Rhodopseudomonas palustris TIE-1 is a metabolically versatile bacterium that can use various electron donors, including Fe(II) and poised electrodes, for photoautotrophic growth. TIE-1 can produce useful biomolecules, such as biofuels and bioplastics, under various growth conditions. Production of such reduced biomolecules is controlled by intracellular electron availability, which, in turn, is mediated by various iron-containing proteins in the cell. Several putative Fe transporters exist in TIE-1’s genome. Some of these transporters can also transport Mn, part of several important cellular enzymes. Therefore, understanding the ability to transport and respond to various levels of Fe and Mn under different conditions is important to improve TIE-1’s ability to produce useful biomolecules. Our data suggest that by overexpressing Fe transporter genes via plasmid-based expression, we can increase the import of Fe and Mn in TIE-1. Future work will leverage these data to improve TIE-1 as an attractive microbial chassis and future biotechnological workhorse.
KEYWORDS: Rhodopseudomonas palustris TIE-1, biofuels and bioplastics, bioproduction, efeU, feoAB, iron transporters, microbial chassis
ABSTRACT
The purple nonsulfur bacterium Rhodopseudomonas palustris TIE-1 can produce useful biochemicals such as bioplastics and biobutanol. Production of such biochemicals requires intracellular electron availability, which is governed by the availability and the transport of essential metals such as iron (Fe). Because of the distinct chemical properties of ferrous [Fe(II)] and ferric iron [Fe(III)], different systems are required for their transport and storage in bacteria. Although Fe(III) transport systems are well characterized, we know much less about Fe(II) transport systems except for the FeoAB system. Iron transporters can also import manganese (Mn). We studied Fe and Mn transport by five putative Fe transporters in TIE-1 under metal-replete, metal-depleted, oxic, and anoxic conditions. We observed that by overexpressing feoAB, efeU, and nramp1AB, the intracellular concentrations of Fe and Mn can be enhanced in TIE-1 under oxic and anoxic conditions, respectively. The deletion of a single gene/operon does not attenuate Fe or Mn uptake in TIE-1 regardless of the growth conditions used. This indicates that genetically dissimilar yet functionally redundant Fe transporters in TIE-1 can complement each other. Relative gene expression analysis shows that feoAB and efeU are expressed during Fe and Mn depletion under both oxic and anoxic conditions. The promoters of these transporter genes contain a combination of Fur and Fnr boxes, suggesting that their expression is regulated by both Fe and oxygen availability. The findings from this study will help us modulate intracellular Fe and Mn concentrations, ultimately improving TIE-1’s ability to produce desirable biomolecules.
IMPORTANCE Rhodopseudomonas palustris TIE-1 is a metabolically versatile bacterium that can use various electron donors, including Fe(II) and poised electrodes, for photoautotrophic growth. TIE-1 can produce useful biomolecules, such as biofuels and bioplastics, under various growth conditions. Production of such reduced biomolecules is controlled by intracellular electron availability, which, in turn, is mediated by various iron-containing proteins in the cell. Several putative Fe transporters exist in TIE-1’s genome. Some of these transporters can also transport Mn, part of several important cellular enzymes. Therefore, understanding the ability to transport and respond to various levels of Fe and Mn under different conditions is important to improve TIE-1’s ability to produce useful biomolecules. Our data suggest that by overexpressing Fe transporter genes via plasmid-based expression, we can increase the import of Fe and Mn in TIE-1. Future work will leverage these data to improve TIE-1 as an attractive microbial chassis and future biotechnological workhorse.
INTRODUCTION
Iron (Fe) and manganese (Mn) are essential nutrients for biological processes (1–3). Because of the unique redox properties of Fe, it plays an important role as a cofactor in enzymes involved in a variety of cellular processes (4). Similarly, Mn plays an essential role in lipid, protein, and carbohydrate metabolism (5). It also serves as a cofactor of Mn-dependent superoxide dismutase and can contribute to the catalytic detoxification of reactive oxygen species (ROS) (5–7). However, when in excess, these metals are toxic to cells. An evaluation of Fe toxicity revealed that the presence of 1 mM Fe(III) and 0.5 mM Fe(II) can significantly affect the growth of Escherichia coli (8). Such elevated concentrations can perturb intracellular redox conditions and produce reactive hydroxyl radicals (1). Likewise, excess Mn can inactivate enzymes that use other divalent ions. Mn is known to replace Fe from cellular proteins (6, 7). Therefore, the function of many Fe-containing proteins (e.g., cytochromes, dehydrogenases, and iron-sulfur proteins), which are involved in diverse cellular processes, may be affected due to replacement of Fe by Mn when a very high level of Mn is present (9). The interplay of the need and the toxicity of these metals forces organisms to carefully maintain metal homeostasis. This ensures that metal availability is in accordance with their physiological needs (1). This homeostasis is largely maintained by regulating specific metal transport systems across all biological systems (4, 10–17).
Depending on oxygen availability in the environment, iron exists in two forms: ferric [Fe(III)] and ferrous [Fe(II)]. In oxic environments, most bacteria acquire insoluble Fe(III) by synthesizing high-affinity Fe(III) siderophores via a process that involves multienzyme pathways (1, 18–20). In contrast, Fe(II) uptake is much simpler and involves direct transportation of Fe(II) into the cytoplasm through distinct Fe(II) transporters (21–23). Likewise, depending on oxygen availability, manganese is also found in two most stable forms: Mn(II) and Mn(IV). In many cases, Fe(II) transporters can also transport Mn(II) across the cytoplasmic membrane (24, 25). Although Fe(III) transport systems are well understood, we know much less about Fe(II) transport systems (except for the FeoAB system) and their ability to transport Mn(II) in bacteria, which is the focus of this study.
In this investigation, we studied Fe and Mn transport in a metabolically versatile anoxygenic phototroph Rhodopseudomonas palustris TIE-1. Depending on the availability of different energy and carbon sources, TIE-1 can perform multiple modes of metabolisms, such as photoautotrophy, photoheterotrophy, chemoautotrophy, and chemoheterotrophy (26–28). Similar to the other strains of Rhodopseudomonas that have been used to produce value-added compounds (29–34), TIE-1 can also produce compounds, such as bioplastics and biofuels, under various growth conditions (35; W. Bai, T. O. Ranaivoarisoa, R. Singh, K. Rengasamy, and A. Bose, submitted for publication). Electron transfer during the synthesis of these compounds requires Fe-containing proteins, such as cytochromes. The activity of such proteins depends on the bioavailability and the transport of Fe (28, 35, 36).
We studied the role of five genes (feoAB, efeU, nramp1AB, nramp3AB, and sitABC) that encode Fe(II) transporters in TIE-1 to import Fe and Mn under metal-replete and -depleted conditions with respect to oxygen availability. Using heterologous complementation, mutant analysis, and gene expression analysis, we showed that by manipulating TIE-1’s Fe transport systems, we can enhance its ability to acquire Fe and Mn. Identifying such key transporters might be beneficial for developing TIE-1 as a bioproduction chassis.
RESULTS
TIE-1 possesses six putative ferrous iron transporter genes.
We identified six putative Fe(II) transporters in TIE-1 using whole-genome homology searches for previously characterized Fe(II) transport systems from E. coli and R. palustris CGA009 (Fig. 1). The first is the Fe(II)-specific FeoAB system. Unlike E. coli, TIE-1 contains only FeoA and FeoB and not FeoC. However, the Feo system lacking FeoC is fully functional for Fe(II) uptake in several bacteria (37). The second Fe(II)-specific transport system is EfeU, which is a member of the oxidase-dependent iron transporters (OFeT) and is a homolog of the iron permease Ftr1p from yeast (38). It is a part of the efeUOB tricistronic operon, which is expressed in response to Fe availability in E. coli (24). The third system is SitABC (SitD is absent), which has been reported to have a much greater affinity for Mn than Fe (39). Fe- and Mn-dependent regulation of sitABC operon has been previously described for Staphylococcus epidermidis (40) and Staphylococcus aureus (41), respectively. The fourth transport system belongs to the natural resistance-associated macrophage protein (NRAMP) family. We found three nramp gene/operons: nramp1AB, nramp2, and nramp3AB, which are also known to be important for Fe and Mn uptake and homeostasis in other organisms (42, 43). Nramp1A belongs to the DNA binding transcriptional regulator LysR family, whereas Nramp3A is a hypothetical protein (Rpal_3713) that is predicted only for the genomes of TIE-1 and the related strain CGA009 (Fig. 1E). Nramp1B, Nramp2, and Nramp3B belong to a Mn transporter protein family, MntH from E. coli (42, 43). Because we were unable to delete nramp2 from TIE-1, we excluded nramp2 from our studies.
FIG 1.
Genomic organization of R. palustris TIE-1 genes that are likely involved in Fe(II) transport. Six candidates’ loci were identified (A to F). The genes of interest are shown in black with their names bolded. Other genes are shown in gray with their locus tags, searchable at https://img.jgi.doe.gov/cgi-bin/w/main.cgi.
Putative ferrous iron transport systems from TIE-1 can rescue iron transport deficiencies in a heterologous host.
To assess whether the putative Fe(II) transporters support iron uptake, we performed two heterologous-complementation experiments with E. coli as an initial test. For the first complementation experiment, we used E. coli H1771, a mutant defective for the Feo system and siderophore biosynthesis with a chromosomal fhuF-lacZ (encoding β-galactosidase) reporter system. This reporter system has been previously used in similar studies (44–46). The fhuF promoter of the reporter system is responsive to Fe, where repression of β-galactosidase activity represents adequate intracellular Fe concentration while an increase in β-galactosidase activity indicates Fe starvation (47, 48).
The identified Fe transporter genes/operons from TIE-1 were cloned into the low-copy-number vector pWKS30 (47) and were driven by the constitutive promoter PaphII (49). We have also recently reported gene expression using the PaphII promoter in TIE-1: we produced PioA in TIE-1 in a pioA deletion TIE-1 background using this promoter and confirmed protein expression by Western blotting (36). To further confirm the efficiency of the PaphII promoter, we built a plasmid in which mCherry was driven by PaphII. TIE-1 carrying this plasmid showed a 5,000-fold-higher fluorescence signal (normalized to optical density at 600 nm [OD600]) than wild-type (WT) TIE-1 (see Fig. S1 in the supplemental material). This promoter has been also used previously in a closely related organism, Rhodobacter capsulatus (50).
Plasmids carrying the transporter genes were then transformed into E. coli H1771, and β-galactosidase (reporter) activity was assayed under four different conditions, namely, (i) Fe(III) replete [50 μM Fe(III)-citrate], (ii) Fe(III) depleted [50 μM Fe(III)-citrate with 100 μM 2,2′-dipyridyl (DiP)], (iii) Fe(II) replete [50 μM ascorbate-reduced Fe(III)-citrate], and (iv) Fe(II) depleted [50 μM ascorbate-reduced Fe(III)-citrate with 100 μM DiP]. The membrane-permeant chelator DiP was used to control the bioavailability of Fe(II) and Fe(III). DiP is a Fe(II)-specific bidentate organic ligand that acts by directly depleting intracellular stores of ferrous iron (51). The inherent fhuF-lacZ reporter system of E. coli H1771 carrying an empty vector expressed lacZ to a full extent due to a low intracellular Fe concentration (Fig. 2). E. coli H1771 complemented with K-12 feoABC through a plasmid served as a positive control and showed more than an 80% decrease in lacZ expression as determined by β-galactosidase activity compared to the vector control under all conditions (Fig. 2). Regardless of different Fe(III) concentrations and transporter genes from TIE-1, none of the complemented E. coli H1771 strains showed significant changes in β-galactosidase activity (Fig. 2). In contrast, all the complemented strains under Fe(II)-replete conditions showed a lower β-galactosidase activity (Fig. 2C) than both the vector control and the activities under Fe(II)-depleted conditions (Fig. 2D). The most pronounced difference in the β-galactosidase activity compared to the empty vector was observed for the efeU-complemented strain under Fe(II)-replete conditions (62% lower than the vector control) (Fig. 2C).
FIG 2.
E. coli H1771 complementation by selected iron transport genes resulted in less iron stress when grown in Fe(II) supplied LB medium but had no effect when grown in Fe(III)-supplied LB medium. The Miller β-galactosidase assay was used to determine the level of iron stress. Four conditions were used: Fe(III) replete [50 μM Fe(III)-citrate] (A), Fe(III) depleted [50 μM Fe(III)-citrate with 100 μM 2,2′-dipyridyl (DiP)] (B), Fe(II) replete [50 μM ascorbate-reduced Fe(III)-citrate] (C), and Fe(II) depleted [50 μM ascorbate-reduced Fe(III)-citrate with 100 μM DiP] (D). Cells at the exponential phase were used for all assays. Values are represented as means ± standard errors from six independent biological measurements. The number on each bar represents the percent reduction (normalized to empty vector control) of Miller β-galactosidase activity. The x axis shows the genes used for complementation. TIE-1, Rhodopseudomonas palustris TIE-1; Ec, E. coli K-12.
To further confirm the role of the putative Fe(II) transporters in cell growth, we employed a second heterologous-complementation experiment using E. coli GR536. E. coli GR536 is a mutant lacking all five known Fe transport systems (ΔfecABCDE::kan ΔzupT::cat, ΔmntH, ΔfeoABC, and ΔentC), and therefore, it is unable to grow under Fe-depleted conditions (52). We expressed the Fe(II) transporter genes from TIE-1 in this heterologous host and examined if their expression can rescue the growth defect of E. coli GR536 under Fe-depleted conditions (Fig. 3A to E). Indeed, complementation of E. coli GR536 with efeU, nramp1AB, nramp3AB, and sitABC from TIE-1 restored its growth to various degrees after ∼60 h (Fig. 3B to E). In contrast, although the growth defect was rescued by complementation with feoABC from E. coli K-12 (a positive control) within 24 h (Fig. 3F), the expression of the FeoAB system from TIE-1 could not rescue the growth defect (Fig. 3A). This result suggests that all three genes of the Feo system, including the FeoC gene, are important for Fe transport in E. coli.
FIG 3.
Complementation with selected Fe(II) transport genes aid growth of E. coli GR536 mutant (which lacks all known iron transport genes) during severe iron deprivation (in Tris-mineral salts medium at pH 7.0 with no added iron). E. coli GR536 was complemented by Rhodopseudomonas palustris TIE-1 feoAB (A), TIE-1 efeU (B), TIE-1 nramp1AB (C), TIE-1 nramp3AB (D), and TIE-1 sitABC (E) and E. coli K-12 feoABC (positive control) (F). Two representative growth conditions are shown: without and with 150 μM DiP. Empty vector was used as a control for both conditions. Growth was measured as OD600. Values represent the means ± standard deviations from biological triplicates.
Putative ferrous iron transporters from TIE-1 do not transport zinc, cadmium, or copper.
Based on previous studies, the FeoAB and EfeU transporters are predicted to be specific for Fe uptake, while the Nramp and Sit systems are known to also transport other divalent cations (39, 42, 53, 54). Therefore, we further investigated the metal specificity of these putative Fe transporters in TIE-1. Although DiP is a strong intracellular Fe(II) chelator, it also binds to other divalent metals, such as copper [Cu(II)], cadmium [Cd(II)], and zinc [Zn(II)] (55). Because of this broader metal binding capacity of DiP, we further used this chelator in studying the metal specificity of these transport systems. Heterologous complementation was performed in two different strains: (i) E. coli GG48, which lacks key Zn transport genes, and (ii) E. coli ΔcopA ΔcueO ΔcusCFBA::cat, which lacks the key Cu transport genes (56). Complementation of these E. coli hosts with a functional Zn/Cu/Cd transport system is detrimental and is reflected by a lower growth rate when these metals are provided in the growth medium (56). We then determined the ability of the putative Fe(II) transport systems from TIE-1 to transport Zn(II), Cd(II), and Cu(II) by monitoring the growth rate of the heterologous E. coli host complemented with plasmids expressing TIE-1’s putative Fe(II) transporters compared to the control strain (Table 1; P ≤ 0.05). These data suggest that the TIE-1 Fe(II) transporters had either no effect or a positive effect on the growth rate of E. coli. The increase in growth rate could have accounted for the ability of these transporters to bring in extracellular Fe into the cell. The only case where we observed a negative effect on growth rate was under the Cd/Cu-supplemented conditions for E. coli ΔcopA ΔcueO ΔcusCFBA::cat complemented with the E. coli feoABC system. Overall, these data suggest that the TIE-1’s Fe transport systems do not import enough Zn/Cu/Cd into these E. coli mutant strains to observe a severe growth defect. The result implies that these TIE-1 Fe transport systems likely have a low affinity for Zn/Cu/Cd.
TABLE 1.
Metal specificity tests using E. coli GG48 for Zn and E. coli ΔcopA ΔcueO ΔcusCFBA::cat for Cd and Cu transformed with plasmids with genes encoding Fe transporters from R. palustris TIE-1 or E. coli K-12a
| Gene/operon | Zn | Cd | Cu |
|---|---|---|---|
| R. palustris TIE-1 | |||
| feoAB | 0 | + | 0 |
| efeU | 0 | 0 | 0 |
| nramp1AB | + | 0 | 0 |
| nramp3AB | 0 | + | 0 |
| sitABC | 0 | + | 0 |
| E. coli K-12 | |||
| feoABC | + | − | − |
A “0” indicates no significant difference in growth from the empty vector control (P > 0.05), “+” a significantly higher growth rate for the experimental strain versus that of the control, and “−” a significantly lower growth rate versus that of the control (P ≤ 0.05).
Overexpression of ferrous iron transporter genes increases intracellular iron and manganese in TIE-1 under oxic and anoxic conditions.
After confirming the role of the putative Fe(II) transporters in Fe transport and growth of the heterologous host E. coli, we sought to investigate their role in Fe and Mn accumulation in the native organism TIE-1. We constructed markerless deletions of these genes in TIE-1 as described in Materials and Methods (27). We were unable to obtain some of the mutants despite screening >100 colonies. These include feoA, feoB, nramp1A, nramp2, and sitA mutants. We tested the ability of the five obtained mutants (ΔfeoAB, ΔefeU, Δnramp1AB, Δnramp3AB, and ΔsitABC mutants), their complemented strains (each complemented by corresponding genes), and the WT (positive control) to intracellularly accumulate Fe and Mn under anoxic, oxic, metal-replete, and metal-depleted conditions. The complemented transporter genes were expressed using the same plasmid, from the same PaphII promoter and ribosome binding site as described above. Therefore, we assume that the expression level for each gene is similar. We quantified intracellularly accumulated Fe and Mn using inductively coupled plasma mass spectrometry (ICP-MS). The results are expressed as the ratio of metal accumulated by a strain normalized to the metal accumulated by the wild-type control strain. We did not observe any metal precipitation during our experiments.
TIE-1 is an ideal candidate to study Fe and Mn uptake due to its ability to grow under both oxic and anoxic conditions, which allowed us to study Fe(II), Fe(III), Mn(II), and Mn(IV) transport systems using the same organism. Although the ideal conditions to study the transport of these metal species is to use the same growth medium, we had to grow TIE-1 aerobically on yeast-peptone (YP) medium and anaerobically on defined freshwater (FW) medium as described in Materials and Methods. This is because TIE-1 does not grow robustly in YP medium under anoxic conditions or in FW medium under oxic conditions. Such different growth conditions have recently been used in a Fe transport study in Shewanella oneidensis (57). To further control the bioavailability of Fe and Mn, two different chelators, EDTA and DiP, were tested for all conditions. Being membrane-permeant (58), DiP has the potential to diffuse into cells and alter the intracellular metal distribution (59). It has stability constants of 17.5 and 16.3 with Fe(II) and Fe(III), respectively, and 6 with Mn(II) (60, 61). In contrast, EDTA is a large molecule that is membrane impermeant (58). In addition, the presence of two nitrogen atoms and four carboxyl groups in EDTA’s structure makes it a strong metal chelator for iron [stability constants, 25.10 with Fe(III) and 14.33 with Fe(II)] and manganese [stability constants, 24.80 with Mn(III) and 14.04 with Mn(II)] (59). Due to its inability to enter cells, it can only bind to extracellular Fe or Mn via metal-ligand interaction, eventually limiting their transports (58). Our results indicate that the complemented strains accumulate amounts of Fe comparable to those accumulated by the WT and the mutant strains under anoxic growth conditions. When Fe was depleted by adding EDTA or DiP under anoxic conditions, growth was suppressed (OD660, ∼0.1 [Fig. S2]) and Fe acquisition was abolished (Fig. 4A to E). Two exceptions were with the Δnramp3AB and ΔsitABC mutants, for which growth was observed with EDTA and/or DiP in the mutants but not in the WT or the complemented mutants (Fig. S2). Because we could not obtain a measurable metal concentration from the WT, with which we normalized the other values, we could not report the Fe concentration from the Δnramp3AB and ΔsitABC mutants during growth with EDTA and/or DiP.
FIG 4.
Fe acquisition by Rhodopseudomonas palustris TIE-1 mutants, complemented strains, and WT under Fe-replete, Fe-depleted, oxic, and anoxic conditions using inductively coupled plasma mass spectrometry (ICP-MS). The iron content of the cell is normalized to the Fe acquisition by the WT. (A to E) Fe acquisition under anoxic conditions. (F to J) Fe acquisition under oxic conditions. Values represent the means ± standard deviations from biological triplicates. FWS, freshwater media supplemented with 1 mM succinate; YPS, yeast-peptone supplemented with 1 mM succinate; NG, no growth. *, conditions under which an OD660 of >0.1 was observed only for the mutant and not the WT or the complemented strain (see Fig. S2).
Supplementation of 50 μM Fe(II) did not increase Fe accumulation by these strains under anoxic conditions (Fig. 4A to E; Table S1a to e). In contrast, compared to the WT and their respective mutants, Fe(II) supplementation to the basal YP (yeast-peptone supplemented with 1 mM succinate) medium under oxic conditions significantly increased intracellular Fe concentration (up to ∼2- to ∼7-fold higher) by the complemented strains of the ΔfeoAB, ΔefeU, Δnramp1AB, and ΔsitABC mutants (Fig. 4F, G, H, and J; P < 0.05; Table S1). Similar to the anoxic growth conditions, the addition of EDTA suppressed cell growth (OD660, <0.1) as well as Fe transport by all the strains (Fig. 4F to J). However, Fe(II) supplementation restored Fe transport and rescued their growth except for the complemented strains. Because gentamicin was added to maintain plasmid (pBBRIMCS-5) (62) expressing the individual genes from TIE-1 in the complementation strains, we hypothesize that the lack of growth is likely because of a combined effect of gentamicin and EDTA. A combination of EDTA and gentamicin has been previously reported to inhibit the growth of Pseudomonas aeruginosa (63). The growth inhibition in the presence of EDTA was consistently observed in all the complemented strains under oxic conditions despite the addition of Fe (Fig. S2k). In contrast, the same effect did not hold true under anoxic conditions with FW medium. Even the complemented strains accumulated amounts of Fe very similar to those accumulated by the mutants and WT strains with their subsequent growth (Fig. 4A to E; Fig. S2). The combined toxic effects of EDTA and gentamicin might have been reversed by the presence of other cations in the FW medium including magnesium and calcium. The addition of magnesium, calcium, and iron appears to block cell death and detachment of P. aeruginosa biofilms (63). This could suggest that the addition of other divalent metals increases the binding competition for EDTA and frees more Fe for cell growth. However, future work will be required to determine the specific role of medium composition in this process. In contrast, combination of DiP and gentamicin under oxic conditions did not seem to have any toxic effects on the complemented strains and their subsequent metal accumulation (Fig. 4F to J).
To investigate if the putative Fe(II) transporters also play a role in Mn transport, we quantified the total amounts of Mn accumulated by the different strains of TIE-1. Under anoxic growth conditions with a supply of Mn and EDTA, the complemented strains of the ΔfeoAB and ΔefeU mutants accumulated noticeably more Mn (∼3.6- and ∼1.8-fold, respectively) than the WTs and their mutants (Fig. 5A and B; P < 0.05; Table S1k and l). However, when the strains were cultured in the basal FW medium supplemented with Mn(II), only the ΔefeU complemented strain accumulated a significant amount of Mn compared to those accumulated by the WT and its mutant (Fig. 5B; Table S1l). Similar to the Fe studies, the addition of EDTA and DiP to the basal medium abolished cell growth and Mn accumulation by all the strains under anoxic conditions, with the two exceptions noted above (Fig. 5A to E; Fig. S2).
FIG 5.
Mn acquisition by R. palustris TIE-1 mutants, complemented strains, and WT under Mn-replete, Mn-depleted, oxic, and anoxic conditions. The Mn content of the cells was normalized to the Mn acquisition by WT. (A to E) Mn acquisition under the anoxic conditions. (F to J) Mn acquisition under oxic conditions. Values represent the means ± standard deviations from biological triplicates. *, conditions under which an OD660 of >0.1 was observed only for the mutant and not WT or the complemented strain (see Fig. S2).
Under oxic growth conditions, only the ΔefeU complemented strain accumulated a larger amount of Mn than the WT as well as the mutant (∼3-fold) when Mn(II) was added to the basal YP medium (Fig. 5G; P < 0.005; Table S1q). Mn accumulation by the rest of the TIE-1 strains was similar under oxic conditions (Fig. 5F to J; Table S1p to t). The combined toxic effects of EDTA and gentamicin under oxic conditions were also observed in this case. None of the complemented strains accumulated Mn when the medium was supplemented with Mn(II) and EDTA (Fig. 5F to J; Fig. S2f to j), including the complemented strains of the Δnramp1AB, Δnramp3AB, and ΔsitABC mutants, which showed modest growth (OD660, ∼0.1) (Fig. S2h to j). The amount of Mn accumulated by these three strains was below our detection limit. Under Mn-depleted conditions using EDTA, we observed neither growth (OD660, <0.1) nor Mn accumulation by these strains (Fig. 5F to J; Fig. S2). Overall, the Mn accumulation results show that the Fe transporter efeU also participates in Mn transport in TIE-1 (Fig. 5G).
Gene expression of ferrous iron transporters varies in response to iron and manganese availability and oxygen tension.
Because Fe transporter genes are regulated primarily by the availability of Fe and oxygen in the environment (64, 65), we analyzed the gene expression profiles of these transport systems in wild-type TIE-1 in response to Fe, Mn, and oxygen availability. We used reverse transcription-quantitative PCR (RT-qPCR) with recA and clpX as reference genes as performed previously (28). Data reported here are with respect to recA for consistency with previous studies (28, 35, 36, 64, 65). The trends obtained were similar to those with clpX as a reference gene. Under conditions where no growth was observed (OD660, <0.1), we collected large volumes of cells to extract sufficient RNA for RT-qPCR.
Fe depletion by the addition of EDTA elevated the expression of feoB (up to 20-fold), efeU (2.5-fold), nramp3B (5-fold), and sitA (5.6-fold) under anoxic conditions (Fig. 6A to E; Table S2a to e). This overexpression was reversed when the medium was supplemented with 50 μM Fe(II). Similarly, Fe depletion by DiP increased the expression of feoB ∼8-fold. However, this upregulation was not reversed by Fe(II) supplementation (Fig. 6A; P < 0.05; Table S2a). Among these genes, nramp1B appears to be less responsive to Fe bioavailability, as the addition of chelators or Fe did not show a significant effect on its expression (Fig. 6C; Table S2c).
FIG 6.
Determination of relative mRNA abundance of Fe-transporting genes in TIE-1 using RT-qPCR under Fe-replete, Fe-depleted, oxic, and anoxic conditions. (A to E) Relative gene expression under anoxic conditions. (F to J) Relative gene expression under oxic conditions. Values represent the means ± standard deviations from biological triplicates.
Under oxic growth conditions, the addition of both Fe(II) and EDTA increased the expression of the feoB (∼8-fold), efeU (∼3-fold), and sitA (∼3-fold) genes (Fig. 6F, G, and J; P < 0.05; Table S2f, g, and j). Overall, relative gene expression obtained in the presence of EDTA was higher than the expression observed in the presence of DiP (Fig. 6F to J). nramp3B was minimally expressed (Fig. 6I).
We also tested the relative gene expressions under different degrees of Mn availability. Under anoxic Mn-depleted conditions (with EDTA), all five genes, namely, feoB, efeU, nramp1B, nramp3B, and sitA, were upregulated (up to ∼2.7-fold) (Fig. 7A to E; Table S2k to o). However, the expression was downregulated when excess Mn(II) was added. This pattern remained consistent even when the chelator was changed from EDTA to DiP, except for the feoB gene (Fig. 7A). The supply of Mn(II) upregulated feoB, similar to the trend observed with Fe(II). Unlike the highly variable gene expression observed under anoxic conditions, gene expression under oxic conditions did not vary significantly from that under the control conditions (Fig. 7F to J; Table S2p to t). We observed that expression of the previously known Fe-specific transporter systems, such as Feo and EfeU, can be regulated by Mn bioavailability in TIE-1.
FIG 7.
Determination of relative abundances of Fe-transporting genes in TIE-1 using RT-qPCR under Mn-replete, Mn-depleted, oxic, and anoxic conditions. (A to E) Relative gene expression under anoxic conditions. (F to J) Relative gene expression under oxic conditions. Values represent the means ± standard deviations from biological triplicates.
Promoter predictions.
Because Fe transporter genes are regulated primarily by the availability of Fe and oxygen in the environment, next we analyzed the promoter regions of these Fe transporters to identify the binding sites for Fe and oxygen-responsive regulators. We found a putative Fur-like binding site (Table S3). Fur is known to be a transcriptional regulator of Fe transporter genes in E. coli and many other bacteria (66, 67). We also identified a putative binding site for Fnr family proteins in the feoAB promoter along with a Fur/Irr binding site (Fig. S3) (68). Fnr is a transcriptional activator under anoxic conditions (69) that turns on the transcription of the feo operon in the absence of oxygen (22). The efeU promoter has a putative Fnr box (Fig. S4) but only a weak Fur box (68). Similar binding sites have been identified in the Nramp1AB promoter sequence (Fig. S5). We found a weak Fur box and an Fnr box in the nramp3B upstream region that encompasses the small open reading frame (ORF) nramp3A. We were unable to detect nramp3A mRNA under any condition tested, which suggests that this ORF is likely not transcribed. The sitABC promoter also contains an Fnr box along with a Fur box (Fig. S7) (68).
DISCUSSION
This study provided insight into the role of five putative Fe(II) transporter genes (Fig. 1) to transport Fe and Mn in TIE-1 under differing degrees of Fe, Mn, and oxygen availability. The important role of these transporters in Fe uptake and cellular growth was determined first by heterologous complementation of E. coli H1771 (lacking the Feo system and siderophore biosynthesis genes) and E. coli GR536 (lacking all Fe transporter systems), respectively (Fig. 2D and Fig. 3). Total Fe and Mn quantification in the wild-type, single-gene/operon deletion mutants, and complemented strains of R. palustris TIE-1 showed that these transporter genes are important for Fe and Mn transport in TIE-1. Under anoxic conditions, all TIE-1 mutant strains accumulated similar amounts of Fe, suggesting that the deletion of no single transporter gene affects iron homeostasis in TIE-1. However, some TIE-1 strains under oxic conditions, particularly the complemented strains of the feoAB, efeU, nramp1AB, and sitABC mutants, accumulated a larger amount of Fe than did the WT and mutants (Fig. 4F to J). Under oxic conditions, Fe likely exists as Fe(III). Because overexpressing Fe(II) transporters increases total Fe content under oxic conditions, it is possible that assimilatory ferric reductases may allow reduction of Fe(III) to Fe(II). Fe(II) in the periplasm is subsequently transported by these Fe(II) transporters (present in the inner membrane). This would lead to an increase in intracellular Fe concentration when these transporters are overexpressed under a strong constitutive promoter under oxic conditions. Ferric reductases are known to be involved in Fe acquisition under oxic conditions in several microbes (70). We also found that expressing the putative Fe(II) transporters, including the previously described Fe-specific transporters such as feoAB and efeU, can increase intracellular Mn in TIE-1 under both anoxic and oxic conditions (Fig. 5). Under oxic conditions, Mn likely exists as Mn(IV). Similar to Fe(III) uptake, Mn reductases likely mediate Mn(IV) reduction in the periplasm to Mn(II) (71), which can be then transported via Fe transporters.
Our metal accumulation data are also supported by the relative gene expression of these transporters under anoxic and oxic conditions with respect to metal availability. Production of metal transporters is often induced as the metal concentrations are lowered (72, 73). Because the presence of metal chelators reduces metal availability, we observed the upregulation of putative Fe transporters under anoxic metal-depleted conditions (Fig. 6A to E; Fig. 7A to E). A similar observation has been made previously for Salmonella enterica, in which the FeoB protein was overexpressed when levels of both oxygen and Fe were low (74). However, a supply of Fe(II) significantly downregulated the expression. This trend appears more obvious in the case of feoB with iron. Upstream regulatory elements such as ferric iron regulator (fur) have been widely found to regulate the expression of feo in the presence or absence of iron (22, 75). When iron is limited by chelators, Fur releases repression, upregulating the expression of iron transport genes (22, 75). Fur protein has been also indicated to directly or indirectly mediate manganese-dependent regulation of gene expression (76). Likewise, fumarate and nitrate reductase transcriptional regulator (Fnr), which is a transcriptional activator of anaerobic respiratory genes (69), is known to activate transcription of the Feo system under anoxic conditions (48) that can increase the expression level of Feo up to 3-fold (22). Indeed, the genome of TIE-1 appears to have at least 11 identifiable Fnr family proteins (Table S3) that are involved in oxygen sensing (50).
Curiously, we observed opposite gene expression trends under oxic conditions. The expression of feoB and efeU in the basal YP medium was lower with EDTA than the expression obtained under the control conditions (Fig. 6 and 7). We also observed growth inhibition of WT strains with EDTA (Fig. S2f to j). EDTA has been reported to kill both planktonic cells and biofilms of P. aeruginosa (63). We speculate that EDTA may have prevented TIE-1’s growth (Fig. S2f to j) and subsequent gene expression of feoB and efeU. This could be also true in the case of growth with Mn (Fig. 7F to J). However, the addition of Fe or Mn may reduce the negative effect of EDTA via its interaction with added metals. This is also reflected by their increased growth when Fe or Mn was added to the YP medium (Fig. S2f to j). Therefore, growth and metal limitation in the presence of Fe and EDTA may have contributed to the increased relative gene expression of feoB and efeU under oxic conditions. However, under anoxic conditions, the presence of other divalent cations, such as Ca and Mg in FW medium (stability constants of 10.6 and 8.7, respectively) (77), may increase the binding competition for EDTA, freeing more Fe for cells. Future work, however, will be required to confirm this hypothesis.
Overall, our results show that TIE-1 tightly regulates and maintains Fe and Mn homeostasis. The deletion of any single gene or operon does not affect the metal uptake capacity and viability of TIE-1. This suggests that the existence of compensatory systems for metal uptake in TIE-1 is crucial for its metabolic adaptability under different levels of Fe/Mn and oxygen.
R. palustris TIE-1 has homologs for both Fur and two Irr proteins that mediate iron-dependent regulation of gene expression (Table S3) (68). The genome of TIE-1 appears to have at least 11 identifiable Fnr family proteins (Table S3) that are involved in oxygen sensing (78). One of these homologs is the FixK protein, which has a Fe-S cluster, and its oxygen sensing response is linked to the two-component regulation system FixLJ (64).
We have recently shown that TIE-1 can produce bioplastics and biofuels such as n-butanol under various growth conditions (35; Bai et al., submitted). Other strains of Rhodopseudomonas have also been used to produce value-added compounds (29–34). Production of such biomolecules is controlled by intracellular electron availability, which, in turn, is modulated by the action of various Fe-containing proteins. Mn is part of many enzymes in central metabolism. By controlling Fe and Mn intake via synthetic biology, we can modulate bioproduction by R. palustris TIE-1. This will be investigated in future studies in which overexpression of the two Fe transporters feoAB and efeU (involved in Fe and Mn transport that we have identified here) will be performed with bioplastic and biofuel production strains to see if product titers can be increased.
MATERIALS AND METHODS
Bacterial strains and growth conditions.
E. coli strains were obtained from the sources indicated in Table 2. They were grown in lysogeny broth (LB) at pH 7.0 at 37°C with shaking at 225 rpm. Rhodopseudomonas palustris TIE-1 was obtained from Dianne K. Newman, Division of Biology and Biological Engineering and the Division of Geological and Planetary Sciences, California Institute of Technology. Prior to photoferrotrophy [Fe(II) as an electron donor], TIE-1 cells were grown chemoheterotrophically in medium with 0.3% yeast extract and 0.3% peptone (YP), with 1 mM sodium succinate and 10 mM MOPS [3-N-(morpholino)propanesulfonic acid] at pH 7.0 in the dark at 30°C with shaking at 250 rpm (64). Time course cell growth was monitored using a Spectronic 200 spectrophotometer (Thermo Fisher Scientific, USA). To adapt the cells to photoautotrophic growth using H2 as the sole electron donor, chemoheterotrophically grown TIE-1 cells were transferred into anoxic (purged with 34.5 kPa N2-CO2 [80%-20%]) bicarbonate-buffered freshwater (FW) (79) medium with ammonium chloride (NH4Cl; 5.61 mM) as a nitrogen source and H2 as an electron donor. The cells were incubated at 30°C under a 60-W incandescent light source placed at a distance of 12.5 cm. For photoautotrophic growth with Fe(II) as an electron donor, photoautotrophically grown TIE-1 cells were inoculated into anoxic FW medium prepared under a flow of 34.5 kPa N2-CO2 (80%-20%) and dispensed into presterilized serum bottles/Balch tubes purged with 34.5 kPa N2-CO2 (80%-20%). The containers were then sealed using sterile butyl rubber stoppers with aluminum crimps and stored at room temperature for at least a day before supplementation with anoxic sterile stocks of FeCl2 to a final concentration of 5 mM. For anoxic growth, all sample manipulations were performed inside an anaerobic chamber (Coy; MI). For growth on solid medium, LB or YP medium was solidified with 1.5% agar and supplemented with antibiotics as described previously (64).
TABLE 2.
Strains used and constructed in this study
| Strain | Descriptiona | Reference or source |
|---|---|---|
| E. coli strains | ||
| H1771 | MC4100 aroB feoB7 fhuF::Δplac Mu | 48 |
| GR536 | ΔfecABCDE::kan ΔzupT::cat ΔmntH ΔfeoABC ΔentC | 52 |
| GG48 | zntA::kan ΔzitB::cam | 56 |
| ΔcopA ΔcueO ΔcusCFBA::cat mutant | ΔcopA ΔcueO ΔcusCFBA::cat | Kindly provided by Gregor Grass |
| S17-1 | Tpr Smr recA thi pro hsdRM+ RP4-2 Tc::Mu Km::Tn7 | 85 |
| AB445 | pWKS30 in E. coli H1771 | This study |
| AB450 | pAB446 in E. coli H1771 | This study |
| AB451 | pAB447 in E. coli H1771 | This study |
| AB452 | pAB448 in E. coli H1771 | This study |
| AB453 | pAB449 in E. coli H1771 | This study |
| AB455 | pAB454 in E. coli H1771 | This study |
| AB457 | pAB456 in E. coli H1771 | This study |
| AB463 | pAB462 in E. coli H1771 | This study |
| AB464 | pAB446 in E. coli GR536 | This study |
| AB465 | pAB447 in E. coli GR536 | This study |
| AB466 | pAB448 in E. coli GR536 | This study |
| AB467 | pAB449 in E. coli GR536 | This study |
| AB468 | pAB454 in E. coli GR536 | This study |
| AB469 | pAB456 in E. coli GR536 | This study |
| AB470 | pAB462 in E. coli GR536 | This study |
| AB471 | pWKS30 in E. coli GR536 | This study |
| AB472 | pAB434 in E. coli GR536 | This study |
| AB486 | pWKS30 in E. coli GG48 | This study |
| AB487 | pAB434 in E. coli GG48 | This study |
| AB488 | pAB446 in E. coli GG48 | This study |
| AB489 | pAB447 in E. coli GG48 | This study |
| AB490 | pAB448 in E. coli GG48 | This study |
| AB491 | pAB449 in E. coli GG48 | This study |
| AB492 | pAB454 in E. coli GG48 | This study |
| AB493 | pAB456 in E. coli GG48 | This study |
| AB494 | pAB462 in E. coli GG48 | This study |
| AB588 | pAB413 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB589 | pAB434 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB590 | pAB446 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB591 | pAB447 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB592 | pAB448 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB593 | pAB449 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB594 | pAB454 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB595 | pAB456 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| AB596 | pAB462 in E. coli ΔcopA ΔcueO ΔcusCFBA::cat | This study |
| R. palustris TIE-1 strains | ||
| DKN379 | WT | 26 |
| AB41 | ΔfeoAB | This study |
| AB63 | Complemented ΔfeoAB strain | This study |
| AB42 | ΔefeU | This study |
| AB64 | Complemented ΔefeU strain | This study |
| AB68 | Δnramp1B | This study |
| AB43 | Δnramp1AB | This study |
| AB65 | Complemented Δnramp1AB strain | This study |
| AB77 | Δnramp3A | This study |
| AB70 | Δnramp3B | This study |
| AB44 | Δnramp3AB | This study |
| AB66 | Complemented Δnramp3AB strain | This study |
| AB72 | ΔsitB | This study |
| AB74 | ΔsitC | This study |
| AB45 | ΔsitABC | This study |
| AB67 | Complemented ΔsitABC strain | This study |
Tpr, trimethoprim resistance; Smr, streptomycin resistance.
DNA isolation and plasmid and strain construction.
Genomic DNA of TIE-1 was isolated using the DNeasy blood and tissue kit (Qiagen, Valencia, CA) and used as a template for PCRs. All nucleic acids isolated in this study were quantified using a NanoDrop 1000 spectrophotometer (Thermo Scientific, Waltham, MA). A QIAprep spin miniprep kit (Qiagen, Valencia, CA) was used for plasmid DNA isolation from E. coli. All primers used in this study were obtained from Integrated DNA Technologies, Coralville, IA, and their sequences are available upon request. The identity of all DNA constructs was confirmed via DNA sequencing at Genewiz Inc., South Plainfield, NJ. E. coli strains were transformed by electroporation using an E. coli Gene Pulser (Bio-Rad, Hercules, CA), as recommended by the supplier. Plasmids were mobilized from E. coli S17-1/λ pir into TIE-1 by conjugation on YP agar. All plasmids constructed are indicated in Table S4. Mutant construction was performed as described previously for TIE-1 (28, 36, 64, 65). Briefly, 1-kb DNA fragments upstream and downstream of the gene of interest were PCR amplified using TIE-1 genomic DNA as the template and cloned into pJQ200KS, a suicide vector. The constructs were mobilized into TIE-1 via conjugation with E. coli S17-1. Homologous recombination was allowed to occur on selective YP medium containing 400 μg/ml of gentamicin. Vector loss was selected using media containing 10% sucrose. Mutants lacking the target genes were screened using PCR. The mutants created are listed in Table 2. The primers used for verification are provided in Table 3. All the mutants and plasmids are maintained by the lab as frozen stocks and will be distributed upon request.
TABLE 3.
Primers used to construct and check mutants constructed in this study
| Primer | Sequence |
|---|---|
| Mutant construction | |
| ΔfeoBupforApaI | ACTAGTGGGCCCCGACTCCGCGTCATGCCCGGCCTCGTG |
| ΔfeoBuprevSmaI | ACTAGTCCCGGGCGCGCAATCGCCAAATCAAGAAGCTGCAATCTG |
| ΔfeoAdnforEcoRV | ACTAGTGATATCTGACGCGCAGATTGCAGCTTCTTGATTTG |
| ΔfeoAdnrevSpeI | GGATCCACTAGTGAACGCGGCGCGCGCCATGTAGC |
| ΔefeUupforXhoI | ACTAGTCTCGAGCGCGGCTTCGACCATCAAGCAC |
| ΔefeUuprevBamHI | ACTAGTGGATCCCTGCGCCAACTTCGCCTCGCCCAAC |
| ΔefeUdnforBamHI | ACTAGTGGATCCTGAGCCGAACCTGCAGCG |
| ΔefeUdnrevNotI | ACTAGTGCGGCCGCCACGCGTTCCACGGAATCAAGC |
| Δnramp1upforPstI | ACTAGTCTGCAGGAATGACGACGAGAAGAATC |
| Δnramp1uprevBamHI | ACTAGTGGATCCCGAAAGCGTCTCCTGATGCCTAG |
| Δnramp1dnforBamHI | ACTAGTGGATCCTAGCCTCGCGCCAGTCATTCCG |
| Δnramp1dnrevNotI | ACTAGTGCGGCCGCCTGTTCACGCTGCGCGAACT |
| Δnramp3upforPstI | ACTAGTCTGCAGGCCTATTACGGCGACAGCTAC |
| Δnramp3uprevBamHI | ACTAGTGGATCCACGGTGAGATCAGGCGGCTAGC |
| Δnramp3dnforBamHI | ACTAGTGGATCCTGATGCATCCGGCGGTTGCTG |
| Δnramp3dnrevSpeI | GGCGCGCCACTAGTTGAACTTGGTGACGCGGTC |
| ΔsitABCupforSalI | ACTAGTGTCGACTGACCGACGCCAGACCACGCTG |
| ΔsitABCuprevBamHI | ACTAGTGGATCCGGTCACCTCATTGCCACCAACAC |
| ΔsitABCdnforBamHI | ACTAGTGGATCCTGACGCAGCGCCGGTCCCGCTG |
| ΔsitABCdnrevNotI | ACTAGTGCGGCCGCGTCTGCACCAATTGCTGCAGC |
| Mutant check | |
| ΔfeoAupckfor | TTTTGTGCCAAATCAAACCA |
| ΔfeoAdnckrev | TGAACAGGGAGGTCTTACCG |
| ΔfeoBupckfor | GAAGTGCTGCACGAGGGTAT |
| ΔfeoBdnckrev | AACTCATCACGTTGGTCGTG |
| Δnramp1upckfor | GACCTGCTCGGTGTGATCC |
| Δnramp1dnckrev | GGACTCTCGCCCAACTAACTT |
| Δnramp3upckfor | CGAAATCAGCATCAGACGTG |
| Δnramp3dnckrev | ATCTGCGATCTCGACGATGT |
| ΔsitAupckfor | CCTCCCTCTCAATCCCATTT |
| ΔsitAdnckrev | CATGAATTCGAACTCGGTGA |
| ΔsitBupckfor | CCGACAACCAGGTCGAAG |
| ΔsitBdnckrev | GGACGGCGTATAGACGTGAA |
| ΔsitCupckfor | CCAGCCATCATCCTGGTC |
| ΔsitCdnckrev | GGTCATCAGGCAGTTACTCCA |
E. coli β-galactosidase assays.
E. coli H1771 derivatives were grown in LB medium at pH 7.0 at 37°C with shaking at 225 rpm. Four different growth conditions were tested for each strain: (i) Fe(III) replete [50 μM Fe(III)-citrate], (ii) Fe(III) depleted [50 μM Fe(III)-citrate with 100 μM DiP], (iii) Fe(II)-replete [50 μM ascorbate-reduced Fe(III)-citrate], and (iv) Fe(II)-depleted [50 μM ascorbate-reduced Fe(III)-citrate with 100 μM DiP]. Ascorbate-reduced Fe(III)-citrate was prepared as previously described (32). The E. coli strains were grown with 100 μg/ml of ampicillin to maintain the pWKS30 plasmid derivatives. Overnight cultures of these strains were inoculated into the respective media with a dilution factor of 1:100. The cultures were grown at 37°C with shaking at 225 rpm for 5 h. These cells were then assayed for β-galactosidase activity as previously described using the Miller assay (80). β-Galactosidase activity, expressed in Miller units, was calculated using the following formula: Miller units = (OD420 × 1,000)/(OD600 × V × t), where V is volume of culture processed for each sample and t is time elapsed from start to end of the reaction.
E. coli growth curves.
E. coli GR536 derivatives were maintained in LB medium with pH 7.0 with 25 μg/ml of chloramphenicol and 50 μg/ml of kanamycin. The strains carrying pWKS30 derivatives had 100 μg/ml of ampicillin in addition to chloramphenicol and kanamycin. Overnight cultures of these strains were grown and inoculated into Tris-mineral salts medium with 3 g/liter of Casamino Acids and 0.2% sodium gluconate (50 mM Tris-Cl [pH 7.0], 80 mM NaCl, 20 mM KCl, 20 mM NH4Cl, 1 mM MgCl2·6H2O, 0.2 mM CaCl2·2H2O, 5 μM iron ammonium citrate, 3 mM Na2SO4·10H2O, 50 μM Na2HPO4·12H2O) with 0.1× SL6 trace elements solution. Increasing concentrations of 2,2′-dipyridyl (DiP) were added to the medium, with the highest concentration at 150 μM. Similar to E. coli GR536 derivatives, E. coli GG48 derivatives were also maintained in LB medium with pH 7.0 with 25 μg/ml of chloramphenicol and 50 μg/ml of kanamycin. The zinc, cadmium, and copper toxicity tests were performed in LB medium at pH 7.0 with increasing concentrations of added ZnCl2 from 0 to 400 μM, CdCl2 from 0 to 100 μM, and CuCl2 from 0 to 400 μM, respectively. The cultures were grown at 37°C with shaking at 225 rpm. Samples were withdrawn periodically for OD600 measurements. E. coli ΔcopA ΔcueO ΔcusCFBA::cat derivatives were maintained in pH 7.0 LB medium with 25 μg/ml of chloramphenicol. The strains carrying pWKS30 derivatives had 100 μg/ml of ampicillin in addition to chloramphenicol.
Iron and manganese uptake assays.
Iron and manganese uptake assays were performed as previously described (48), with some modifications. For anoxic growth conditions, TIE-1 strains were grown in FW medium at pH 7.0 with 1 mM sodium succinate at 30°C under a 60-W incandescent light source placed at a distance of 12.5 cm from the cultures. Time course OD660 was measured by withdrawing the samples under anoxic conditions. Late-exponential-phase cultures were then aliquoted into presterilized anoxic Balch tubes, followed by headspace flushing with 34.5 kPa N2-CO2 (80%-20%). The tubes were placed on ice until use. For oxic growth conditions, TIE-1 was grown in YP medium with 3 g/liter of yeast extract and 3 g/liter of peptone supplemented with 1 mM succinate, with shaking at 250 rpm for 120 h.
To test iron and manganese accumulation by single-gene mutants and complemented and WT strains and their responses to metal-replete and -depleted conditions with respect to oxygen availability, the following experiments were included: (i) normal level of Fe(II) or Mn(II) (basal media only), (ii) basal media with 100 μM DiP or EDTA, (iii) basal media with 50 μM Fe(II) or Mn(II), and (iv) basal media with 100 μM DiP or EDTA and 50 μM Fe(II) or Mn(II), under oxic and anoxic conditions. Fe(II), Mn(II), EDTA, and DiP were added from a 50 mM stock solution at the beginning of the growth.
Iron and manganese analysis by ICP-MS analysis.
A 1-ml sample was taken from the cultures incubated with iron or manganese and centrifuged at 21,000 × g for 5 min. Samples were washed with 1 ml of Tris-EDTA (TE) buffer and 1 ml of ultrapure water. Washed pellets were then added with 50 μl of high-purity HNO3 trace element (Fisher) and digested with a CEM MARS 6 microwave at 180°C for 20 min. Digested samples were then diluted 2-fold with ultrapure water and filtered with a 0.22-μm polyethersulfone (PES) filter. Filtered samples were analyzed using a Perkin Elmer Elan DRC II ICP-MS. Iron was analyzed as a 55.845 isotope and manganese as a 54.94 isotope. Yttrium was used as an internal standard. Standard curves were built from ICP-MS-grade iron and manganese (Inorganic Venture, VA) using the following concentrations: 0, 1, 10, 50, 100, and 200 ppb. Standards were also used as abiotic controls. Obtained Fe and Mn concentrations were normalized to the OD of the sample and further normalized to the concentration obtained from the WT TIE-1.
Gene expression analysis.
Gene expression analysis was performed using RT-qPCR. We quantified the mRNA abundances of the putative Fe(II) transporter genes in TIE-1 under the following conditions: (i) basal medium only (Fe, ∼4 nM; Mn, ∼0.25 nM), (ii) basal medium with 100 μM DiP or EDTA, (iii) basal medium with 50 μM Fe(II) or Mn(II), and (iv) basal medium with 100 μM DiP or EDTA and 50 μM Fe(II) or Mn(II), under oxic and anoxic conditions. The data were normalized to the gene expression obtained from the basal medium only. The comparative threshold cycle (CT) method was used as described previously (64) to assess the expression of the relevant genes. Primer efficiencies were determined using the manufacturer’s protocol (Applied Biosystems Inc.; user bulletin number 2). clpX and recA were used as the two internal standards; they have been previously used and validated as internal standards (64). The primers used for the assays are indicated in Table 4. The iScript cDNA synthesis kit (Bio-Rad, Hercules, CA) was used for reverse transcription. iTaq FAST SYBR green Supermix with ROX (Bio-Rad) and the Stratagene Mx3005P qPCR system (Agilent, Santa Clara, CA) were used for all quantitative assays.
TABLE 4.
RT-qPCR primers used in this study
| Primer name | Sequence | Reference or source |
|---|---|---|
| recAfor | ATCGGCCAGATCAAGGAAC | 64 |
| recArev | GAATTCGACCTGCTTGAACG | 64 |
| clpXfor | GGAGATCTGCAAGGTTCTCG | 64 |
| clpXrev | CCGCTTGTAGTGATTGTGGA | 64 |
| feoAfor | CCCATCACAACGGCCATAG | This study |
| feoArev | ACCCCAGCTCGATCAGTC | This study |
| feoBfor | TCGATTCTCAGCCGTTCAAC | This study |
| feoBrev | GTAGTTCGCCACCTTCTGAC | This study |
| efeUfor | TGACCAGCCGAGAAATCTATG | This study |
| efeUrev | TGATGGTTTCCTGTCGCAG | This study |
| nramp1Afor | CTTTGCAGATCGTGCTGTTC | This study |
| nramp1Arev | AATCGGAGACACCGACTTTG | This study |
| nramp1Bfor | CGCCCTATCTGTTCTTCTGG | This study |
| nramp1Brev | GGTGTCTTGATCAGCGGTTT | This study |
| nramp2for | CGATCACTGCCACCGATCT | This study |
| nramp2rev | GCGGAATCCCGAACAACA | This study |
| nramp3Afor | AACTTCAAAACCGCTTGGTG | This study |
| nramp3Arev | GTTGTCGTTGGCGTGGAC | This study |
| nramp3Bfor | ATTCGGCACATACACCCAG | This study |
| nramp3Brev | CCATCTCCTGATTGACGTACAG | This study |
| sitAfor | TGGCACGCTGTATTCCG | This study |
| sitArev | TGCCGGACCATATCAATGTAAG | This study |
| sitBfor | AAGGGCACCAACATCGATC | This study |
| sitBrev | TCGACGCATTCAATCACCAG | This study |
| sitCfor | ACCTTTAACGATGTCACCCTC | This study |
| sitCrev | TTCAGGATACCAACGATGCC | This study |
Bioinformatics tools.
For identifying iron transporters in TIE-1, delta-blast (81), FASTA (82; http://www.ebi.ac.uk/Tools/sss/fasta/), and the IMG ortholog neighborhood search (83; http://img.jgi.doe.gov/cgi-bin/w/main.cgi) were used. Transmembrane predictions were made using the TMHMM server v. 2.0 at http://www.cbs.dtu.dk/services/TMHMM/. Promoter predictions were made using Virtual Footprint v. 3.0 at http://www.prodoric.de/vfp/ (84).
Statistical analysis.
All statistical analyses (two-tailed Student’s t test) were performed with Python. A P value of <0.05 was considered significant. All the experiments were carried out using biological triplicates.
ACKNOWLEDGMENTS
We thank the Nano Research and Environmental Laboratory (NREF) at Washington University in St. Louis for their support to measure iron and manganese using ICP-MS.
This work was supported by the following grants to A.B.: The David and Lucile Packard Foundation Fellowship (201563111), the U.S. Department of Energy (grant number DESC0014613), and the U.S. Department of Defense, Army Research Office (grant number W911NF-18-1-0037). A.B. was also funded by a Collaboration Initiation Grant, an Office of the Vice-Chancellor of Research Grant, and an International Center for Energy, Environment and Sustainability Grant from Washington University in St. Louis.
Footnotes
Supplemental material is available online only.
REFERENCES
- 1.Porcheron G, Garénaux A, Proulx J, Sabri M, Dozois CM. 2013. Iron, copper, zinc, and manganese transport and regulation in pathogenic enterobacteria: correlations between strains, site of infection and the relative importance of the different metal transport systems for virulence. Front Cell Infect Microbiol 3:90. doi: 10.3389/fcimb.2013.00090. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Hood MI, Skaar EP. 2012. Nutritional immunity: transition metals at the pathogen–host interface. Nat Rev Microbiol 10:525–537. doi: 10.1038/nrmicro2836. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Hassan HM, Schrum LW. 1994. Roles of manganese and iron in the regulation of the biosynthesis of manganese-superoxide dismutase in Escherichia coli. FEMS Microbiol Rev 14:315–323. doi: 10.1111/j.1574-6976.1994.tb00105.x. [DOI] [PubMed] [Google Scholar]
- 4.Andrews SC, Robinson AK, Rodríguez-Quiñones F. 2003. Bacterial iron homeostasis. FEMS Microbiol Rev 27:215–237. doi: 10.1016/S0168-6445(03)00055-X. [DOI] [PubMed] [Google Scholar]
- 5.Hohle TH, O’Brian MR. 2012. Manganese is required for oxidative metabolism in unstressed Bradyrhizobium japonicum cells. Mol Microbiol 84:766–777. doi: 10.1111/j.1365-2958.2012.08057.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Sobota JM, Imlay JA. 2011. Iron enzyme ribulose-5-phosphate 3-epimerase in Escherichia coli is rapidly damaged by hydrogen peroxide but can be protected by manganese. Proc Natl Acad Sci U S A 108:5402–5407. doi: 10.1073/pnas.1100410108. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Anjem A, Imlay JA. 2012. Mononuclear iron enzymes are primary targets of hydrogen peroxide stress. J Biol Chem 287:15544–15556. doi: 10.1074/jbc.M111.330365. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Kalantari N, Ghafari S. 2008. Evaluation of toxicity of heavy metals for Escherichia coli growth. Iran J Environ Health Sci Eng 15:173–178. [Google Scholar]
- 9.Kaur G, Sengupta S, Kumar V, Kumari A, Ghosh A, Parrack P, Dutta D. 2014. Novel MntR-independent mechanism of manganese homeostasis in Escherichia coli by the ribosome-associated protein HflX. J Bacteriol 196:2587–2597. doi: 10.1128/JB.01717-14. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Cornelis P, Wei Q, Andrews SC, Vinckx T. 2011. Iron homeostasis and management of oxidative stress response in bacteria. Metallomics 3:540–549. doi: 10.1039/c1mt00022e. [DOI] [PubMed] [Google Scholar]
- 11.Porcheron G, Dozois CM. 2015. Interplay between iron homeostasis and virulence: Fur and RyhB as major regulators of bacterial pathogenicity. Vet Microbiol 179:2–14. doi: 10.1016/j.vetmic.2015.03.024. [DOI] [PubMed] [Google Scholar]
- 12.Peracino B, Buracco S, Bozzaro S. 2013. The Nramp (Slc11) proteins regulate development, resistance to pathogenic bacteria and iron homeostasis in Dictyostelium discoideum. J Cell Sci 126:301–311. doi: 10.1242/jcs.116210. [DOI] [PubMed] [Google Scholar]
- 13.Hanikenne M, Krämer U, Demoulin V, Baurain D. 2005. A comparative inventory of metal transporters in the green alga Chlamydomonas reinhardtii and the red alga Cyanidioschizon merolae. Plant Physiol 137:428–446. doi: 10.1104/pp.104.054189. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Bolchi A, Ruotolo R, Marchini G, Vurro E, di Toppi LS, Kohler A, Tisserant E, Martin F, Ottonello S. 2011. Genome-wide inventory of metal homeostasis-related gene products including a functional phytochelatin synthase in the hypogeous mycorrhizal fungus Tuber melanosporum. Fungal Genet Biol 48:573–584. doi: 10.1016/j.fgb.2010.11.003. [DOI] [PubMed] [Google Scholar]
- 15.Coombs J, Barkay T. 2005. New findings on evolution of metal homeostasis genes: evidence from comparative genome analysis of bacteria and archaea. Appl Environ Microbiol 71:7083–7091. doi: 10.1128/AEM.71.11.7083-7091.2005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Bartolucci S, Contursi P, Fiorentino G, Limauro D, Pedone E. 2013. Responding to toxic compounds: a genomic and functional overview of Archaea. Front Biosci (Landmark Ed) 18:165–189. doi: 10.2741/4094. [DOI] [PubMed] [Google Scholar]
- 17.Srivastava P, Kowshik M. 2013. Mechanisms of metal resistance and homeostasis in haloarchaea. Archaea 2013:732864. doi: 10.1155/2013/732864. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Baars O, Morel FM, Zhang X. 2018. The purple non‐sulfur bacterium Rhodopseudomonas palustris produces novel petrobactin‐related siderophores under aerobic and anaerobic conditions. Environ Microbiol 20:1667–1676. doi: 10.1111/1462-2920.14078. [DOI] [PubMed] [Google Scholar]
- 19.Stintzi A, Barnes C, Xu J, Raymond KN. 2000. Microbial iron transport via a siderophore shuttle: a membrane ion transport paradigm. Proc Natl Acad Sci U S A 97:10691–10696. doi: 10.1073/pnas.200318797. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Carpenter C, Payne SM. 2014. Regulation of iron transport systems in Enterobacteriaceae in response to oxygen and iron availability. J Inorg Biochem 133:110–117. doi: 10.1016/j.jinorgbio.2014.01.007. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Ge R, Sun X. 2012. Iron trafficking system in Helicobacter pylori. Biometals 25:247–258. doi: 10.1007/s10534-011-9512-8. [DOI] [PubMed] [Google Scholar]
- 22.Lau CK, Krewulak KD, Vogel HJ. 2016. Bacterial ferrous iron transport: the Feo system. FEMS Microbiol Rev 40:273–298. doi: 10.1093/femsre/fuv049. [DOI] [PubMed] [Google Scholar]
- 23.Hantke K. 2003. Is the bacterial ferrous iron transporter FeoB a living fossil? Trends Microbiol 11:192–195. doi: 10.1016/s0966-842x(03)00100-8. [DOI] [PubMed] [Google Scholar]
- 24.Kehres DG, Zaharik ML, Finlay BB, Maguire ME. 2000. The NRAMP proteins of Salmonella typhimurium and Escherichia coli are selective manganese transporters involved in the response to reactive oxygen. Mol Microbiol 36:1085–1100. doi: 10.1046/j.1365-2958.2000.01922.x. [DOI] [PubMed] [Google Scholar]
- 25.Boyer E, Bergevin I, Malo D, Gros P, Cellier M. 2002. Acquisition of Mn (II) in addition to Fe (II) is required for full virulence of Salmonella enterica serovar Typhimurium. Infect Immun 70:6032–6042. doi: 10.1128/iai.70.11.6032-6042.2002. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Jiao Y, Kappler A, Croal LR, Newman DK. 2005. Isolation and characterization of a genetically tractable photoautotrophic Fe(II)-oxidizing bacterium, Rhodopseudomonas palustris strain TIE-1. Appl Environ Microbiol 71:4487–4496. doi: 10.1128/AEM.71.8.4487-4496.2005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.Jiao Y, Newman DK. 2007. The pio operon is essential for phototrophic Fe(II) oxidation in Rhodopseudomonas palustris TIE-1. J Bacteriol 189:1765–1773. doi: 10.1128/JB.00776-06. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Bose A, Gardel EJ, Vidoudez C, Parra E, Girguis PR. 2014. Electron uptake by iron-oxidizing phototrophic bacteria. Nat Commun 5:3391. doi: 10.1038/ncomms4391. [DOI] [PubMed] [Google Scholar]
- 29.Huang JJ, Heiniger EK, McKinlay JB, Harwood CS. 2010. Production of hydrogen gas from light and the inorganic electron donor thiosulfate by Rhodopseudomonas palustris. Appl Environ Microbiol 76:7717–7722. doi: 10.1128/AEM.01143-10. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Jiao Y, Navid A, Stewart BJ, McKinlay JB, Thelen MP, Pett-Ridge J. 2012. Syntrophic metabolism of a co-culture containing Clostridium cellulolyticum and Rhodopseudomonas palustris for hydrogen production. Int J Hydrog Energy 37:11719–11726. doi: 10.1016/j.ijhydene.2012.05.100. [DOI] [Google Scholar]
- 31.Choorit W, Saikeur A, Chodok P, Prasertsan P, Kantachote D. 2011. Production of biomass and extracellular 5-aminolevulinic acid by Rhodopseudomonas palustris KG31 under light and dark conditions using volatile fatty acid. J Biosci Bioeng 111:658–664. doi: 10.1016/j.jbiosc.2011.01.014. [DOI] [PubMed] [Google Scholar]
- 32.Merugu R, Girisham S, Reddy S. 2010. Production of PHB (polyhydroxybutyrate) by Rhodopseudomonas palustris KU003 under nitrogen limitation. Int J Appl Biol Pharm 2:686–688. [Google Scholar]
- 33.Doud DF, Holmes EC, Richter H, Molitor B, Jander G, Angenent LT. 2017. Metabolic engineering of Rhodopseudomonas palustris for the obligate reduction of n-butyrate to n-butanol. Biotechnol Biofuels 10:178. doi: 10.1186/s13068-017-0864-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.McKinlay JB, Oda Y, Rühl M, Posto AL, Sauer U, Harwood CS. 2014. Non-growing Rhodopseudomonas palustris increases the hydrogen gas yield from acetate by shifting from the glyoxylate shunt to the tricarboxylic acid cycle. J Biol Chem 289:1960–1970. doi: 10.1074/jbc.M113.527515. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Ranaivoarisoa TO, Singh R, Rengasamy K, Guzman MS, Bose A. 2019. Towards sustainable bioplastic production using the photoautotrophic bacterium Rhodopseudomonas palustris TIE-1. J Ind Microbiol Biotechnol 46:1401–1410. doi: 10.1007/s10295-019-02165-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36.Gupta D, Sutherland MC, Rengasamy K, Meacham JM, Kranz RG, Bose A. 2019. Photoferrotrophs produce a PioAB electron conduit for extracellular electron uptake. mBio 10:e02668-19. doi: 10.1128/mBio.02668-19. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37.Sankari S, O’Brian MR. 2016. The Bradyrhizobium japonicum ferrous iron transporter FeoAB is required for ferric iron utilization in free living aerobic cells and for symbiosis. J Biol Chem 291:15653–15662. doi: 10.1074/jbc.M116.734129. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Grosse C, Scherer J, Koch D, Otto M, Taudte N, Grass G. 2006. A new ferrous iron‐uptake transporter, EfeU (YcdN), from Escherichia coli. Mol Microbiol 62:120–131. doi: 10.1111/j.1365-2958.2006.05326.x. [DOI] [PubMed] [Google Scholar]
- 39.Sabri M, Léveillé S, Dozois CM. 2006. A SitABCD homologue from an avian pathogenic Escherichia coli strain mediates transport of iron and manganese and resistance to hydrogen peroxide. Microbiology 152:745–758. doi: 10.1099/mic.0.28682-0. [DOI] [PubMed] [Google Scholar]
- 40.Hill PJ, Cockayne A, Landers P, Morrissey JA, Sims CM, Williams P. 1998. SirR, a novel iron-dependent repressor in Staphylococcus epidermidis. Infect Immun 66:4123–4129. doi: 10.1128/IAI.66.9.4123-4129.1998. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Horsburgh MJ, Wharton SJ, Cox AG, Ingham E, Peacock S, Foster SJ. 2002. MntR modulates expression of the PerR regulon and superoxide resistance in Staphylococcus aureus through control of manganese uptake. Mol Microbiol 44:1269–1286. doi: 10.1046/j.1365-2958.2002.02944.x. [DOI] [PubMed] [Google Scholar]
- 42.Nevo Y, Nelson N. 2006. The NRAMP family of metal-ion transporters. Biochim Biophys Acta 1763:609–620. doi: 10.1016/j.bbamcr.2006.05.007. [DOI] [PubMed] [Google Scholar]
- 43.Courville P, Chaloupka R, Cellier M. 2006. Recent progress in structure–function analyses of Nramp proton-dependent metal-ion transporters. Biochem Cell Biol 84:960–978. doi: 10.1139/o06-193. [DOI] [PubMed] [Google Scholar]
- 44.Weaver EA, Wyckoff EE, Mey AR, Morrison R, Payne SM. 2013. FeoA and FeoC are essential components of the Vibrio cholerae ferrous iron uptake system, and FeoC interacts with FeoB. J Bacteriol 195:4826–4835. doi: 10.1128/JB.00738-13. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.Chai S, Welch TJ, Crosa JH. 1998. Characterization of the interaction between Fur and the iron transport promoter of the virulence plasmid in Vibrio anguillarum. J Biol Chem 273:33841–33847. doi: 10.1074/jbc.273.50.33841. [DOI] [PubMed] [Google Scholar]
- 46.Morrison RR. 2012. Purification of Feo proteins and analysis of residues important for Feo protein interactions. PhD thesis. University of Texas in Austin, Austin, TX. [Google Scholar]
- 47.Rong C, Huang Y, Zhang W, Jiang W, Li Y, Li J. 2008. Ferrous iron transport protein B gene (feoB1) plays an accessory role in magnetosome formation in Magnetospirillum gryphiswaldense strain MSR-1. Res Microbiol 159:530–536. doi: 10.1016/j.resmic.2008.06.005. [DOI] [PubMed] [Google Scholar]
- 48.Kammler M, Schön C, Hantke K. 1993. Characterization of the ferrous iron uptake system of Escherichia coli. J Bacteriol 175:6212–6219. doi: 10.1128/jb.175.19.6212-6219.1993. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49.Khan SR, Gaines J, Roop RM, Farrand SK. 2008. Broad-host-range expression vectors with tightly regulated promoters and their use to examine the influence of TraR and TraM expression on Ti plasmid quorum sensing. Appl Environ Microbiol 74:5053–5062. doi: 10.1128/AEM.01098-08. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.Fogg PC, Westbye AB, Beatty JT. 2012. One for all or all for one: heterogeneous expression and host cell lysis are key to gene transfer agent activity in Rhodobacter capsulatus. PLoS One 7:e43772. doi: 10.1371/journal.pone.0043772. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51.Romeo AM, Christen L, Niles EG, Kosman DJ. 2001. Intracellular chelation of iron by bipyridyl inhibits DNA virus replication ribonucleotide reductase maturation as a probe of intracellular iron pools. J Biol Chem 276:24301–24308. doi: 10.1074/jbc.M010806200. [DOI] [PubMed] [Google Scholar]
- 52.Grass G, Franke S, Taudte N, Nies DH, Kucharski LM, Maguire ME, Rensing C. 2005. The metal permease ZupT from Escherichia coli is a transporter with a broad substrate spectrum. J Bacteriol 187:1604–1611. doi: 10.1128/JB.187.5.1604-1611.2005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Rajasekaran MB, Nilapwar S, Andrews SC, Watson KA. 2010. EfeO-cupredoxins: major new members of the cupredoxin superfamily with roles in bacterial iron transport. Biometals 23:1. doi: 10.1007/s10534-009-9262-z. [DOI] [PubMed] [Google Scholar]
- 54.Cartron ML, Maddocks S, Gillingham P, Craven CJ, Andrews SC. 2006. Feo—transport of ferrous iron into bacteria. Biometals 19:143–157. doi: 10.1007/s10534-006-0003-2. [DOI] [PubMed] [Google Scholar]
- 55.Wood EJ. 1987. Data for biochemical research, p 97 In Dawson RMC, Elliott DC, Elliott WH, Jones KM (ed), Biochemical education. Oxford Science Publications, Oxford University Press, Oxford, United Kingdom. [Google Scholar]
- 56.Grass G, Wong MD, Rosen BP, Smith RL, Rensing C. 2002. ZupT is a Zn(II) uptake system in Escherichia coli. J Bacteriol 184:864–866. doi: 10.1128/jb.184.3.864-866.2002. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Dong Z, Guo S, Fu H, Gao H. 2017. Investigation of a spontaneous mutant reveals novel features of iron uptake in Shewanella oneidensis. Sci Rep 7:11788. doi: 10.1038/s41598-017-11987-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Kicic A, Chua AC, Baker E. 2001. Effect of iron chelators on proliferation and iron uptake in hepatoma cells. ACS 92:3093–3110. doi:. [DOI] [PubMed] [Google Scholar]
- 59.Hallaway M. 1959. Metal chelating agents, p 155 In Dawson RMC, Elliott DC, Elliott WH, Jones KM (ed), Data for biochemical research. Oxford University Press, Clarendon, Oxford, United Kingdom. [Google Scholar]
- 60.Maguire M. 2007. Magnesium, manganese and divalent cation transport assay in intact cells, p 289–307. In Schatten H, Eisenstark A, Eisenstark A (ed), Salmonella: methods and protocols. Humana Press, Totowa, NJ. [DOI] [PubMed] [Google Scholar]
- 61.Irving H, Mellor D. 1962. 1002. The stability of metal complexes of 1,10-phenanthroline and its analogues. Part I. 1,10-Phenanthroline and 2,2′-bipyridyl. ACS (Res) 1962:5222–5237. doi: 10.1039/JR9620005222. [DOI] [Google Scholar]
- 62.Kovach ME, Elzer PH, Hill DS, Robertson GT, Farris MA, Roop RM II, Peterson KM. 1995. Four new derivatives of the broad-host-range cloning vector pBBR1MCS, carrying different antibiotic-resistance cassettes. Gene 166:175–176. doi: 10.1016/0378-1119(95)00584-1. [DOI] [PubMed] [Google Scholar]
- 63.Banin E, Brady KM, Greenberg EP. 2006. Chelator-induced dispersal and killing of Pseudomonas aeruginosa cells in a biofilm. Appl Environ Microbiol 72:2064–2069. doi: 10.1128/AEM.72.3.2064-2069.2006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 64.Bose A, Newman DK. 2011. Regulation of the phototrophic iron oxidation (pio) genes in Rhodopseudomonas palustris TIE‐1 is mediated by the global regulator, FixK. Mol Microbiol 79:63–75. doi: 10.1111/j.1365-2958.2010.07430.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 65.Guzman MS, Rengasamy K, Binkley MM, Jones C, Ranaivoarisoa TO, Singh R, Fike DA, Meacham JM, Bose A. 2019. Phototrophic extracellular electron uptake is linked to carbon dioxide fixation in the bacterium Rhodopseudomonas palustris. Nat Commun 10:1355. doi: 10.1038/s41467-019-09377-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 66.Hantke K. 1981. Regulation of ferric iron transport in Escherichia coli K12: isolation of a constitutive mutant. Mol Gen Genet 182:288–292. doi: 10.1007/BF00269672. [DOI] [PubMed] [Google Scholar]
- 67.Bagg A, Neilands J. 1987. Molecular mechanism of regulation of siderophore-mediated iron assimilation. Microbiol Rev 51:509–518. doi: 10.1128/MMBR.51.4.509-518.1987. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 68.Rodionov DA, Gelfand MS, Todd JD, Curson AR, Johnston AW. 2006. Computational reconstruction of iron-and manganese-responsive transcriptional networks in α-proteobacteria. PLoS Comput Biol 2:e163. doi: 10.1371/journal.pcbi.0020163. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 69.Spiro S, Guest JR. 1990. FNR and its role in oxygen-regulated gene expression in Escherichia coli. FEMS Microbiol Rev 6:399–428. doi: 10.1111/j.1574-6968.1990.tb04109.x. [DOI] [PubMed] [Google Scholar]
- 70.Schröder I, Johnson E, De Vries S. 2003. Microbial ferric iron reductases. FEMS Microbiol Rev 27:427–447. doi: 10.1016/S0168-6445(03)00043-3. [DOI] [PubMed] [Google Scholar]
- 71.Nealson KH, Myers CR. 1992. Microbial reduction of manganese and iron: new approaches to carbon cycling. Appl Environ Microbiol 58:439–443. doi: 10.1128/AEM.58.2.439-443.1992. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 72.Yang J, Sangwan I, Lindemann A, Hauser F, Hennecke H, Fischer H-M, O’Brian MR. 2006. Bradyrhizobium japonicum senses iron through the status of haem to regulate iron homeostasis and metabolism. Mol Microbiol 60:427–437. doi: 10.1111/j.1365-2958.2006.05101.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 73.Small SK, Puri S, O’Brian MR. 2009. Heme-dependent metalloregulation by the iron response regulator (Irr) protein in Rhizobium and other Alpha-proteobacteria. Biometals 22:89–97. doi: 10.1007/s10534-008-9192-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Kim H, Lee H, Shin D. 2013. The FeoC protein leads to high cellular levels of the Fe (II) transporter FeoB by preventing FtsH protease regulation of FeoB in Salmonella enterica. J Bacteriol 195:3364–3370. doi: 10.1128/JB.00343-13. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 75.Sestok AE, Linkous RO, Smith AT. 2018. Toward a mechanistic understanding of Feo-mediated ferrous iron uptake. Metallomics 10:887–898. doi: 10.1039/c8mt00097b. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 76.Platero R, Peixoto L, O’Brian MR, Fabiano E. 2004. Fur is involved in manganese-dependent regulation of mntA (sitA) expression in Sinorhizobium meliloti. Appl Environ Microbiol 70:4349–4355. doi: 10.1128/AEM.70.7.4349-4355.2004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 77.Flora SJ, Pachauri V. 2010. Chelation in metal intoxication. Int J Environ Res Public Health 7:2745–2788. doi: 10.3390/ijerph7072745. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Matsui M, Tomita M, Kanai A. 2013. Comprehensive computational analysis of bacterial CRP/FNR superfamily and its target motifs reveals stepwise evolution of transcriptional networks. Genome Biol Evol 5:267–282. doi: 10.1093/gbe/evt004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 79.Ehrenreich A, Widdel F. 1994. Anaerobic oxidation of ferrous iron by purple bacteria, a new type of phototrophic metabolism. Appl Environ Microbiol 60:4517–4526. doi: 10.1128/AEM.60.12.4517-4526.1994. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 80.Miller MJ, Zhu H, Xu Y, Wu C, Walz AJ, Vergne A, Roosenberg JM, Moraski G, Minnick AA, McKee-Dolence J, Hu J, Fennell K, Kurt Dolence E, Dong L, Franzblau S, Malouin F, Möllmann U. 2009. Utilization of microbial iron assimilation processes for the development of new antibiotics and inspiration for the design of new anticancer agents. Biometals 22:61–75. doi: 10.1007/s10534-008-9185-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 81.Boratyn GM, Schäffer AA, Agarwala R, Altschul SF, Lipman DJ, Madden TL. 2012. Domain enhanced lookup time accelerated BLAST. Biol Direct 7:12. doi: 10.1186/1745-6150-7-12. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 82.Lipman DJ, Pearson WR. 1985. Rapid and sensitive protein similarity searches. Science 227:1435–1441. doi: 10.1126/science.2983426. [DOI] [PubMed] [Google Scholar]
- 83.Markowitz VM, Chen I-MA, Palaniappan K, Chu K, Szeto E, Grechkin Y, Ratner A, Jacob B, Huang J, Williams P, Huntemann M, Anderson I, Mavromatis K, Ivanova NN, Kyrpides NC. 2012. IMG: the Integrated Microbial Genomes database and comparative analysis system. Nucleic Acids Res 40:D115–D122. doi: 10.1093/nar/gkr1044. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 84.Münch R, Hiller K, Grote A, Scheer M, Klein J, Schobert M, Jahn D. 2005. Virtual Footprint and PRODORIC: an integrative framework for regulon prediction in prokaryotes. Bioinformatics 21:4187–4189. doi: 10.1093/bioinformatics/bti635. [DOI] [PubMed] [Google Scholar]
- 85.Simon R, Priefer U, Puhler A. 1983. A broad host range mobilization system for in vivo genetic engineering: transposon mutagenesis in gram negative bacteria. Nat Biotechnol 1:784–791. doi: 10.1038/nbt1183-784. [DOI] [Google Scholar]







