Xu Menglong, Liu Yazi, Deng Yan, Zhang Siyuan, Hao Xiaodong, Zhu Ping, Zhou Jieyi, Yin Huaqun, Liang Yili, Liu Hongwei, Liu Xueduan, Bai Lianyang, Jiang Luhua, Jiang Huidan
School of Minerals Processing and Bioengineering, Central South University Changsha 410083 China
Hunan Biotechnology Research Institute, Hunan Academy of Agricultural Sciences Changsha 410125 China
RSC Adv. 2020 Jul 10;10(44):26090-26101. doi: 10.1039/d0ra03935g. eCollection 2020 Jul 9.
Cadmium (Cd) pollution poses a serious risk to human health and ecological security. Bioremediation can be a promising and effective remediation technology for treating Cd contaminated soils. In this study, seven heterotrophic strains were isolated from Cd contaminated soil and 7 autotrophic strains were isolated from acid mine drainage. Cd removal efficiencies were compared after leaching with autotrophic bacteria (Att-sys), heterotrophic isolates (Htt-sys) and cooperative leaching systems (Co-sys) in laboratory agitating reactors. The results indicated that Cd removal efficiency of Co-sys (32.09%) was significantly higher than that of Att-sys (23.24%) and Htt-sys (0.74%). By analyzing the soil microbial community in different bioleaching systems, we found that the addition of heterotrophic isolates significantly promoted the growth of some heavy metal resistant inhabitants (, , , ), and Co-sys had a minor effect on the growth of soil indigenous microbes. In Co-sys, the content of the four Cd fractions all decreased compared with other leaching systems. The analysis of soil physicochemical parameters during the leaching process showed that pH and ORP (oxidation reduction potential) were not the only determinants for Cd removal efficiency in Co-sys, synergistic metabolic activities of autotrophic and heterotrophic strains may be other determinants. This study demonstrated that cooperative bioremediation may prove to be a safe and efficient technique for field application in heavy metal soil pollution.
镉(Cd)污染对人类健康和生态安全构成严重风险。生物修复可能是一种有前景且有效的修复技术,用于处理镉污染土壤。在本研究中,从镉污染土壤中分离出7株异养菌株,从酸性矿山排水中分离出7株自养菌株。在实验室搅拌反应器中,比较了自养细菌浸出系统(Att-sys)、异养分离株浸出系统(Htt-sys)和协同浸出系统(Co-sys)浸出后的镉去除效率。结果表明,Co-sys的镉去除效率(32.09%)显著高于Att-sys(23.24%)和Htt-sys(0.74%)。通过分析不同生物浸出系统中的土壤微生物群落,我们发现添加异养分离株显著促进了一些重金属抗性微生物( 、 、 、 )的生长,而Co-sys对土壤原生微生物的生长影响较小。在Co-sys中,与其他浸出系统相比,四种镉形态的含量均有所下降。浸出过程中土壤理化参数分析表明,pH和氧化还原电位(ORP)不是Co-sys中镉去除效率的唯一决定因素,自养和异养菌株的协同代谢活动可能是其他决定因素。本研究表明,协同生物修复可能是一种安全有效的技术,可用于重金属土壤污染的现场应用。