Biosciences Division, Argonne National Laboratory, Lemont, Illinois, United States of America.
Institute of Chemical Engineering, Bulgarian Academy of Sciences, Sofia, Bulgaria.
PLoS One. 2021 May 20;16(5):e0251883. doi: 10.1371/journal.pone.0251883. eCollection 2021.
Iron reduction and sulfate reduction are two of the major biogeochemical processes that occur in anoxic sediments. Microbes that catalyze these reactions are therefore some of the most abundant organisms in the subsurface, and some of the most important. Due to the variety of mechanisms that microbes employ to derive energy from these reactions, including the use of soluble electron shuttles, the dynamics between iron- and sulfate-reducing populations under changing biogeochemical conditions still elude complete characterization. Here, we amended experimental bioreactors comprised of freshwater aquifer sediment with ferric iron, sulfate, acetate, and the model electron shuttle AQDS (9,10-anthraquinone-2,6-disulfonate) and monitored both the changing redox conditions as well as changes in the microbial community over time. The addition of the electron shuttle AQDS did increase the initial rate of FeIII reduction; however, it had little effect on the composition of the microbial community. Our results show that in both AQDS- and AQDS+ systems there was an initial dominance of organisms classified as Geobacter (a genus of dissimilatory FeIII-reducing bacteria), after which sequences classified as Desulfosporosinus (a genus of dissimilatory sulfate-reducing bacteria) came to dominate both experimental systems. Furthermore, most of the ferric iron reduction occurred under this later, ostensibly "sulfate-reducing" phase of the experiment. This calls into question the usefulness of classifying subsurface sediments by the dominant microbial process alone because of their interrelated biogeochemical consequences. To better inform models of microbially-catalyzed subsurface processes, such interactions must be more thoroughly understood under a broad range of conditions.
铁还原和硫酸盐还原是缺氧沉积物中发生的两种主要生物地球化学过程。因此,催化这些反应的微生物是地下最丰富的生物之一,也是最重要的生物之一。由于微生物从这些反应中获取能量的机制多种多样,包括使用可溶性电子穿梭体,因此在不断变化的生物地球化学条件下,铁还原菌和硫酸盐还原菌种群之间的动态关系仍难以完全描述。在这里,我们用铁、硫酸盐、乙酸盐和模型电子穿梭体 AQDS(9,10-蒽醌-2,6-二磺酸钠)对淡水含水层沉积物组成的实验生物反应器进行了修正,并监测了随着时间的推移不断变化的氧化还原条件以及微生物群落的变化。添加电子穿梭体 AQDS 确实会增加 FeIII 还原的初始速率;然而,它对微生物群落的组成几乎没有影响。我们的结果表明,在 AQDS 和 AQDS+系统中,最初都以归类为 Geobacter(异化 FeIII 还原菌的一个属)的生物体为主导,之后归类为 Desulfosporosinus(异化硫酸盐还原菌的一个属)的序列开始主导两个实验系统。此外,大部分铁还原发生在实验的后期,即所谓的“硫酸盐还原”阶段。这使得仅根据主要微生物过程对地下沉积物进行分类的方法变得值得怀疑,因为这会带来相互关联的生物地球化学后果。为了更好地了解微生物催化的地下过程模型,必须在更广泛的条件下更深入地了解这些相互作用。