electronic microscope (SEM)) were also conducted to explore the transformation of tailings during the leaching process. The results showed that bioleaching efficiency was significantly influenced by initial pH and solid concentration. Approximately 85.45% of iron (Fe), 4.12% of Pb, and 97.85% of zinc (Zn) were recovered through bioleaching in optimum conditions. Increasing the brine concentration and temperature promoted lead recovery. Lead was recovered from the bioleaching residues at a rate of 94.70% at 25 °C and at a rate of 99.46% at 50 °C when the NaCl concentration was 150 g/L. The study showed that bioleaching significantly changed the speciation of heavy metals and the formation and surface morphology of tailings. The metals were mainly bound in stable fractions after bioleaching.
在生物浸出过程中,铅(Pb)的回收率较低。这种低回收率是由生物浸出技术的问题导致的。本研究调查了生物浸出与盐水浸出相结合以从铅锌矿尾矿中去除重金属的方法。研究了不同参数的影响,包括生物浸出时初始pH值(1.5 - 3.0)和固体浓度(5 - 20%)的影响,以及盐水浸出时氯化钠(NaCl)浓度(10 - 200 g/L)和温度(25和50°C)的影响。还进行了补充表征实验(顺序提取、X射线衍射仪(XRD)、扫描电子显微镜(SEM))以探索浸出过程中尾矿的转变。结果表明,生物浸出效率受初始pH值和固体浓度的显著影响。在最佳条件下,通过生物浸出可回收约85.45%的铁(Fe)、4.12%的铅和97.85%的锌(Zn)。提高盐水浓度和温度可促进铅的回收。当NaCl浓度为150 g/L时,在25°C下从生物浸出残渣中回收铅的速率为94.70%,在50°C下为99.46%。研究表明,生物浸出显著改变了重金属的形态以及尾矿的形成和表面形态。生物浸出后,金属主要以稳定形态存在。