State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
Colloids Surf B Biointerfaces. 2018 May 1;165:83-91. doi: 10.1016/j.colsurfb.2018.02.020. Epub 2018 Feb 13.
Adhesion of bacteria onto minerals is a ubiquitous process that plays a central role in many biogeochemical, microbiology and environmental processes in soil and sediment. Although bacterial adhesion onto soil minerals such as phyllosilicates and Fe-oxides have been investigated extensively, little is known about the mechanisms for bacterial attachment onto Al-oxides. Here, we explored the adhesion of Bacillus subtilis onto gibbsite (γ-AlOOH) under various ionic strengths (1, 10, 50, and 100 mM NaCl) and pHs (pH 4, 7, and 9) by in-situ attenuated total reflectance Fourier transform infrared (ATR-FTIR) spectroscopy. The time evolution of the peak intensities of the attached bacteria suggested that the adhesion underwent an initial rapid reaction followed by a slow pseudo-first-order kinetic stage. Spectral comparison between the attached and free cells, together with the interaction energy calculated with the Derjaguin, Landau, Verwey, and Overbeek (DLVO) theory and the micro-morphology of bacteria-gibbsite complexes, indicated that both electrostatic and chemical (bacterial groups such as phosphate and carboxyl covalently bind to gibbsite) interactions participated in the adhesion processes. Both solution ionic strength (IS) and pH impacted the spectra of attached bacteria, but the peak intensity of different bands changed differently with these two factors, showing a preferential adhesion of surface groups (phosphate, carboxyl, and amide groups) on gibbsite at different conditions. The diverse responses to IS and pH alteration of the forces (chemical bonds, electrostatic attractions, and the hydrophobic interactions) that essentially govern the adhesion might be responsible for the preferential adhesion. These results may help to better understand how bacteria adhere onto soil oxides at molecular scales.
细菌在矿物上的黏附是一种普遍存在的过程,在土壤和沉积物中的许多生物地球化学、微生物学和环境过程中起着核心作用。尽管已经广泛研究了细菌在诸如层状硅酸盐和 Fe 氧化物等土壤矿物上的黏附,但对于细菌在 Al 氧化物上的附着机制知之甚少。在这里,我们通过原位衰减全反射傅里叶变换红外(ATR-FTIR)光谱法研究了枯草芽孢杆菌在各种离子强度(1、10、50 和 100 mM NaCl)和 pH 值(pH 4、7 和 9)下在水铝石(γ-AlOOH)上的黏附。附着细菌的峰强度随时间的变化表明,附着过程经历了初始快速反应,然后是缓慢的拟一级动力学阶段。附着和游离细胞之间的光谱比较,以及用德加古因、朗道、维韦尔和奥弗贝克(DLVO)理论计算的相互作用能以及细菌-水铝石复合物的微观形态,表明静电和化学(如磷酸盐和羧基共价结合到水铝石的细菌基团)相互作用都参与了附着过程。溶液离子强度(IS)和 pH 都影响附着细菌的光谱,但不同波段的峰强度随这两个因素的变化方式不同,表明在不同条件下,水铝石表面基团(磷酸盐、羧基和酰胺基团)具有优先黏附性。控制附着的力(化学键、静电吸引和疏水力)对 IS 和 pH 变化的不同响应可能是导致优先附着的原因。这些结果可能有助于更好地了解细菌如何在分子尺度上黏附在土壤氧化物上。