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Methane Emission in a Specific Riparian-Zone Sediment Decreased with Bioelectrochemical Manipulation and Corresponded to the Microbial Community Dynamics

机译:生物电化学处理降低并与微生物群落动力学相对应的特定河岸带沉积物中的甲烷排放

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摘要

Dissimilatory metal-reducing bacteria are widespread in terrestrial ecosystems, especially in anaerobic soils and sediments. Thermodynamically, dissimilatory metal reduction is more favorable than sulfate reduction and methanogenesis but less favorable than denitrification and aerobic respiration. It is critical to understand the complex relationships, including the absence or presence of terminal electron acceptors, that govern microbial competition and coexistence in anaerobic soils and sediments, because subsurface microbial processes can effect greenhouse gas emissions from soils, possibly resulting in impacts at the global scale. Here, we elucidated the effect of an inexhaustible, ferrous-iron and humic-substance mimicking terminal electron acceptor by deploying potentiostatically poised electrodes in the sediment of a very specific stream riparian zone in Upstate New York state. At two sites within the same stream riparian zone during the course of 6 weeks in the spring of 2013, we measured CH4 and N2/N2O emissions from soil chambers containing either poised or unpoised electrodes, and we harvested biofilms from the electrodes to quantify microbial community dynamics. At the upstream site, which had a lower vegetation cover and highest soil temperatures, the poised electrodes inhibited CH4 emissions by ∼45% (when normalized to remove temporal effects). CH4 emissions were not significantly impacted at the downstream site. N2/N2O emissions were generally low at both sites and were not impacted by poised electrodes. We did not find a direct link between bioelectrochemical treatment and microbial community membership; however, we did find a correspondence between environment/function and microbial community dynamics.
机译:异化还原金属的细菌广泛分布在陆地生态系统中,特别是在厌氧土壤和沉积物中。在热力学上,异化金属还原比硫酸盐还原和甲烷生成更有利,但比反硝化和有氧呼吸更不利。了解厌氧土壤和沉积物中微生物竞争和共存的复杂关系(包括末端电子受体的存在与否)至关重要,因为地下微生物过程会影响土壤的温室气体排放,可能对全球温室气体产生影响。规模。在这里,我们通过在纽约上州州一个非常特殊的河岸带区域的沉积物中部署恒电位平衡电极,阐明了一种用尽不竭的,铁-铁和腐殖质模拟末端电子受体的效果。在2013年春季的6周内,在同一河岸带内的两个地点,我们测量了含有平衡电极或未平衡电极的土壤室中CH4和N2 / N2O的排放,并从电极中收获生物膜以量化微生物群落动力学。在上游地区,植被覆盖率较低,土壤温度最高,准备好的电极将CH4的排放抑制了约45%(当进行标准化以消除时间影响时)。 CH4排放在下游站点没有受到重大影响。在这两个地点,N2 / N2O排放通常都很低,并且不受平衡电极的影响。我们没有发现生物电化学治疗与微生物群落成员之间有直接联系;但是,我们确实发现环境/功能与微生物群落动态之间存在对应关系。

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