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Manipulation of the Dissolved Organic Carbon Pool in an Agricultural Stream: Responses in Microbial Community Structure, Denitrification, and Assimilatory Nitrogen Uptake

机译:在农业流中溶解的有机碳库的操纵:微生物群落结构,反硝化作用和同化氮吸收的响应。

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Carbon (C) and nitrogen (N) are strongly coupled across ecosystems due to stoichiometrically balanced assimilatory demand as well as dissimilatory processes such as denitrification. Microorganisms mediate these biogeochemical cycles, but how microbial communities respond to environmental changes, such as dissolved organic carbon (DOC) availability, and how those responses impact coupled biogeochemical cycles in streams is not clear. We enriched a stream in central Indiana with labile DOC for 5 days to investigate coupled C and N cycling. Before, and on day 5 of the enrichment, we examined assimilatory uptake and denitrification using whole-stream 15N-nitrate tracer additions and short-term nitrate releases. Concurrently, we measured bacterial and denitrifier abundance and community structure. We predicted N assimilation and denitrification would be stimulated by the addition of labile C and would be mediated by increases in bacterial activity, abundance, and a shift in community structure. In response to the twofold increase in DOC concentrations in the water column, N assimilation increased throughout the enrichment. Community respiration doubled during the enrichment and was associated with a change in bacterial community structure (based on terminal restriction fragment length polymorphisms of the 16S rRNA gene). In contrast, there was little response in denitrification or denitrifier community structure, likely because labile C was assimilated by heterotrophic communities on the stream bed prior to reaching denitrifiers within the sediments. Our results suggest that coupling between C and N in streams involves potentially complex interactions with sediment texture and organic matter, microbial community structure, and possibly indirect biogeochemical pathways.
机译:由于化学计量平衡的同化需求以及诸如反硝化等异化过程,碳(C)和氮(N)在整个生态系统中紧密耦合。微生物介导了这些生物地球化学循环,但是尚不清楚微生物群落如何响应环境变化,例如溶解有机碳(DOC)的可用性,以及这些响应如何影响河流中耦合的生物地球化学循环。我们用不稳定的DOC富集了印第安那州中部的一条河流,历时5天,以研究C和N耦合的循环。在富集之前和第5天,我们使用全流15 N硝酸盐示踪剂添加和短期硝酸盐释放来研究同化吸收和反硝化作用。同时,我们测量了细菌和反硝化细菌的丰度和群落结构。我们预测,添加不稳定的C会刺激N同化和反硝化作用,而N的吸收和反硝化作用将通过细菌活性的增加,丰度的增加和群落结构的变化来介导。响应于水柱中DOC浓度的两倍增加,整个吸收过程中N同化作用均增加。在富集过程中,群落呼吸增加了一倍,并与细菌群落结构的变化有关(基于16S rRNA基因的末端限制性片段长度多态性)。相反,反硝化作用或反硝化作用剂群落结构几乎没有反应,这可能是由于不稳定的C在到达沉积物内的反硝化作用剂之前已被河床中的异养菌群落吸收。我们的结果表明,河流中C和N之间的耦合涉及与沉积物质地和有机物,微生物群落结构以及间接生物地球化学途径的潜在复杂相互作用。

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