Li Xingjie, Li Dongbo, Yan Zhenning, Ao Yansong
School of Agriculture and Biology, Shanghai Jiao Tong University Shanghai 200240 China
RSC Adv. 2018 Sep 3;8(54):30902-30911. doi: 10.1039/c8ra06270f. eCollection 2018 Aug 30.
Plant growth-promoting rhizobacteria (PGPR) not only promote growth and heavy metal uptake by plants but are promising biosorbents for heavy metals remediation. However, there exist arguments over whether extracellular adsorption (biosorption) or intracellular accumulation (bioaccumulation) play dominant roles in Cd(ii) adsorption. Therefore, three cadmium-resistant PGPR, GX_5, sp. GX_15, and sp. GX_31 were used to study bioaccumulation and biosorption mechanisms under different initial Cd(ii) concentrations, using batch adsorption experiments, desorption experiments, scanning electron microscopy coupled with energy dispersive X-ray (SEM-EDX) spectroscopy, transmission electron microscopy (TEM), and Fourier-transform infrared (FTIR) spectroscopy. In this study, with the increase of the initial Cd(ii) concentrations, the removal efficiency of strains decreased and the adsorption capacity improved. The highest Cd(ii) removal efficiency values were 25.05%, 53.88%, and 86.06% for GX_5, GX_15, and GX_31 with 20 mg l of Cd(ii), while the maximum adsorption capacity values were 7.97, 17.13, and 26.43 mg g of GX_5, GX_15, and GX_31 with 100 mg l of Cd(ii). Meanwhile, the removal efficiency and adsorption capacity could be ordered as GX_31 > GX_15 > GX_5. The dominant adsorption mechanism for GX_5 was bioaccumulation (50.66-60.38%), while the dominant mechanisms for GX_15 and GX_31 were biosorptions (60.29-64.89% and 75.93-79.45%, respectively). The bioaccumulation and biosorption mechanisms were verified by SEM-EDX, TEM and FTIR spectroscopy. These investigations could provide a more comprehensive understanding of metal-bacteria sorption reactions as well as practical application in remediation of heavy metals.
植物促生根际细菌(PGPR)不仅能促进植物生长和对重金属的吸收,还是用于重金属修复的有前景的生物吸附剂。然而,关于细胞外吸附(生物吸附)或细胞内积累(生物累积)在镉(II)吸附中是否起主导作用存在争议。因此,使用三株耐镉PGPR,即GX_5、GX_15菌和GX_31菌,通过批量吸附实验、解吸实验、扫描电子显微镜结合能量色散X射线(SEM-EDX)光谱、透射电子显微镜(TEM)和傅里叶变换红外(FTIR)光谱,研究了不同初始镉(II)浓度下的生物累积和生物吸附机制。在本研究中,随着初始镉(II)浓度的增加,菌株的去除效率降低,吸附容量提高。对于GX_5、GX_15和GX_31,在镉(II)浓度为20 mg/L时,最高镉(II)去除效率分别为25.05%、53.88%和86.06%,而在镉(II)浓度为100 mg/L时,最大吸附容量分别为7.97、17.13和26.43 mg/g。同时,去除效率和吸附容量的顺序为GX_31 > GX_15 > GX_5。GX_5的主要吸附机制是生物累积(50.66 - 60.38%),而GX_