Jakus Natalia, Blackwell Nia, Osenbrück Karsten, Straub Daniel, Byrne James M, Wang Zhe, Glöckler David, Elsner Martin, Lueders Tillmann, Grathwohl Peter, Kleindienst Sara, Kappler Andreas
Geomicrobiology, Center for Applied Geoscience, University of Tuebingen, Tuebingen, Germany.
Microbial Ecology, Center for Applied Geoscience, University of Tuebingen, Tuebingen, Germany.
Appl Environ Microbiol. 2021 Jul 27;87(16):e0046021. doi: 10.1128/AEM.00460-21.
Nitrate removal in oligotrophic environments is often limited by the availability of suitable organic electron donors. Chemolithoautotrophic bacteria may play a key role in denitrification in aquifers depleted in organic carbon. Under anoxic and circumneutral pH conditions, iron(II) was hypothesized to serve as an electron donor for microbially mediated nitrate reduction by Fe(II)-oxidizing (NRFeOx) microorganisms. However, lithoautotrophic NRFeOx cultures have never been enriched from any aquifer, and as such, there are no model cultures available to study the physiology and geochemistry of this potentially environmentally relevant process. Using iron(II) as an electron donor, we enriched a lithoautotrophic NRFeOx culture from nitrate-containing groundwater of a pyrite-rich limestone aquifer. In the enriched NRFeOx culture that does not require additional organic cosubstrates for growth, within 7 to 11 days, 0.3 to 0.5 mM nitrate was reduced and 1.3 to 2 mM iron(II) was oxidized, leading to a stoichiometric NO/Fe(II) ratio of 0.2, with N and NO identified as the main nitrate reduction products. Short-range ordered Fe(III) (oxyhydr)oxides were the product of iron(II) oxidation. Microorganisms were observed to be closely associated with formed minerals, but only few cells were encrusted, suggesting that most of the bacteria were able to avoid mineral precipitation at their surface. Analysis of the microbial community by long-read 16S rRNA gene sequencing revealed that the culture is dominated by members of the family that are known as autotrophic, neutrophilic, and microaerophilic iron(II) oxidizers. In summary, our study suggests that NRFeOx mediated by lithoautotrophic bacteria can lead to nitrate removal in anthropogenically affected aquifers. Removal of nitrate by microbial denitrification in groundwater is often limited by low concentrations of organic carbon. In these carbon-poor ecosystems, nitrate-reducing bacteria that can use inorganic compounds such as Fe(II) (NRFeOx) as electron donors could play a major role in nitrate removal. However, no lithoautotrophic NRFeOx culture has been successfully isolated or enriched from this type of environment, and as such, there are no model cultures available to study the rate-limiting factors of this potentially important process. Here, we present the physiology and microbial community composition of a novel lithoautotrophic NRFeOx culture enriched from a fractured aquifer in southern Germany. The culture is dominated by a putative Fe(II) oxidizer affiliated with the family and performs nitrate reduction coupled to Fe(II) oxidation leading to NO and N formation without the addition of organic substrates. Our analyses demonstrate that lithoautotrophic NRFeOx can potentially lead to nitrate removal in nitrate-contaminated aquifers.
在贫营养环境中,硝酸盐的去除通常受到合适有机电子供体可用性的限制。化能自养细菌可能在有机碳耗尽的含水层反硝化过程中发挥关键作用。在缺氧和接近中性pH条件下,据推测亚铁可作为通过亚铁氧化(NRFeOx)微生物进行微生物介导的硝酸盐还原的电子供体。然而,从未从任何含水层中富集过化能自养的NRFeOx培养物,因此,没有可用于研究这一潜在环境相关过程的生理学和地球化学的模型培养物。我们以亚铁作为电子供体,从富含黄铁矿的石灰岩含水层的含硝酸盐地下水中富集了一种化能自养的NRFeOx培养物。在不需要额外有机共底物即可生长的富集NRFeOx培养物中,7至11天内可还原0.3至0.5 mM硝酸盐,氧化1.3至2 mM亚铁,导致化学计量的NO/亚铁比为0.2,其中N和NO被确定为主要的硝酸盐还原产物。短程有序的铁(III)(氢)氧化物是亚铁氧化的产物。观察到微生物与形成的矿物密切相关,但只有少数细胞被包裹,这表明大多数细菌能够避免在其表面形成矿物沉淀。通过长读长16S rRNA基因测序分析微生物群落表明,该培养物以被认为是自养、嗜中性和微需氧亚铁氧化菌的家族成员为主。总之,我们的研究表明,化能自养细菌介导的NRFeOx可导致人为影响的含水层中的硝酸盐去除。地下水中微生物反硝化去除硝酸盐通常受到有机碳浓度低的限制。在这些贫碳生态系统中,能够利用亚铁等无机化合物作为电子供体的硝酸盐还原细菌可能在硝酸盐去除中起主要作用。然而,尚未从这类环境中成功分离或富集到化能自养的NRFeOx培养物,因此,没有可用于研究这一潜在重要过程的限速因素的模型培养物。在此,我们展示了从德国南部一个裂隙含水层中富集的新型化能自养NRFeOx培养物的生理学和微生物群落组成。该培养物以一个与该家族相关的假定亚铁氧化菌为主,在不添加有机底物的情况下,进行与亚铁氧化耦合的硝酸盐还原,导致NO和N的形成。我们的分析表明,化能自养的NRFeOx可能导致受硝酸盐污染的含水层中的硝酸盐去除。