Du Huihui, Qu ChenChen, Liu Jing, Chen Wenli, Cai Peng, Shi Zhihua, Yu Xiao-Ying, Huang Qiaoyun
State Key Laboratory of Agricultural Microbiology, Huazhong Agricultural University, Wuhan 430070, China; Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtze River), Ministry of Agriculture, College of Resources and Environment, Huazhong Agricultural University, Wuhan 430070, China; College of Resources and Environment, Hunan Agricultural University, Changsha 410128, China.
State Key Laboratory of Agricultural Microbiology, Huazhong Agricultural University, Wuhan 430070, China; Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtze River), Ministry of Agriculture, College of Resources and Environment, Huazhong Agricultural University, Wuhan 430070, China.
Environ Pollut. 2017 Oct;229:871-878. doi: 10.1016/j.envpol.2017.07.052. Epub 2017 Jul 25.
Bacteria-phyllosilicate complexes are commonly found in natural environments and are capable of immobilizing trace metals. However, the molecular binding mechanisms of heavy metals to these complex aggregates still remain poorly understood. This study investigated Cd adsorption on Gram-positive Bacillus subtilis, Gram-negative Pseudomonas putida and their binary mixtures with montmorillonite using surface complexation model, Cd K-edge extended X-ray absorption fine structure (EXAFS) spectroscopy and isothermal titration calorimetry (ITC). We have shown that larger amounts of Cd are adsorbed by B. subtilis than by P. putida at pH<∼6, and Cd sorption that binding to phosphate groups plays a more important role in P. putida than in B. subtilis. This remind us that we should consider the microbe species when predict the biochemical behavior of trace metals in microbe-bearing environments. The observed Cd adsorption on the binary bacteria-clay composites was more than that predicted based on the component additivity approach. When taking bacteria-clay (1:1 mass ratio) as a representative example, an approximately 68%:32% metal distribution between the bacterial and mineral fraction was found. Both the EXAFS and ITC fits showed that the binding stoichiometry for Cd-carboxyl/phosphate was smaller in the binary mixtures than that in pure bacteria. We proposed that the significant deviations were possibly due to the physical-chemical interaction between the composite fractions that might reduce the agglomeration of the clay grains, increase the negative surface charges, and provide additional bridging of metals ions between bacterial cells and clays.
细菌-层状硅酸盐复合物在自然环境中普遍存在,并且能够固定痕量金属。然而,重金属与这些复合聚集体的分子结合机制仍知之甚少。本研究使用表面络合模型、Cd K边扩展X射线吸收精细结构(EXAFS)光谱和等温滴定量热法(ITC),研究了革兰氏阳性枯草芽孢杆菌、革兰氏阴性恶臭假单胞菌及其与蒙脱石的二元混合物对镉的吸附。我们发现,在pH<∼6时,枯草芽孢杆菌比恶臭假单胞菌吸附的镉更多,并且在恶臭假单胞菌中,与磷酸基团结合的镉吸附比在枯草芽孢杆菌中发挥更重要的作用。这提醒我们,在预测含微生物环境中痕量金属的生化行为时应考虑微生物种类。观察到的二元细菌-粘土复合物对镉的吸附量超过了基于组分加和法预测的吸附量。以细菌-粘土(质量比1:1)作为代表性例子,发现细菌和矿物部分之间的金属分布约为68%:32%。EXAFS和ITC拟合均表明,二元混合物中Cd-羧基/磷酸盐的结合化学计量比小于纯细菌中的结合化学计量比。我们认为,显著偏差可能是由于复合组分之间的物理化学相互作用,这可能会减少粘土颗粒的团聚,增加表面负电荷,并在细菌细胞和粘土之间提供额外的金属离子桥接。