Kuroiwa Megumi, Fukushima Keitaro, Hashimoto Kazuma, Senga Yukiko, Sato Tsubasa, Katsuyama Chie, Suwa Yuichi
Department of Applied Chemistry, Graduate School of Engineering, Tokyo University of Agriculture and Technology;
Faculty & Graduate School of Urban Environmental Sciences, Tokyo Metropolitan University; Center for Ecological Research, Kyoto University.
J Vis Exp. 2020 Oct 7(164). doi: 10.3791/59562.
The importance of understanding the fate of nitrate (NO3), which is the dominant N species transferred from terrestrial to aquatic ecosystems, has been increasing because global nitrogen loads have dramatically increased following industrialization. Dissimilatory nitrate reduction to ammonium (DNRA) and denitrification are both microbial processes that use NO3 for respiration. Compared to denitrification, quantitative determinations of the DNRA activity have been carried out only to a limited extent. This has led to an insufficient understanding of the importance of DNRA in NO3 transformations and the regulating factors of this process. The objective of this paper is to provide a detailed procedure for the measurement of the potential DNRA rate in environmental samples. In brief, the potential DNRA rate can be calculated from the N-labeled ammonium (NH4) accumulation rate in NO3 added incubation. The determination of the NH4 and NH4 concentrations described in this paper is comprised of the following steps. First, the NH4 in the sample is extracted and trapped on an acidified glass filter as ammonium salt. Second, the trapped ammonium is eluted and oxidized to NO3 via persulfate oxidation. Third, the NO3 is converted to N2O via an N2O reductase deficient denitrifier. Finally, the converted N2O is analyzed using a previously developed quadrupole gas chromatography-mass spectrometry system. We applied this method to salt marsh sediments and calculated their potential DNRA rates, demonstrating that the proposed procedures allow a simple and more rapid determination compared to previously described methods.
理解硝酸盐(NO₃)的归宿至关重要,因为硝酸盐是从陆地生态系统转移到水生生态系统的主要氮形态。随着工业化进程中全球氮负荷急剧增加,其重要性日益凸显。异化硝酸盐还原为铵(DNRA)和反硝化作用都是利用NO₃进行呼吸的微生物过程。与反硝化作用相比,对DNRA活性的定量测定仅在有限程度上开展过。这导致对DNRA在NO₃转化中的重要性以及该过程的调控因素认识不足。本文的目的是提供一种用于测量环境样品中潜在DNRA速率的详细方法。简而言之,潜在DNRA速率可根据添加NO₃的培养物中氮标记铵(NH₄)的积累速率来计算。本文所述的NH₄和NH₄浓度的测定包括以下步骤。首先,将样品中的NH₄提取并以铵盐形式捕获在酸化玻璃滤器上。其次,将捕获的铵洗脱并通过过硫酸盐氧化氧化为NO₃。第三,通过缺乏N₂O还原酶的反硝化细菌将NO₃转化为N₂O。最后,使用先前开发的四极杆气相色谱 - 质谱系统分析转化后的N₂O。我们将该方法应用于盐沼沉积物并计算了它们的潜在DNRA速率,结果表明与先前描述的方法相比,所提出的程序能够实现更简单、更快速的测定。