Institute of Environmental Assessment and Water Research (IDAEA, CSIC), 08034, Barcelona, Catalonia, Spain; Departament de Genètica, Microbiologia I Estadística, Universitat de Barcelona, 08028, Barcelona, Catalonia, Spain.
Institute of Environmental Assessment and Water Research (IDAEA, CSIC), 08034, Barcelona, Catalonia, Spain.
Chemosphere. 2020 Dec;260:127554. doi: 10.1016/j.chemosphere.2020.127554. Epub 2020 Jul 10.
Estuarine sediments are often characterized by abundant iron oxides, organic matter, and anthropogenic nitrogen compounds (e.g., nitrate and nitrite). Anoxic dissimilatory iron reducing bacteria (e.g., Shewanella loihica) are ubiquitous in these environments where they can catalyze the reduction of Fe(III) (oxyhydr)oxides, thereby releasing aqueous Fe(II). The biologically produced Fe(II) can later reduce nitrite to form nitrous oxide. The effect on nitrite reduction by both biologically produced and artificially amended Fe(II) was examined experimentally. Ferrihydrite was reduced by Shewanella loihica in a batch reaction with an anoxic synthetic sea water medium. Some of the Fe(II) released by S. loihica adsorbed onto ferrihydrite, which was involved in the transformation of ferrihydrite to magnetite. In a second set of experiments with identical medium, no microorganism was present, instead, Fe(II) was amended. The amount of solid-bound Fe(II) in the experiments with bioproduced Fe(II) increased the rate of abiotic NO reduction with respect to that with synthetic Fe(II), yielding half-lives of 0.07 and 0.47 d, respectively. The δO and δN of NO was measured through time for both the abiotic and innoculated experiments. The ratio of εO/εN was 0.6 for the abiotic experiments and 3.1 when NO was reduced by S. loihica, thus indicating two different mechanisms for the NO reduction. Notably, there is a wide range of the εO/εN values in the literature for abiotic and biotic NO reduction, as such, the use of this ratio to distinguish between reduction mechanisms in natural systems should be taken with caution. Therefore, we suggest an additional constraint to identify the mechanisms (i.e. abiotic/biotic) controlling NO reduction in natural settings through the correlation of δN-NO and the aqueous Fe(II) concentration.
河口沉积物通常富含铁氧化物、有机物和人为氮化合物(如硝酸盐和亚硝酸盐)。在这些环境中,普遍存在着异化型铁还原菌(如希瓦氏菌属),它们可以催化三价铁(氧)氢氧化物的还原,从而释放出可溶的二价铁。生物产生的二价铁随后可以将亚硝酸盐还原为一氧化二氮。本研究通过实验考察了生物产生和人工添加的二价铁对亚硝酸盐还原的影响。在一个缺氧的合成海水介质的分批反应中,希瓦氏菌属还原了水铁矿。希瓦氏菌属释放的部分二价铁被水铁矿吸附,这涉及到水铁矿向磁铁矿的转化。在一组具有相同介质的对照实验中,没有微生物存在,而是添加了二价铁。在有生物产生的二价铁的实验中,固相结合的二价铁的量增加了非生物还原 NO 的速率,相对于用合成二价铁的实验,半衰期分别为 0.07 和 0.47 d。通过时间测量了非生物和接种实验中 NO 的 δO 和 δN。非生物实验的 εO/εN 比值为 0.6,当 NO 被希瓦氏菌属还原时,比值为 3.1,这表明 NO 还原有两种不同的机制。值得注意的是,在非生物和生物还原 NO 的文献中,εO/εN 值的范围很广,因此,在自然系统中使用该比值来区分还原机制应谨慎。因此,我们建议通过 δN-NO 和可溶二价铁浓度的相关性,为识别控制自然环境中 NO 还原的机制(即非生物/生物)提供一个额外的约束条件。