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Denitrification by sulfur-oxidizing bacteria in a eutrophic lake

机译:富营养化湖泊中硫氧化细菌的反硝化作用

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ABSTRACT: Understanding the mechanistic controls of microbial denitrification is of central importance to both environmental microbiology and ecosystem ecology. Loss of nitrate (NO3−) is often attributed to carbon-driven (heterotrophic) denitrification. However, denitrification can also be coupled to sulfur (S) oxidation by chemolithoautotrophic bacteria. In the present study, we used an in situ stable isotope (15NO3−) tracer addition in combination with molecular approaches to understand the contribution of sulfur-oxidizing bacteria to the reduction of NO3− in a eutrophic lake. Samples were incubated across a total dissolved sulfide (H2S) gradient (2 to 95 μM) between the lower epilimnion and the upper hypolimnion. Denitrification rates were low at the top of the chemocline (4.5 m) but increased in the deeper waters (5.0 and 5.5 m), where H2S was abundant. Concomitant with increased denitrification at depths with high sulfide was the production of sulfate (SO42−), suggesting that the added NO3− was used to oxidize H2S to SO42−. Alternative nitrate removal pathways, including dissimilatory nitrate reduction to ammonium (DNRA) and anaerobic ammonium oxidation (anammox), did not systematically change with depth and accounted for 1 to 15% of the overall nitrate loss. Quantitative PCR revealed that bacteria of the Sulfurimonas genus that are known denitrifiers increased in abundance in response to NO3− addition in the treatments with higher H2S. Stoichiometric estimates suggest that H2S oxidation accounted for more than half of the denitrification at the depth with the highest sulfide concentration. The present study provides evidence that microbial coupling of S and nitrogen (N) cycling is likely to be important in eutrophic freshwater ecosystems.
机译:摘要:了解微生物反硝化的机械控制对环境微生物学和生态系统生态学都至关重要。硝酸盐(NO 3 -)的损失通常归因于碳驱动的(异养)反硝化作用。然而,反硝化作用还可以与化肥性自养细菌氧化成硫(S)。在本研究中,我们结合使用了原位稳定同位素( 15 NO 3 -)示踪剂用分子方法来了解硫氧化细菌对富营养化湖泊中NO 3 -的还原的贡献。样品在下epi上缘和上hypo上缘之间的总溶解硫化物(H 2 S)梯度(2至95μM)中孵育。趋化线顶部(4.5 m)的反硝化率较低,但在H 2 S丰富的较深水域(5.0和5.5 m)则反硝化率较高。随着高硫化物深度处反硝化作用的增加,硫酸盐的产生(SO 4 2-),表明添加了NO 3 -用于将H 2 S氧化为SO 4 2-。替代性硝酸盐去除途径,包括将硝酸盐异化还原为铵(DNRA)和厌氧铵氧化(anammox),不会随着深度的变化而系统地变化,占硝酸盐总损失的1%至15%。定量PCR结果表明,在H含量较高的处理中,已知的反硝化细菌 Sulphurimonas 的细菌响应NO 3 -的添加而大量增加。 2 S。化学计量的估计表明,在硫化物浓度最高的深度,H 2 的氧化占反硝化作用的一半以上。本研究提供的证据表明,S和氮(N)循环的微生物耦合在富营养淡水生态系统中可能很重要。

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