微生物介导硝酸盐还原耦合亚铁氧化过程的动力学及其影响因素

【目的】探究不同菌浓度和亚铁浓度条件下,Acidovorax sp. strain BoFeN1介导的厌氧亚铁氧化耦合硝酸盐还原过程的动力学和次生矿物。【方法】构建包含菌BoFeN1、硝酸盐、亚铁的厌氧培养体系,测试硝酸根、亚硝酸根、乙酸根、亚铁等浓度,并收集次生矿物,采用XRD、SEM进行矿物种类和形貌表征。【结果】在微生物介导硝酸盐还原耦合亚铁氧化的体系中,高菌浓度促进硝酸盐还原,对亚铁氧化也有一定促进作用;高浓度亚铁在低菌浓度下氧化反应速率和程度降低,但是在高菌浓度下无明显影响;亚铁浓度越高次生矿物结晶度越高,但对硝酸盐还原具有一定抑制作用。在微生物介导亚硝酸盐还原耦合亚铁氧化的体系中,高的菌浓度和亚铁浓度都会促进亚硝酸盐还原,但亚铁氧化的次生矿物会对亚硝酸盐的微生物还原产生较强的抑制作用,次生矿物的种类和结晶度主要受亚铁浓度影响。【结论】硝酸盐还原主要是生物反硝化作用,亚硝酸盐还原包含生物反硝化和化学反硝化两部分,在硝酸盐体系中亚铁氧化与次生矿物生成是受生物和化学反硝化作用的共同影响,但亚硝酸盐体系中亚铁氧化与次生矿物生成主要是受化学反硝化作用影响。该研究可为深入理解厌氧微生物介导铁氮耦合反应机制提供基础数据和理论支撑。     

湖泊微生物反硝化过程及速率研究进展

湖泊中微生物介导的反硝化过程对于区域乃至全球的气候环境变化有着深远的影响。因此,研究湖泊微生物反硝化过程及速率有助于我们深刻理解湖泊氮元素生物地球化学循环规律,全面认识湖泊生境对全球氮循环的贡献。本文综述了湖泊生境中反硝化过程(包括典型的反硝化过程及与其他物质循环耦合的反硝化过程,如与有机氮耦合的共反硝化作用、与碳循环耦合的硝酸盐/亚硝酸盐依赖型厌氧甲烷氧化、与铁循环耦合的硝酸盐依赖型铁氧化、与硫循环耦合的硝酸盐还原硫氧化)的速率、驱动微生物及其影响因素。最后对湖泊反硝化过程研究现状和未来发展方向提出总结与展望。     

微生物介导铁还原耦合氨氧化过程的研究进展

铁的氧化还原过程可以显著影响环境中次生矿物的形成、养分转化和污染物的归趋。作为厌氧环境中新发现的铁循环过程,铁氨氧化过程对自然和农田生态系统中氨氧化的贡献可达10%以上,对环境保护和农业生产具有深远的意义。文章主要从发展历程、相关微生物、反应机制、影响因素和环境意义等方面综述了铁氨氧化过程。在此过程中,Acidimicrobiaceaesp.A6和异化铁还原菌(DIRB)是驱动铁氨氧化过程的关键微生物,环境pH、Fe(Ⅲ)的浓度和种类、碳源和Mn(Ⅳ)氧化物是重要环境影响因子。铁氨氧化过程可能由微生物独立驱动完成,也可能由微生物-化学耦合作用驱动完成。从环境意义看,铁氨氧化过程对减少温室气体排放、固定重金属等方面具有积极影响,但也会导致氮素流失等负面环境效应。后续的研究可以从纯化微生物、拓展研究方法等方面着手,进一步提升铁氨氧化过程的研究广度和深度。     

双阳极室甲烷微生物燃料电池同步脱氮除硫性能及微生物群落分析

【背景】甲烷厌氧氧化(anaerobic oxidation of methane, AOM)包含反硝化型甲烷厌氧氧化和硫酸盐还原型甲烷厌氧氧化。目前,人们向水体中排放过量的含氮及含硫污染物,引起了严重的环境污染和生态破坏。【目的】利用甲烷厌氧氧化微生物燃料电池(microbial fuel cell, MFC)研究同步脱氮除硫耦合反应机理及反应过程中微生物的多样性信息。【方法】构建了3个微生物燃料电池(N-S-MFC、N-MFC、S-MFC),以甲烷作为唯一碳源,探究其同步脱氮除硫性能,并采用16S rRNA基因高通量测序技术对微生物群落结构进行分析。【结果】N-S-MFC中硝酸盐和硫酸盐的去除率分别为90.91%和18.46%。阳极室中微生物的相对丰度提高,与反硝化及硫酸盐还原菌相关的微生物大量富集,如门水平上拟杆菌门(Bacteroidota)、厚壁菌门(Firmicutes)和脱硫杆菌门(Desulfobacterota),同时属水平上Methylobacterium＿Methylorubrum、Methylocaldum、Methylomonas等常见的甲烷氧化菌增多。【结论...     

化能自养硫氧化细菌Halothiobacillus sp.LS2介导的以乙炔为电子受体的硫氧化反应

【目的】探究化能自养硫氧化细菌Halothiobacillus sp. LS2介导的以乙炔为电子受体的厌氧硫氧化反应。【方法】稀释涂布法测定细胞生长情况,离子色谱仪测试硫氧化动力学中SO_4~(2–)和S_2O_3~(2–)以及基于相对荧光定量法的基因表达分析。【结果】尽管菌株LS2在以氧气为电子受体时的最大反应速率V_(max)更高,但在厌氧条件下且以乙炔为电子受体时,菌株LS2的生长量是氧气为电子受体时的2倍,且硫氧化酶基因soxB的表达量显著高于氧气作为电子受体时。【结论】菌株LS2不仅可以以乙炔为电子受体完成厌氧硫氧化反应,且这一代谢过程的产能效率较有氧硫氧化过程更高。本研究首次发现了微生物介导的以乙炔为电子受体的厌氧硫氧化反应,对丰富硫的生物地球化学循环理论有积极意义。     

利用硝酸盐和亚硝酸盐同步富集厌氧甲烷氧化微生物的比较实验

【背景】反硝化厌氧甲烷氧化(Denitrifying anaerobic methane oxidation,DAMO)是以硝酸盐或亚硝酸盐为电子受体以甲烷为电子供体的厌氧氧化过程,对认识全球碳氮循环、削减温室气体排放和开发废水脱氮新技术等方面具有重要意义。【目的】认识以硝酸盐和亚硝酸盐为电子受体的DAMO微生物富集过程和结果的差异性。【方法】在序批式反应器(Sequencing batch reaetor,SBR)内接种混合物,分别以硝酸盐和亚硝酸盐为电子受体连续培养800 d,定期检测反应器基质浓度变化、计算转化速率;利用16S rRNA基因系统发育分析研究功能微生物的多样性,利用实时荧光定量PCR技术定量测定功能微生物。【结果】以亚硝酸盐为电子受体的1、3号反应器富集到了DAMO细菌,未检测到DAMO古菌;以硝酸盐为电子受体的2号反应器富集到了DAMO细菌和古菌的混合物;3个反应器的脱氮速率经过初始低速期、快速提升期,最终达到稳定,但2号快速提升期开始时间比1、3号晚了80 d左右,达到稳定的时间更长,稳定最大速率为1、3号的44.7%、40.3%。【结论】硝酸盐和亚硝酸盐对富集产物有决定性影响;以硝酸盐为电子受体富集得到的DAMO古菌和细菌协同体系可以长期稳定共存,DAMO古菌可能是协同体系中脱氮速率的限制性因素。     

南大西洋中脊热液区异化铁还原微生物及其矿化产物分析

【目的】从深海热液区获取异化铁还原微生物(Dissimilatory iron reducing microorganisms,DIRM),分析其矿化速率和矿化产物,认识其参与的深海生物地球化学循环。【方法】以羟基氧化铁(FeOOH)为电子受体,以乙酸等简单有机物做电子供体,在60°C恒温厌氧条件下,对南大西洋中脊深海热液区硫化物样品中的DIRM进行富集、培养;采用扫描电镜(SEM)和透射电镜(TEM)、选区电子衍射(SAED)以及能谱仪(EDS)等方法对矿化产物进行形貌观察与成分分析。【结果】从2个硫化物样品中,共获得了139个铁还原培养物,它们均能将培养基中FeOOH (Fe3+90 mmol/L)转化为矿化产物。电镜下可见明显的晶体形态,以立方体形晶体为主,边长为5.0–20.0 nm;EDS分析表明,所有矿物晶体的主要元素为铁和氧,推测是由菱铁矿和磁铁矿组成的混合矿物。矿物晶体形成的时间差异较大,从3d到54d不等,多数培养物可在11 d到20 d内形成晶体。微生物多样性表明,培养物中优势菌主要为厚壁菌门(Firmicutes)和广古菌门(Euryarchaeota),包括一氧化碳胞菌(Carboxydocella)与脱硫肠状菌(Desulfotomaculum)近似新物种(16SrRNA基因同源性89%–91%)和广古菌地丸菌(Geoglobus)。【结论】热液区高温厌氧细菌与古菌可以利用简单有机物为电子供体进行铁还原,形成铁氧化物晶体。实验结果对于微生物参与铁元素的生物地球化学循环与矿物形成的潜力具有支持作用。然而它们是否参与了热液区铁元素的生物地球化学循环与矿物形成还需要大量研究工作验证。     

分离自活性污泥的硫酸盐还原菌用于铅锌冶炼渣重金属污染修复

【背景】从活性污泥中分离出一类具有硫酸盐还原能力的菌株,探讨了其用于铅锌冶炼渣重金属污染修复的可行性。【目的】研究硫酸盐还原菌(Sulfate reducing bacteria)对铅锌冶炼渣中重金属的固化作用。【方法】将从活性污泥中分离出的硫酸盐还原菌接种到铅锌冶炼渣中进行修复,采用X射线衍射、Tessier、电感耦合等离子体发射光谱仪检测、高通量测序等方法进行实验。检测铅锌冶炼渣中矿物组成,以及修复过程中重金属化学形态、各金属离子浓度和微生物群落结构的变化。【结果】修复实验表明,体系中电位降低、pH值提高、各重金属稳定态增加、离子浓度降低且微生物群落结构变化显著,硫酸盐还原菌成为优势菌群。【结论】接种硫酸盐还原菌后铅锌冶炼渣中的重金属原位固化效果显著,从而降低生物可利用性,将恶性循环变为良性循环,所以硫酸盐还原菌可用作重金属污染修复的固化药剂。     

微生物厌氧氨氧化耦合铁还原的研究进展及展望

厌氧氨氧化耦合铁还原[ammonium oxidation coupled to Fe(Ⅲ) reduction, Feammox]作为一种连接氮循环和铁循环之间的氮代谢途径,在自然界中氨氮转化过程中起到了重要作用。系统研究Feammox驱动的氮铁的生物地球化学耦合过程及其受控因素,有助于深入理解地球元素循环的微生物机制,也有助于揭示Feammox在缺氧地质历史时期对古海洋氮库演变和含铁矿物形成过程中的作用。本文从Feammox发展历史、相关微生物、影响因素和潜在地质意义等方面综述了Feammox的研究过程和研究内容,并对Feammox的未来研究方向提出展望。     

铁还原细菌Shewanella oneidensis MR-4诱导水合氧化铁形成蓝铁矿的过程

【目的】研究铁还原细菌Shewanella oneidensis MR-4在细胞外诱导形成含铁矿物的矿物相、化学成分和形貌结构等特性及其变化,深化对铁还原细菌细胞外诱导矿化过程的认识。【方法】在以30 mmol/L乳酸钠为电子供体,10 mmol/L水合氧化铁为电子受体,[HCO_3~–]为30 mmol/L,[PO_4~(3–)]为5 mmol/L条件下,30°C恒温下厌氧培养,进行细菌生长和细胞外诱导矿化实验,定期采样测量反应体系的pH、生物量、Fe(Ⅱ)浓度;采用激光拉曼光谱(Raman)、扫描电子显微镜(SEM)、透射电子显微镜(TEM)和X-射线衍射(XRD)等方法对不同时间点的矿化产物进行分析。【结果】MR-4在还原Fe(Ⅲ)的过程中,细胞快速生长,表明MR-4的Fe(Ⅲ)还原和乳酸氧化过程相互耦合,从而进行细胞生长,并在细胞外诱导矿物形成。对不同阶段矿化产物的综合分析表明,反应进行到约8 d时,无定形-弱结晶的水合氧化铁部分地转化为纳米尺寸的磁铁矿晶体颗粒;约16 d时,反应体系中开始出现蓝铁矿晶体颗粒;约20 d后,几乎所有矿物转化为纤维状或者叶片状的蓝铁矿。【结论】铁还原细菌Shewanella oneidensis MR-4细胞外诱导矿化过程受环境条件控制,当以乳酸钠和水合氧化铁分别作为电子供体和受体,相对高的[PO_4~(3–]/[HCO_3~–](1:6)时,水合氧化铁先转化为磁铁矿,最后大量转化为蓝铁矿。本研究为全面认识铁还原细菌的生物诱导矿化过程和评估其参与铁元素地球化学循环提供了新的数据。     

Geochemical Controls on Microbial Nitrate-Dependent U(IV) Oxidation

After reductive immobilization of uranium, the element may be oxidized and remobilized in the presence of nitrate by the activity of dissimilatory nitrate-reducing bacteria. We examined controls on microbially mediated nitrate-dependent U(IV) oxidation in landfill leachate-impacted subsurface sediments. Nitrate-dependent U(IV)-oxidizing bacteria were at least two orders of magnitude less numerous in these sediments than glucose- or Fe(II)-oxidizing nitrate-reducing bacteria and grew more slowly than the latter organisms, suggesting that U(IV) is ultimately oxidized by Fe(III) produced by nitrate-dependent Fe(II)-oxidizing bacteria or by oxidation of Fe(II) by nitrite that accumulates during organotrophic dissimilatory nitrate reduction. We examined the effect of nitrate and reductant concentration on nitrate-dependent U(IV) oxidation in sediment incubations and used the initial reductive capacity (RDC = [reducing equivalents] - [oxidizing equivalents]) of the incubations as a unified measurement of the nitrate or reductant concentration. When we lowered the RDC with progressively higher nitrate concentrations, we observed a corresponding increase in the extent of U(IV) oxidation, but did not observe this relationship between RDC and U(IV) oxidation rate, especially when RDC > 0, suggesting that nitrate concentration strongly controls the extent, but not the rate of nitrate-dependent U(IV) oxidation. On the other hand, when we raised the RDC in sediment incubations with progressively higher reductant (acetate, sulfide, soluble Fe(II), or FeS) concentrations, we observed progressively lower extents and rates of nitrate-dependent U(IV) oxidation. Acetate was a relatively poor inhibitor of nitrate-dependent U(IV) oxidation, while Fe(II) was the most effective inhibitor. Based on these results, we propose that it may be possible to predict the stability of U(IV) in a bioremediated aquifer based on the geochemical characteristics of that aquifer.     

Ecophysiology and the energetic benefit of mixotrophic Fe(II) oxidation by various strains of nitrate-reducing bacteria

In order to assess the importance of nitrate-dependent Fe(II) oxidation and its impact on the growth physiology of dominant Fe oxidizers, we counted these bacteria in freshwater lake sediments and studied their growth physiology. Most probable number counts of nitrate-reducing Fe(II)-oxidizing bacteria in the sediment of Lake Constance, a freshwater lake in Southern Germany, yielded about 10⁵ cells mL⁻¹ of the total heterotrophic nitrate-reducing bacteria, with about 1% (10³ cells mL⁻¹) of nitrate-reducing Fe(II) oxidizers. We investigated the growth physiology of Acidovorax sp. strain BoFeN1, a dominant nitrate-reducing mixotrophic Fe(II) oxidizer isolated from this sediment. Strain BoFeN1 uses several organic compounds (but no sugars) as substrates for nitrate reduction. It also reduces nitrite, dinitrogen monoxide, and O₂, but cannot reduce Fe(III). Growth experiments with cultures amended either with acetate plus Fe(II) or with acetate alone demonstrated that the simultaneous oxidation of Fe(II) and acetate enhanced growth yields with acetate alone (12.5 g dry mass mol⁻¹ acetate) by about 1.4 g dry mass mol⁻¹ Fe(II). Also, pure cultures of Pseudomonas stutzeri and Paracoccus denitrificans strains can oxidize Fe(II) with nitrate, whereas Pseudomonas fluorescens and Thiobacillus denitrificans strains did not. Our study demonstrates that nitrate-dependent Fe(II) oxidation contributes to the energy metabolism of these bacteria, and that nitrate-dependent Fe(II) oxidation can essentially contribute to anaerobic iron cycling.     

长江口外低氧区及其邻近海域表层沉积物反硝化微生物多样性和分布特征

【目的】微生物参与的反硝化是河口区氮损失的主要途径。【方法】本研究采用Illumina MiSeq测序方法,研究了长江口外低氧区及其邻近海域表层沉积物中nirS型和nirK型反硝化微生物群落的多样性和分布特征。【结果】样品共检测到346个nirS Operational Taxonomic Units和267个nirK Operational TaxonomicUnits,根据采样地的环境特征及nirS型和nirK型反硝化微生物群落聚类分析结果将所有OperationalTaxonomicUnits划分为低氧区、南部区域及外部深水区,其中外部深水区的样品nirS功能基因的多样性最高。各实验样地优势Operational Taxonomic Units在系统进化关系上可分为多个不同的簇。此次发现的所有优势OperationalTaxonomicUnits均属于未被培养的菌群,其中部分Operational Taxonomic Units还是首次被发现。此外还发现nirS功能基因对低氧区的环境适应性更好。【结论】我们的研究结果表明广泛存在的反硝化微生物在河口沉积物的氮循环中发挥重要作用。     

Nitrate-dependent [Fe(II)EDTA]2- oxidation by Paracoccus ferrooxidans sp. nov., isolated from a denitrifying bioreactor

Enrichments with [Fe(II)EDTA]2- as electron donor and nitrate or nitrite as electron acceptor were established using an inoculum from a bioreactor performing denitrification. A nitrate-reducing, [Fe(II)EDTA]2- oxidizing strain was isolated and named strain BDN-1. The G + C content of strain BDN-1 was 67%, and the organism was closely affiliated to Paracoccus denitrificans, P. pantotrophus and P. versutus by 16S rRNA sequence comparison. Results from DNA-DNA hybridization, rep-PCR, and whole cell protein analysis gave congruent results confirming the genotypic and phenotypic differences between strain BDN-1 and the other species of Paracoccus. From these results, we considered strain BDN-1 as a novel species for which we propose the name Paracoccus ferrooxidans. Apart from [Fe(II)EDTA]2-, BDN-1 could also use thiosulfate and thiocyanate as inorganic electron donors. Nitrate, nitrite, N2O, [Fe(II)EDTA.NO]2- and oxygen could be used by strain BDN-1 as electron acceptors. Repeated transfer on a culture medium with bicarbonate as the sole carbon source confirmed that strain BDN-1 was a facultative autotroph. [Fe(II)EDTA]2- oxidation dependent denitrification was also performed by other Paracoccus species, that were closely affiliated to P. ferrooxidans.     

Fe(II) Oxidation Is an Innate Capability of Nitrate-Reducing Bacteria That Involves Abiotic and Biotic Reactions

Phylogenetically diverse species of bacteria can catalyze the oxidation of ferrous iron [Fe(II)] coupled to nitrate (NO₃⁻) reduction, often referred to as nitrate-dependent iron oxidation (NDFO). Very little is known about the biochemistry of NDFO, and though growth benefits have been observed, mineral encrustations and nitrite accumulation likely limit growth. Acidovorax ebreus, like other species in the Acidovorax genus, is proficient at catalyzing NDFO. Our results suggest that the induction of specific Fe(II) oxidoreductase proteins is not required for NDFO. No upregulated periplasmic or outer membrane redox-active proteins, like those involved in Fe(II) oxidation by acidophilic iron oxidizers or anaerobic photoferrotrophs, were observed in proteomic experiments. We demonstrate that while “abiotic” extracellular reactions between Fe(II) and biogenic NO₂⁻/NO can be involved in NDFO, intracellular reactions between Fe(II) and periplasmic components are essential to initiate extensive NDFO. We present evidence that an organic cosubstrate inhibits NDFO, likely by keeping periplasmic enzymes in their reduced state, stimulating metal efflux pumping, or both, and that growth during NDFO relies on the capacity of a nitrate-reducing bacterium to overcome the toxicity of Fe(II) and reactive nitrogen species. On the basis of our data and evidence in the literature, we postulate that all respiratory nitrate-reducing bacteria are innately capable of catalyzing NDFO. Our findings have implications for a mechanistic understanding of NDFO, the biogeochemical controls on anaerobic Fe(II) oxidation, and the production of NO₂⁻, NO, and N₂O in the environment.     

Effect of Oxidation Rate and Fe(II) State on Microbial Nitrate-Dependent Fe(III) Mineral Formation

A nitrate-dependent Fe(II)-oxidizing bacterium was isolated and used to evaluate whether Fe(II) chemical form or oxidation rate had an effect on the mineralogy of biogenic Fe(III) (hydr)oxides resulting from nitrate-dependent Fe(II) oxidation. The isolate (designated FW33AN) had 99% 16S rRNA sequence similarity to Klebsiella oxytoca. FW33AN produced Fe(III) (hydr)oxides by oxidation of soluble Fe(II) [Fe(II)_sol] or FeS under nitrate-reducing conditions. Based on X-ray diffraction (XRD) analysis, Fe(III) (hydr)oxide produced by oxidation of FeS was shown to be amorphous, while oxidation of Fe(II)_sol yielded goethite. The rate of Fe(II) oxidation was then manipulated by incubating various cell concentrations of FW33AN with Fe(II)_sol and nitrate. Characterization of products revealed that as Fe(II) oxidation rates slowed, a stronger goethite signal was observed by XRD and a larger proportion of Fe(III) was in the crystalline fraction. Since the mineralogy of Fe(III) (hydr)oxides may control the extent of subsequent Fe(III) reduction, the variables we identify here may have an effect on the biogeochemical cycling of Fe in anoxic ecosystems.     

Neutrophilic, nitrate-dependent, Fe(II) oxidation by a Dechloromonas species

A species of Dechloromonas, strain UWNR4, was isolated from a nitrate-reducing, enrichment culture obtained from Wisconsin River (USA) sediments. This strain was characterized for anaerobic oxidation of both aqueous and chelated Fe(II) coupled to nitrate reduction at circumneutral pH. Dechloromonas sp. UWNR4 was incubated in anoxic batch reactors in a defined medium containing 4.5–5 mM NO₃ ^?, 6 mM Fe²⁺ and 1–1.8 mM acetate. Strain UWNR4 efficiently oxidized Fe²⁺ with 90 % oxidation of Fe²⁺ after 3 days of incubation. However, oxidation of Fe²⁺ resulted in Fe(III)-hydroxide-encrusted cells and loss of metabolic activity, suggested by inability of the cells to utilize further additions of acetate. In similar experiments with chelated iron (Fe(II)-EDTA), encrusted cells were not produced and further additions of acetate and Fe(II)-EDTA could be oxidized. Although members of the genus Dechloromonas are primarily known as perchlorate and nitrate reducers, our findings suggest that some species could be members of microbial communities influencing iron redox cycling in anoxic, freshwater sediments. Our work using Fe(II)-EDTA also demonstrates that Fe(II) oxidation was microbially catalyzed rather than a result of abiotic oxidation by biogenic NO₂ ^?.     

电子穿梭体对菌株Clostridium butyricum LQ25异化铁还原性质影响

【目的】在异化铁还原细菌培养体系中,通过外加电子穿梭体,分析电子穿梭体种类与浓度对细菌异化铁还原性质的影响。【方法】以一株发酵型异化铁还原细菌Clostridium butyricum LQ25为研究对象,设置水溶性介体蒽醌-2-磺酸钠和核黄素作为外加电子穿梭体。【结果】在氢氧化铁为电子受体、葡萄糖为电子供体培养条件下,不同浓度蒽醌-2-磺酸钠和核黄素对菌株LQ25异化铁还原效率影响具有显著性差异。外加蒽醌-2-磺酸钠浓度为0.5 mmol/L时,菌株累积产生Fe(Ⅱ)浓度最高,为12.95±0.08 mg/L,相比对照组提高88%。核黄素浓度为100mg/L时,菌株累积产生Fe(Ⅱ)浓度是11.06±0.04mg/L,相比对照组提高61%。外加电子穿梭体能够改变菌株LQ25发酵产物中丁酸和乙酸浓度,提高乙酸相对含量。【结论】蒽醌-2-磺酸钠和核黄素作为外加电子穿梭体能显著促进细菌异化铁还原效率,为揭示发酵型异化铁还原细菌胞外电子传递机制提供实验支持。