The oxygen sensor MgFnr controls magnetite biomineralization by regulation of denitrification in Magnetospirillum gryphiswaldense
© Li et al.; licensee BioMed Central Ltd. 2014
Received: 21 March 2014
Accepted: 28 May 2014
Published: 10 June 2014
Magnetotactic bacteria are capable of synthesizing magnetosomes only under oxygen-limited conditions. However, the mechanism of the aerobic repression on magnetite biomineralization has remained unknown. In Escherichia coli and other bacteria, Fnr (fumarate and nitrate reduction regulator) proteins are known to be involved in controlling the switch between microaerobic and aerobic metabolism. Here, we report on an Fnr-like protein (MgFnr) and its role in growth metabolism and magnetite biomineralization in the alphaproteobacterium Magnetospirillum gryphiswaldense.
Deletion of Mgfnr not only resulted in decreased N2 production due to reduced N2O reductase activity, but also impaired magnetite biomineralization under microaerobic conditions in the presence of nitrate. Overexpression of MgFnr in the WT also caused the synthesis of smaller magnetite particles under anaerobic and microaerobic conditions in the presence of nitrate. These data suggest that proper expression of MgFnr is required for WT-like magnetosome synthesis, which is regulated by oxygen. Analyses of transcriptional gusA reporter fusions revealed that besides showing similar properties to Fnr proteins reported in other bacteria, MgFnr is involved in the repression of the expression of denitrification genes nor and nosZ under aerobic conditions, possibly owing to several unique amino acid residues specific to MTB-Fnr.
We have identified and thoroughly characterized the first regulatory protein mediating denitrification growth and magnetite biomineralization in response to different oxygen conditions in a magnetotactic bacterium. Our findings reveal that the global oxygen regulator MgFnr is a genuine O2 sensor. It is involved in controlling expression of denitrification genes and thereby plays an indirect role in maintaining proper redox conditions required for magnetite biomineralization.
Magnetotactic bacteria (MTB) use magnetosomes for orientation in the Earth’s magnetic field to search for growth-favoring oxygen-limited zones of stratified aquatic habitats . In the freshwater alphaproteobacterium Magnetospirillum gryphiswaldense (in the following referred to as MSR-1) and other MTB, magnetosomes are membrane-enveloped magnetic crystals of magnetite (Fe3O4) that are aligned in chains . Magnetite biomineralization is not only controlled by more than 30 specific genes encoded within a genomic magnetosome island (MAI) [2–4], but also requires genes located outside MAI for synthesis of WT-like magnetosomes [5, 6]. Although the mechanism of biomineralization is not completely understood, it has been proposed that the biosynthesis of mixed-valence iron oxide magnetite [FeII(FeIII)2O4] occurs by coprecipitation of ferrous and ferric iron in supersaturating concentrations, which requires a balanced ratio of ferrous and ferric iron [7–9]. In magnetospirilla, magnetosome formation is only induced at low oxygen tension, and maximum magnetosome yield was found under microaerobic conditions in the presence of nitrate, whereas aerobic conditions completely inhibit magnetite biomineralization [5, 10]. However, it is unknown whether this aerobic repression is controlled by biological regulation, or alternatively, directly caused by chemical oxidation of iron ions within the cells. In addition, our recent work indicated that magnetite biomineralization in MSR-1 is linked to denitrification [5, 6]. Deletion of nap genes encoding a periplasmic nitrate reductase not only abolished anaerobic growth and delayed aerobic growth in both nitrate and ammonium medium, but also severely impaired magnetite biomineralization and resulted in biosynthesis of fewer, smaller and irregular crystals during denitrification and microaerobic respiration . In addition, loss of the nitrite reductase gene nirS led to defective growth of cells, which synthesized fewer, smaller and irregular crystals during nitrate reduction . Transcriptional gusA fusions revealed that expression of nap is upregulated by oxygen, whereas other denitrification genes including nirS, nor, and nosZ display the highest expression under microaerobic conditions in the presence of nitrate .
In many bacteria, changes in oxygen tension serve as an important environmental signal to trigger adaptive changes between anaerobic and aerobic respiration. This has been well studied in Escherichia coli where oxygen deprivation induces the synthesis of a number of enzymes, particularly those carrying out anaerobic respiration [11–15]. The alteration of gene expression to facilitate the changes in energy metabolism is achieved by Fnr (fumarate and nitrate reduction regulator), a global anaerobic regulator under anaerobic or microaerobic conditions [16, 17]. Fnr is a member of a superfamily of transcriptional sensors sharing sequence homology with the cyclic-AMP receptor class of proteins . Like all members of this family, Fnr protein comprises a C-terminal DNA-binding domain involved in site-specific DNA recognition of target promoters, and an N-terminal sensory domain . In E. coli, the sensor domain contains five cysteines, four of them (Cys-20, 23, 29, and 122) are essential and bind either a [4Fe-4S]2+ or a [2Fe-2S]2+ cluster [19–21]. Under anaerobic conditions, the Fnr protein is folded as a homodimer that contains one [4Fe-4S]2+ cluster per monomer. The Fnr dimers are able to bind target promoters and regulate transcription. Exposure of the [4Fe-4S]2+ clusters to oxygen results in its conversion to a [2Fe-2S]2+ oxidized form, which triggers conformational changes and further induces the protein monomerization and prevents its binding to DNA [22–28].
In the metabolically versatile MTB so far no oxygen regulators have been identified, and it is unknown how growth metabolism and magnetite biomineralization are regulated in response to different oxygen concentrations. Here, we for the first time identified a putative oxygen sensor MgFnr protein and analyzed its role in magnetite biomineralization. We showed that the MgFnr protein is involved in regulating expression of all denitrification genes in response to different oxygen concentrations, and thus plays an indirect role in magnetosome formation during denitrification. Although sharing similar characteristics with Fnr of other bacteria, MgFnr is able to repress the transcription of denitrification genes (nor and nosZ) under aerobic conditions, possibly owing to several unique amino acid residues specific to MTB-Fnr.
Deletion of Mgfnr impairs biomineralization during microaerobic denitrification
Crystal sizes in various strains under different conditions
Anaerobic nitrate medium
Microaerobic nitrate medium
38.0 ± 15.8 nm
30.5 ± 12.4 nm
40.2 ± 15.3 nm
21.9 ± 7.7 nm
WT + pLYJ110
30.3 ± 15.1 nm
23.5 ± 13.8 nm
ΔMgfnr + pLYJ110
42.1 ± 21.9 nm
30.3 ± 22.3 nm
WT + pLYJ153
31.7 ± 18.7 nm
30.0 ± 21.6 nm
ΔMgfnr + pLYJ153
40.9 ± 20.2 nm
31.3 ± 20.7 nm
In ΔMgfnr expression patterns of denitrification genes are different from those in WT
Effects of oxygen and nitrate on the expression of denitrification genes in ΔMgfnr mutant
+ NO3 -
- NO3 -
+ NO3 -
- NO3 -
79.5 ± 41.8a
67.0 ± 29.4
79.6 ± 38.5
85.4 ± 30.9
(16.2 ± 1.4)b
(15.9 ± 0.8)
(30.8 ± 2.6)
(28.6 ± 2.8)
266.3 ± 10.8
76.5 ± 28.3
85.4 ± 23.0
88.4 ± 54.9
(124.0 ± 5.5)
(21.2 ± 9.6)
(14.2 ± 7.9)
(18.3 ± 7.8)
414.7 ± 52.8
150.9 ± 52.4
559.7 ± 74.0
493.4 ± 52.9
(762.8 ± 37.0)
(221.5 ± 52.4)
(204.4 ± 41.1)
(151.1 ± 10.5)
327.8 ± 32.9
153.2 ± 62.5
751.3 ± 76.1
525.7 ± 53.6
(519.0 ± 43.4)
(118.3 ± 33.3)
(146.6 ± 34.7)
(152.5 ± 21.9)
Decreased N2 production in ΔMgfnr mutant is due to lower N2O reductase activity
Rates of N2O and N2 emission in WT and ΔMgfnr mutant after nitrate addition and rates of O2 consumption during aerobic respiration
Culture (2% oxygen)
WT without nitrate
50.7 ± 10.0
ΔMgfnr mutant without nitrate
44.0 ± 2.0
WT with nitrate
14.1 ± 2.0
0.7 ± 0.5
41.3 ± 2.0
ΔMgfnr mutant with nitrate
12.0 ± 2.0
0.4 ± 0.2
44.0 ± 4.7
Expression of Mgfnr is increased by oxygen and upregulated by itself
Under aerobic conditions, the expression of denitrification genes nor and nosZ was upregulated in the ΔMgfnr mutant, which suggested that MgFnr might be also active as repressor under aerobic conditions. Therefore, we first asked if transcription of the Mgfnr gene itself is under oxygen-dependent regulation. WT cells expressing Mgfnr-gusA showed the lowest β-glucuronidase activity under microaerobic conditions in the absence of nitrate, while the presence of nitrate slightly increased microaerobic expression of Mgfnr (Figure 4B). The expression of Mgfnr was induced approximately 4-fold in the presence of nitrate and more than 2-fold in the absence of nitrate under aerobic conditions relative to microaerobic conditions, which again suggested that MgFnr is likely active and acts as a repressor under aerobic conditions. In the ΔMgfnr mutant, Mgfnr-gusA also exhibited the highest β-glucuronidase activity under aerobic conditions in the presence of nitrate. However, compared to WT under aerobic conditions, expression levels of Mgfnr in ΔMgfnr mutant were significantly decreased, which indicated that expression of Mgfnr is also probably autoregulated. However, we failed to observe a putative Fnr binding site in the Mgfnr promoter region, implying other unknown proteins may be involved in the regulation of Mgfnr.
MgFnr can complement E. coli ΔEcfnr mutant
All previous observations were pointing towards a scenario, in which MgFnr may also repress expression of denitrification genes under aerobic conditions, which however has never been reported for any Fnr protein from other bacteria. Therefore, the question arose as to whether MgFnr is a genuine oxygen-responsive regulator. Consequently, an Ecfnr deletion mutant ΔEcfnr was transcomplemented with Mgfnr. As shown before , ΔEcfnr cells displayed deficient anaerobic growth when nitrate was used as the sole electron acceptor on lactate minimal medium, whereas they grew to similar yields as the WT anaerobically growing on glucose medium (Figure 4C). However, in the ΔEcfnr + pLYJ132 strain which contained the WT-Mgfnr gene, anaerobic growth in the presence of nitrate was restored back to E. coli WT-like level, which demonstrated that MgFnr is also functional in E. coli. Vice versa, the MSR-1 ΔMgfnr strain containing Ecfnr gene (ΔMgfnr + pLYJ153) generated N2 bubbles after 24 h (Figure 4A), suggesting that EcFnr also functions in MSR-1. As shown in Figure 2C and Table 1, ΔMgfnr + pLYJ153 strain containing Ecfnr again synthesized WT-like magnetite crystals. Under anaerobic conditions, overexpression of EcFnr resulted in a decrease in crystals size as overexpression of MgFnr does (Table 1, Additional file 1). However, when EcFnr was overexpressed in MSR-1 WT under microaerobic conditions, magnetite crystals with WT size were formed, contrary to what was observed with overexpression of MgFnr. Altogether, our observations suggested that MgFnr is a genuine oxygen sensor and displays an equivalent in vivo function as EcFnr in E. coli, but some functions of the MgFnr might be slightly distinct from the EcFnr.
MgFnr mutations N27D and I34L increase expression of nosZ under aerobic conditions
Measurements of Cmag, iron content, and crystal size for various Mgfnr strains in microaerobic nitrate medium
Magnetic response (Cmag)
Iron content (%)
Crystal size (nm)
2.22 ± 0.01
29.3 ± 18.6
1.78 ± 0.03
76.0 ± 0.06
20.7 ± 15.9
1.77 ± 0.02
83.6 ± 0.03
19.2 ± 18.9
1.83 ± 0.02
74.2 ± 0.07
21.3 ± 18.2
1.91 ± 0.02
95.6 ± 0.16
24.3 ± 19.9
1.93 ± 0.03
85.8 ± 0.14
23.6 ± 19.4
Our previous findings have implicated denitrification to be involved in redox control of anaerobic and microaerobic magnetite biomineralization [5, 6]. In E. coli and other bacteria the switch between aerobic and microaerobic respiration such as nitrate reduction is primarily controlled by the Fnr regulator [16, 17]. In this study, we have characterized the effect of the MgFnr protein on growth and magnetite biomineralization in MSR-1. Deletion of Mgfnr did not affect the growth yield, but impaired magnetosome formation under microaerobic conditions only in the presence of nitrate (i.e., when denitrification was active) but not in its absence. This implies that MgFnr might be involved in magnetite synthesis by regulation of denitrification genes, whereas expression of terminal oxidases for O2 respiration is likely not under the control of MgFnr, similar to Fnr from Shewanella oneidensis. In fact, we found that neither the rates of oxygen consumption nor transcription of terminal oxidase genes  displayed any difference between the WT and ΔMgfnr mutant. The presence of putative Fnr binding sites in the promoter regions of all operons of denitrification further indicates that MgFnr is involved in controlling the transcription of denitrification genes in response to different oxygen concentrations. Consistent with this, transcription patterns of denitrification genes in ΔMgfnr mutant were different from WT. For example, in the ΔMgfnr strain the expression of nap was no longer upregulated by oxygen, expression of nirS was much higher under aerobic conditions than WT, and aerobic expression of nor and nosZ was no longer repressed but upregulated by oxygen. Furthermore, we failed to identify a putative Fnr protein encoded in the genome of the nondenitrifying magnetotactic bacteria Magnetococcus marinus or Desulfovibrio magneticus strain RS-1, which also suggests that Fnr of MTB is likely only responsible to regulate genes encoding for denitrification, but not required for aerobic respiration. In addition, we also observed significantly decreased N2 evolution in deep slush agar tubes in ΔMgfnr mutant. This raised the question at which step(s) of denitrification is affected by the loss of MgFnr. We propose that this is not likely caused by the reduction steps from NO3 - to N2O based on the following observations: (i) The consumption rate of NO3 - and NO2 - did not decrease in ΔMgfnr mutant; (ii) NO is lethal to the cells while no defective growth was found in ΔMgfnr mutant, and no NO emission was observed during mass spectrometry experiments which also implies that the activity of NO reductase is not decreased; (iii) The N2O emission rate after addition of nitrate was similar for ΔMgfnr mutant and WT. Therefore, we conclude that loss of MgFnr affects the last step of denitrification, the reduction of N2O to N2. In agreement, the emission rate of N2 was lower for ΔMgfnr mutant than for the WT. However, we cannot exclude the possibility that loss of MgFnr has an impact on further pathways involved in biomineralization other than denitrification. For instance, we have previously shown that (i) besides acting as nitrate reductase, Nap also plays a role in redox control for magnetosome formation, (ii) nitrite reductase NirS is capable to oxidize ferrous iron to ferric iron for magnetite synthesis, and (iii) NO reductase Nor also participates in magnetosome formation by yet unknown functions [5, 6]. On the other hand, in the magnetotactic Magnetovibrio blakemorei strain MV-1 which is capable of anaerobic respiration with N2O as electron acceptor, a putative periplasmic Fe (II) oxidase was identified and proposed as N2O reductase NosZ , which suggests that N2O reductase might be also involved in magnetite biomineralization by unknown functions. In addition, in ΔMgfnr mutant the different phenotypes observed under anaerobic and microaerobic conditions in the presence of nitrate indicate that MgFnr plays a more important role in magnetite biomineralization when O2 respiration and denitrification occur simultaneously. Our recent findings showed that maintaining a balance between aerobic respiration and denitrification is crucial for WT-like magnetite biomineralization . In this case, MgFnr might provide the main contribution to mediate the expression of denitrification genes and therefore, poise the redox state for magnetosome formation.
Since deletion of Mgfnr altered oxygen-dependent regulation of denitrification genes under aerobic conditions, we hypothesized that MgFnr protein is active under aerobic conditions. Consistent with this, the expression of Mgfnr was upregulated by oxygen, which, however, was never reported for any Fnr protein from other bacteria. Studies on EcFnr mutants in E. coli have established the important role of a [4Fe-4S]2+ cluster in regulating EcFnr activity, and some single amino acid substitutions at positions not conserved in the Fnr family led to increased stability of Fnr to oxygen and activated transcription of nitrate reductase genes under aerobic growing conditions [24, 25, 30, 32, 36]. None of these reported amino acids of EcFnr are conserved in MgFnr, which might cause a more active MgFnr under aerobic conditions. Among them, Asn-27 and Ile-34 of MgFnr are located very closely to Cys-28 and Cys-37, two of the four cysteine residues that bind the [4Fe-4S]2+ cluster [37, 38]. An E. coli EcFnr mutant protein containing amino acid substitution at either of these two positions showed increased expression of an EcFnr-dependent lac promoter under aerobic conditions [30, 32, 36]. In agreement with these observations, MgFnr mutants including N27D and I34L showed increased aerobic expression of nosZ promoter, suggesting that Asn-27 and Ile-34 of MgFnr are required for a functional MgFnr and likely play a role in maintaining the stability of [4Fe-4S]2+ cluster. However, MgFnr was able to complement ΔEcfnr mutant back to WT-like growth, which indicates that MgFnr also has the universal properties of EcFnr. Nonetheless, ΔEcfnr mutant and ΔMgfnr mutant displayed significantly different phenotypes during anaerobic growth, such as a largely decreased growth yield in ΔEcfnr mutant, but no defective growth in ΔMgfnr mutant. These differences might be explained by different media used for cultivation because in E. coli deletion of Ecfnr only resulted in growth defect in some minimal media  while there is no minimal medium available, which provides reliable growth for MSR-1. In addition, not only deletion of Mgfnr but also overexpression of Mgfnr in WT affected anaerobic and microaerobic magnetite biomineralization in the presence of nitrate and caused the synthesis of smaller magnetosome particles, which indicates that the balanced expression of MgFnr is crucial for WT-like magnetosome synthesis and the expression level is under precise control, be regulated by oxygen. Therefore, MgFnr might play an important role in maintaining redox balance for magnetite synthesis by controlling the expression of denitrification genes, and thus the expression of MgFnr is required to be strictly regulated. On the other hand, since MgFnr serves as an activator for expression of denitrification genes (nor and nosZ) under microaerobic conditions while as a repressor on the same genes under aerobic conditions, it is proposed that other oxygen sensors involved in expression of nor and nosZ are regulated by MgFnr. For example, a NosR protein has been shown to be required to activate the transcription of nos gene in Pseudomonas stutzeri. However, our data cannot rule out the possibility that MgFnr is also regulated by other yet unknown proteins and that other genes involved in magnetosome formation is controlled by MgFnr.
We demonstrated for the first time that MgFnr is a genuine oxygen regulator in a magnetotactic bacterium and mediates anaerobic respiration. The expression of MgFnr is required to be precisely controlled, which is regulated by oxygen. In addition, MgFnr is also involved in regulation of magnetite biomineralization during denitrification, likely by controlling proper expression of denitrification genes. This allows the transcription to be adapted to changes in oxygen availability, and thus maintaining proper redox conditions for magnetite synthesis. Despite of general similarities with Fnr proteins from other bacteria, MgFnr is more insensitive to O2 and further displays additional functions for aerobic conditions, which might result from some non-conserved amino acids.
Although oxygen is known to be a major factor affecting magnetite biomineralization for decades, the mechanism of this effect in MTB is still unknown. The common observation that magnetosomes are only synthesized under oxygen-limited conditions raised the possibility of protein-mediated regulation of the biomineralization process. However, although MgFnr mediates oxygen-dependent regulation, its relatively subtle and indirect effects on magnetite biomineralization cannot account for the observed complete inhibition of magnetite biosynthesis under aerobic conditions. In addition to a possible effect caused by directly perturbing the redox balance of iron ions required for magnetite synthesis, another level of genetic regulation may exist in MSR-1. Since MgFnr only affects expression of denitrification genes but not genes encoding O2 respiration enzymes, magnetite biomineralization is also probably regulated by other unknown O2 sensors. Therefore, further research on respiratory pathways in MTB is likely to gain more insights into the mechanism of oxygen-dependent regulation of biomineralization.
Bacterial strains and growth conditions
Bacteria strains and plasmids used in this study are shown in Additional file 5. If not specified otherwise, E. coli strains were grown in lysogeny broth (LB) at 37°C, and MSR-1 strains were cultivated at 30°C in nitrate medium as described before . In ammonium medium, nitrate was substituted by 4 mM ammonium chloride. When necessary, antibiotics were used at the following concentrations: E. coli: tetracycline (Tc), 12 μg/ml, kanamycin (Km), 25 μg/ml, and gentamicin (Gm), 15 μg/ml; MSR-1: Tc, 5 μg/ml, Km, 5 μg/ml, and Gm, 30 μg/ml. When E. coli strain BW29427 was used as donor in conjugation, 300 μM diaminopimelic acid (DAP) was added.
Experiments for growth and magnetic response (Cmag) were monitored under microaerobic and anaerobic conditions in 250 ml flasks containing 100 ml media. For microaerobic conditions, flasks were sealed with butyl-rubber stoppers under a microaerobic gas mixture containing 2% O2 and 98% N2 before autoclaving. Anaerobic conditions were achieved by removing oxygen from gas mixture. For aerobic conditions, strains were cultured in free gas exchange with air in 300 ml flasks containing 20 ml medium agitated at 200 rpm. Optical density (OD) and magnetic response (Cmag) were measured photometrically at 565 nm as previously described . For gas production assay, cells were inoculated and mixed with nitrate medium with 0.3% agar in oxygen gradient tubes and exposed to the air.
Genetic and molecular biology techniques
Standard molecular and genetic techniques were carried out for DNA isolation, digestion, ligation, and transformation . All DNA products were sequenced using BigDye Terminator version 3.1 chemistry on an ABI 3700 capillary sequencer (Applied Biosystems, Darmstadt, Germany), and sequence data were analyzed with the software Vector NTI Advance® 11.5.1 (Invitrogen, Darmstadt, Germany). All oligonucleotide sequences used in this work are available if required.
Construction of a MSR-1 ΔMgfnr deletion mutant
All PCRs were performed using Phusion polymerase (NEB). Enzymes, including restriction enzymes and T4 DNA ligase, were purchased from Fermentas. To generate the unmarked ΔMgfnr deletion mutant, a modified cre-lox method was used as previously described . An about 2-kb downstream PCR fragment of Mgfnr was generated and cloned into NotI/EcoRI-digested pAL01 to obtain pLYJ106. The plasmid pLYJ106 was conjugationally integrated into the chromosome of MSR-1 and colonies screened positively by PCR for the presence of the kanamycin marker were designated ΔMgfnr-down strain. Subsequently, the plasmid pLYJ105 containing a 2-kb upstream fragment of Mgfnr was integrated into the chromosome of ΔMgfnr-down strain by conjugation. After verified by screening PCR for the presence of kanamycin and gentamicin markers, the strain was designated ΔMgfnr-up-down strain. The lox-mediated excision of Mgfnr was initiated by conjugational transformation of pLYJ87 . Precise excision was further confirmed by PCR amplification and sequencing. The plasmid pLYJ87 was lost by successive cultures in fresh nitrate medium. Finally, this strain was designated ΔMgfnr mutant.
For genetic complementation of ΔMgfnr mutant, the Mgfnr gene with its own promoter region was ligated into Acc65I/SacII-digested pBBR1MCS-2, yielding pLYJ110. Subsequently, pLYJ110 was transformed into MSR-1 WT and ΔMgfnr mutant by conjugation. The Ecfnr gene from E. coli K-12 was also hetero-complemented into ΔMgfnr mutant and WT. The PCR fragment of Ecfnr from E. coli was digested with HindIII and XbaI and ligated into pLYJ36 to yield pLYJ153.
Heterologous transcomplementation of an E. coli ΔEcfnr mutant
First, ΔEcfnr mutant with kanamycin marker was excised with the E. coli Quick and Easy gene deletion kit (Gene Bridges) and the Bac modification kit (Gene Bridges), as reported in . This unmarked mutant was designated ΔEcfnr mutant. To express MgFnr protein from MSR-1, Mgfnr was ligated into SmaI/XbaI-digested pBBR1MCS-2 to yield pLYJ132. Plasmid pLYJ132 was then transformed into ΔEcfnr mutant. For transcomplementation analysis, strains were anaerobically grown in glucose minimal medium and lactate minimal medium .
Construction of different Mgfnr variants
Substitutions at amino acid positions 27, 34, 98, and 153 were created by site-directed mutagenesis. First, PstI-SpeI digested fragment for each of substitutions was cloned into pOR093 to create pLYJ141 (Mgfnr-N27D), pLYJ142 (Mgfnr-I34L), pLYJ143 (Mgfnr-D153E), and pLYJ144 (Mgfnr-L98H), respectively. The different MgFnr mutants were subsequently obtained by a two-step homologous recombination technique in the same manner as described previously . The Mgfnr variants were confirmed by PCR and sequencing.
Analysis of transcriptional gusA fusions
To obtain the transcriptional Mgfnr-gusA fusion plasmid, Mgfnr promoter region was cloned into Acc65I/HindIII-digested pLYJ97, designated pLYJ109. To investigate the expression of Mgfnr under different conditions, β-glucuronidase activity was determined at 37°C as described before . Units were recorded as nanomoles of product formed per minute per mg protein. Triplicate assays were measured and the values reported were averaged by using at least two independent experiments.
To determine the concentration of intracellular iron, cell pellet was washed twice with 1200 μl HEPES buffer (20 mM HEPES, 5 mM EDTA) to remove absorbed iron. After resuspended with 100 μl 65% HNO3, this mixture was incubated at 98°C for 3 h. When the sample cooled down to room temperature, 900 μl H2O was added for ferrozine assay as described before . Briefly, the total Fe-content was determined by complete reduction of iron with hydroxylamine hydrochloride. This dissolved ferrous iron was further reacted with three ferrozine molecules to form an intensively purple-colour complex, which can be quantified spectrophotometrically at 562 nm.
Nitrate and nitrite concentration assay
WT and ΔMgfnr strains were grown under microaerobic conditions in the presence of nitrate. 1 ml culture at different time points was taken to detect nitrate and nitrite concentration as described in . Nitrate was measured using Szechrome reagents (Polysciences, Inc.). Diluted 20-fold samples were mixed with equal modified Szechrome reagents and the absorbance recorded at 570 nm after 30 min. When nitrate was not detectable, cultures without dilution were detected to confirm the absence of nitrate. A nitrate standard curve (0–350 μM) was generated to convert absorbance values to concentrations. Nitrite was examined by the modified Griess reagent (Sigma). 100 μl diluted 20-fold samples of cultures were prepared and equal modified Griess reagent was subsequently added. The absorbance recorded at 540 nm after 15 min. When no nitrite was detected, cultures without dilution were detected to confirm the absence of nitrite. A nitrite standard curve (0–70 μM) was obtained to calculate final nitrite concentration. Duplicate assays were carried out and the values reported were measured in one representative experiment.
Mass spectrometry measurements of O2 respiration and nitrate reduction
WT and ΔMgfnr strains were grown under microaerobic conditions in the presence or absence of nitrate. The cells were centrifuged and resuspended in fresh ammonium medium. Then the suspension was placed in the measuring chamber (1.5 ml) of a mass spectrometer (model PrimaδB; Thermo Electron). The bottom of the chamber (Hansatech electrode type) was sealed by a Teflon membrane, allowing dissolved gases to be directly introduced through a vacuum line into the ion source of the mass spectrometer. The chamber was thermostated at 28°C, and the cell suspension was stirred continuously by a magnetic stirrer. For O2 respiration measurement, air was sparged into the suspension before chamber closing. The consumption of oxygen by the cells was followed at m/e = 32. For denitrification, the cells were sparged with Argon and nitrate reduction was measured using 2 mM K15NO3 (CEA 97.4% 15 N). NO, N2O and N2 concentrations were followed as a function of time.
TEM and crystal analysis
If not specified, MSR-1 WT and mutants were grown at 30°C under anaerobic or microaerobic conditions for 20 h, concentrated and adsorbed onto carbon-coated copper grids. Samples were viewed and recorded with a Morgagni 268 microscope (FEI, Eindhoven, Netherlands) at 80 kV. For magnetosome analysis, more than 300 crystals were characterized for each strain.
fnr genes were identified by BLASTP (http://www.blast.ncbi.nlm.nih.gov/Blast.cgi) homology searching in the genomes of MSR-1 (GenBank: CU459003.1), M. magneticum (GenBank AP007255.1), M. magnetotacticum (NCBI reference sequence NZ_AAAP00000000.1), Mc. marinus (GenBank accession number CP000471.1), and D. magneticus strain RS-1 (GenBank accession number AP010904.1). ClustalW was used for sequence alignment. The identification of Fnr binding sites in the promoter regions of the different operons encoding denitrification enzymes were performed with the virtual footprint software (PRODORIC, http://www.prodoric.tu-bs.de/vfp/index2.php).
We thank Kirsten Jung, Ludwig-Maximilians-Universität München, for strain ΔEcfnr mutant. The China Scholarship Council (CSC) is greatly acknowledged for the financial support of Y. Li, and the Brazilian CNPq program for the financial support of K. T. Silva. This work was supported by grants DFG Schu1080/11-1 and 15–1, and HFSP RGP0052/2012 to D. Schüler.
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