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Applied and Environmental Microbiology, October 2008, p. 6263-6270, Vol. 74, No. 20
0099-2240/08/$08.00+0 doi:10.1128/AEM.00964-08
Copyright © 2008, American Society for Microbiology. All Rights Reserved.
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Geosciences Research Division, Scripps Institution of Oceanography, University of California, San Diego, La Jolla, California 92093
Received 28 April 2008/ Accepted 20 August 2008
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Bacterial heme uptake is accomplished by using mechanisms similar to siderophore and B12 uptake pathways (45). From the extracellular environment, a TonB-dependent outer membrane receptor selectively transports heme into the periplasmic space. In the periplasm, an ABC transport system consisting of a periplasmic binding protein, a membrane permease, and an ATPase is employed to transport heme into the cytoplasm (28). Once the heme has been internalized, it may be directly incorporated into heme-containing proteins or broken down by a heme oxygenase for storage or use in other forms (47).
In oxic marine environments, minimal inputs of iron combined with the low solubility of Fe(III) lead to subnanomolar concentrations of iron, which limit autotrophic and heterotrophic productivity in portions of the ocean (6, 7, 33). Competition for iron among organisms is consequently expected to be intense, and the ability to access a wide range of iron compounds would be advantageous. Various marine bacteria have been shown to use inorganic iron, produce their own siderophores, and use exogenous siderophores produced by other organisms (18, 34, 52). Some experiments indicate that marine bacteria are able to acquire iron from heme and other porphyrin complexes (52). However, the mechanisms behind heme iron uptake and the generality of its bioavailability to marine bacteria have not been studied in detail despite heme's abundance in biological systems. In particular, because of the localization of phytoplankton iron in heme-rich photosystems, heme could represent as much as 45% of the iron in phytoplankton and form a substantial portion of particulate iron in oceanic systems (17, 46). Bacteria living in association with phytoplankton or those involved in the recycling of particulate organic matter are especially likely to benefit from the ability to access heme iron.
The only marine bacteria in which heme uptake has been studied extensively are pathogenic marine vibrios, including Vibrio cholerae, V. vulnificus, and V. anguillarum (20, 30, 38). The heme uptake systems in these organisms are similar to those studied in phylogenetically diverse bacteria (29, 40, 45), suggesting that such systems could occur in other marine bacteria. However, the relevance of these systems to life in the marine environment is unclear, since heme uptake capabilities may be present in these organisms solely for use during infection.
We used the Flexibacteriaceae family member Microscilla marina, whose genome has been sequenced, as a model organism to study heme uptake. Based on 16S rRNA gene sequences, M. marina is the closest cultured bacterium to a group of organisms associated with the cyanobacterium Trichodesmium (24; E. Mann, unpublished data) and it is a member of the phylum Bacteroidetes, the members of which are abundant on marine particles (8, 9, 41). Therefore, M. marina was considered a good representative of the marine bacteria involved in organic matter remineralization on particles where heme may be a significant source of iron. In addition, we searched the genomes of numerous marine bacteria for heme transport systems in order to assess their distribution, providing insight into the bioavailability and cycling of heme in the marine environment.
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Heme uptake.
To synthesize [55Fe(III)]heme, 55FeCl3 (25 µM) was refluxed with equimolar protoporphyrin IX in glacial acetic acid containing 0.1 M sodium acetate for 2 h to insert iron into the porphyrin ring forming Fe(III)-heme (4). The glacial acetic acid solution was diluted to 50% strength with water, and the mixture was then passed through a column of Diaion HP20S resin. Heme was retained on the column, washed with water, and eluted in acetone. The concentration and purity of the [55Fe(III)]heme were determined by UV-Vis spectroscopy by comparison with purchased heme standards (Sigma).
M. marina cultures for uptake experiments were grown in PC medium with 30 nM added FeCl3 to obtain iron-deficient cells and in PC medium with 5 µM added FeCl3 to obtain iron-replete cells. Cultures were harvested by centrifugation during exponential growth and rinsed and resuspended twice in sterile seawater to ensure that all of the culture medium was removed. [55Fe(III)]heme at 5 nM was added to triplicate bottles containing the resuspended M. marina and a single glutaraldehyde (0.01%)-killed control. To monitor uptake of [55Fe(III)]heme, 2-ml samples were taken from each bottle at regular intervals and filtered with a 0.45-µm Durapore filter (Millipore). The filters were washed with Ti-EDTA-citrate wash (22) and filtered seawater, and retained 55Fe was quantified by liquid scintillation counting.
Gene expression.
M. marina growing on different iron sources or at differing iron concentrations was harvested in mid-log phase for analysis of gene expression. Iron-replete cultures in 2216 medium were inoculated in PC medium with 30 nM added FeCl3 and allowed to grow for 24 h, resulting in mild iron stress (data not shown). One milliliter of the mildly stressed culture was then inoculated into 20 ml of PC medium containing 30 nM added FeCl3, 5 µM added FeCl3, or 1.5 µM Fe(III)-heme. After 24 h of growth, cells were harvested by centrifugation and RNA was isolated with TRIzol reagent (Invitrogen) by following the manufacturer's instructions, with the exception that cells were initially incubated with TRIzol at 50°C for 30 min to lyse cells. The isolated RNA was then treated with amplification grade DNase I (Invitrogen), recovered with an RNeasy purification kit (Qiagen), and quantified by using absorbance at 260 and 280 nm measured on a spectrophotometer. Total RNA (200 ng) was reverse transcribed with random hexamer primers to produce cDNA with SuperScript II reverse transcriptase and supplied buffers by following the manufacturer's instructions (Invitrogen). Parallel reactions were run without reverse transcriptase to ensure that there was no significant contaminating DNA.
Real-time quantitative PCR (RT-Q-PCR) was performed on the cDNA to quantify relative transcript amounts on a Stratagene Mx3000P with the Brilliant Sybr green Q-PCR master mix (Stratagene) and gene-specific primers (0.42 µM; Table 1) designed by using the draft genome of M. marina. Temperature profiles for the PCR consisted of an initial 10 min at 95°C, followed by 40 cycles of 95°C for 1 min, 30 s at an annealing temperature several degrees below the melting temperature of the primers (53 to 56°C), and 30 s at 72°C. Five dilutions of genomic DNA were analyzed for each gene to produce a standard curve for quantification of samples based on the crossing of a threshold fluorescence level chosen within the early range of exponential PCR amplification. The genomic DNA was isolated from M. marina cells grown on 2216 medium with a DNeasy kit (Qiagen) and quantified on a spectrophotometer. RNA samples processed without reverse transcriptase had no products or were amplified much later within the run than experimental samples. Melting curve analysis following the PCR and selected analysis of products by gel electrophoresis (2.2% agarose) verified that a single product of the expected length was amplified by each primer set.
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TABLE 1. M. marina genes whose expression was assessed by RT-Q-PCR and the primers used in the analysis
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Phylogenetic trees were constructed with the putative heme outer membrane receptors identified from HMM searches of marine bacterial genomes. Marine bacterial sequences and reference genes were aligned by using ClustalX, and Fitch-Margoliash trees based on protein distances were built with PHYLIP 3.6 (14). A bootstrap analysis consisting of 100 replications was conducted, and a consensus tree was generated. 16S rRNA gene trees were constructed in a similar manner by using positions 50 to 1325 of the aligned sequences.
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FIG. 1. Growth of M. marina with 5 µM added Fe (iron replete), 30 nM added Fe (iron limited), or 5 µM Fe(III)-heme. OD600, optical density at 600 nm.
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FIG. 2. Uptake of [55Fe]heme by M. marina under iron-limited (closed circles) or iron-replete (open circles) conditions.
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TABLE 2. Top BLAST hits of putative M. marina heme transport proteins in the Swiss-Prot database (April 2008)a
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FIG. 3. Expression of heme transport, siderophore biosynthesis, iron regulation, and housekeeping genes in M. marina under different growth conditions assessed by RT-Q-PCR. Quantities of transcripts during growth with 30 nM Fe (iron limited) or 1.5 µM heme were normalized to transcript quantities under iron-replete conditions (5 µM Fe).
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Three members of the Fur metalloregulatory protein family were identified in the M. marina genome (EAY24380, EAY30621, and EAY31090). Only EAY31090 responded to iron stress or growth on heme, being upregulated under both conditions, which suggests that it may be an iron metalloregulatory protein (Fig. 3) (13).
Transcript quantities were normalized to total RNA, which is predominately rRNA. The essentially constant expression levels of two genes involved in DNA and RNA polymerization and commonly used as controls, rpoD and gyrA (10), confirm that the observed upregulation of putative heme transport genes is not due to changes in the proportion of rRNA relative to mRNA under differing growth conditions (Fig. 3).
Heme uptake genes in marine bacteria.
As with M. marina, the genomes of 148 additional marine bacteria were searched for heme transport components. These bacteria are primarily from the water column, though some are from sediments. A representative subset of the results which demonstrates trends in the distribution of putative heme transporters and illustrates their potential phylogenetic diversity is presented here (Fig. 4 and 5; see also Fig. S1 in the supplemental material); for the complete search results, see Table S2 in the supplemental material. Searches with the heme outer membrane receptor HMM yielded some high-scoring sequences in the gamma- and alphaproteobacteria, and additional sequences with intermediate scores which may also be heme transporters were identified (see Table S2 in the supplemental material). The top hits to this HMM from each genome were tested with the Pfam PF00593 model for TonB-dependent outer membrane receptors (see Table S2 in the supplemental material). Sequences which scored above the trusted cutoff threshold on this model, and thus appeared to be TonB-dependent receptors, were used to construct a phylogeny to determine where they clustered in relation to known heme receptors. High-scoring receptors from gammaproteobacteria (e.g., Pseudoalteromonas haloplanktis, Photobacterium profundum 3TCK) and alphaproteobacteria (e.g., Parvularcula bermudensis, Oceanicaulis alexandrii) were closely associated with characterized heme outer membrane receptors with high bootstrap support. These sequences formed a distinct clade from siderophore and B12 outer membrane receptors, strongly suggesting that the genes also code for heme receptors (Fig. 4; see Fig. S1 in the supplemental material). In the alphaproteobacteria, an additional group composed predominately of Roseobacter sequences with intermediate heme outer membrane receptor HMM scores was formed (see Fig. S1 in the supplemental material). These sequences are likely to be heme transporters given their proximity to HemS proteins in the genomes of these roseobacters (see below). Because of the lack of characterized outer membrane receptors in members of the phylum Bacteroidetes, phylogenetic analysis of putative heme transporters in this group was not possible.
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FIG. 4. Phylogenetic tree of TonB-dependent outer membrane receptor protein sequences from representative gammaproteobacteria. Top hits to the heme outer membrane receptor HMM in marine bacteria are included along with reference siderophore, B12, and heme (in bold) outer membrane receptors. Functional labels are placed on sequence groups based on substrate specificity of reference sequences within the group. The tree was constructed from phylogenetic distances by the Fitch-Margoliash method in PHYLIP 3.6. Bootstrap values (from 100 resamplings) are indicated for nodes with values of >50. The scale bar indicates distances in substitutions per site. FhuA from Escherichia coli was used as an outgroup. For the GenBank accession numbers of marine bacterial sequences, see Table S2 in the supplemental material. Reference heme receptors and their GenBank accession numbers are as follows: ChuA from E. coli, AAG44838; ShuA from Shigella dysenteriae, AAC27809; HemR from Yersinia enterocolitica, CAA48250; HasR from Serratia marcescens, CAE46936; HasA from Pseudomonas fluorescens, BAA88490; HutA from V. cholerae, AAF96478; HutA from V. parahaemolyticus, BAC62225; PhuR from Pseudomonas aeruginosa, AAC13289. Reference siderophore receptors and their GenBank accession numbers are as follows: FhuA from E. coli, P06971; FhuE from E. coli, P16869; IutA from E. coli, P14542; FoxA from Y. enterocolitica, Q01674; VuuA from V. vulnificus, AAF28471. Reference B12 receptors and their GenBank accession numbers are as follows: BtuB from Salmonella enterica serovar Typhimurium, P37409; BtuB from E. coli, P06129.
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FIG. 5. Distribution of putative heme transport components (outer membrane receptors and heme oxygenases) with respect to bacterial phylogeny. The tree is an unrooted 16S rRNA gene tree of representative marine bacteria whose genomes were searched for heme uptake components constructed by the Fitch-Margoliash method in PHYLIP 3.6 and bootstrapped with 100 replicates. Positions 50 to 1325 of the 16S rRNA gene with respect to the E. coli sequence were used in this analysis. The scale bar indicates distance in substitutions per site. Organisms which had a good hit to the heme receptor HMM (scores of >100 and E values of <1 E-27 in gammaproteobacteria; scores of >50 and E values of <2 E-12 in alphaproteobacteria and members of the phylum Bacteroidetes) are in bold, and organisms with a HemS-type heme oxygenase (HMM scores of >150 and E values of <1 E-45) are underlined.
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Putative heme transport cluster in M. marina.
In the draft genome of M. marina, a cluster of putative heme transport genes, including an outer membrane receptor, an ABC transport system, and a heme oxygenase, was identified based on sequence similarity to known heme transport systems (Table 2). Because TonB-dependent outer membrane receptors and ABC transport proteins are involved in the uptake of many metal chelates, including heme, siderophores, and B12 (45), the presence of additional genes with similarity to proteins specifically involved in heme transport aided the identification of the substrate specificity of the uptake system. These genes encode a heme oxygenase (hemS) and an outer membrane heme-binding protein (hmuY) and may be used to help identify heme transporters in bacterial genomes (see below) or to study organisms responsible for heme uptake in the environment (29, 43, 44, 47).
Analysis of gene expression showed that the putative heme transporter genes are expressed and upregulated under iron-limiting conditions and during growth on Fe(III)-heme as an iron source (Fig. 3). These results are consistent with the putative role of the cluster in heme transport, but there is no evidence for selective upregulation of the cluster during growth on heme. When M. marina is iron limited or growing on Fe(III)-heme, the expression profiles of putative heme transport and siderophore biosynthesis genes are extremely similar, suggesting similar physiological states (Fig. 3). Growth on Fe(III)-heme appears to induce iron stress and an activation of many iron acquisition mechanisms, including heme and siderophore uptake pathways, rather than specific upregulation of heme uptake systems. General responses to iron availability are often regulated by Fur proteins (13). A putative fur gene has been identified and found to be upregulated under iron stress in M. marina, providing a potential mechanism for the observed response (Fig. 3). In some cases, TonB-dependent receptors participate in their own regulation, acting as both transporters and sensors of their substrate (26, 27). However, HmuR in M. marina lacks the N-terminal domain involved in signal transduction, nor are anti-sigma factors or extracytoplasmic function sigma factors involved in signaling located near the putative heme transport cluster (data not shown). This suggests that M. marina cannot sense external heme and must rely on a general iron-responsive element for regulation, consistent with the observed upregulation of multiple iron uptake pathways during growth on Fe(III)-heme.
The genetic evidence that M. marina contains a heme transporter is also supported by physiological studies showing that M. marina is capable of taking up heme-bound iron(III) and can grow on heme as a sole iron source. Uptake of 55Fe from [55Fe(III)]heme was observed under iron-limited conditions but suppressed under iron-replete conditions, showing that uptake was mediated by an iron-regulated pathway and consistent with gene expression patterns of the putative heme uptake cluster (Fig. 2). While internalization of 55Fe from [55Fe(III)]heme does not conclusively demonstrate that the entire heme molecule was transported, the uptake was rapid and immediate, which might not be expected under some alternate explanations for 55Fe uptake such as siderophore uptake. Siderophores would need to be excreted into the uptake medium and extract iron from heme prior to initiation of uptake. M. marina has the ability to grow on Fe(III)-heme as an iron source, and though this may be mediated by multiple iron uptake pathways, it is consistent with the presence of a heme transport system. While genetic manipulations, including knockout experiments, could provide more definitive evidence that the putative heme transport cluster is responsible for heme uptake, such techniques are not currently available for M. marina, nor have they been developed for other, related, marine bacteria. However, the strong sequence similarity of the cluster to known heme transport proteins and its regulatory behavior, in conjunction with physiological evidence demonstrating M. marina's capability to access heme bound iron(III), strongly suggest that the cluster is involved in heme transport.
Distribution of putative heme transport genes in marine bacteria.
Having examined the putative heme transport system in M. marina, we searched the genomes of numerous marine bacteria for related transport systems to better understand the distribution of heme uptake capabilities and the role of heme in the marine iron cycle. Putative heme transport systems were identified in representatives of the gamma- and alphaproteobacteria and the phylum Bacteroidetes based on the identification of a putative heme receptor and, in certain cases, a HemS-type heme oxygenase colocated in the genome (Fig. 5). The most notable feature in the distribution is a lack of heme transporters in known free-living bacteria, including Pelagibacter ubique, Silicibacter pomeroyi, and all marine cyanobacteria (16, 36, 37). In fact, these organisms do not appear to have any TonB-dependent receptors, as no candidate sequences were identified by using the Pfam PF00593 HMM for TonB-dependent outer membrane receptors (data not shown). Putative heme transporters were generally found in bacteria from taxa known to be associated with particles such as vibrios, roseobacters, and members of the phylum Bacteroidetes (8, 9, 19, 41).
The Roseobacter clade, in which the habitats of sequenced representatives have been examined (37), provides a good example of this distribution of heme transporters (Fig. 5). S. pomeroyi, which is thought to be mainly free living (36, 37), lacks putative heme transporters along with other TonB-dependent receptors. In contrast, sulfitobacters and Silicibacter sp. strain TM1040, which have been found associated with dinoflagellates (1, 25), possess putative heme transporters (Fig. 5; see Table S2 in the supplemental material). These putative heme receptors are among the few TonB-dependent receptors in the genomes, and in fact in Silicibacter sp. strain TM1040, the putative heme receptor is the only TonB-dependent receptor, implying that the ability to access heme is especially important for the survival of this bacterium.
Although major advances have been made in understanding the distribution of iron concentrations in the ocean (35), characterization of iron speciation at the molecular level and a mechanistic understanding of iron fluxes have been difficult to achieve as a result of the low concentration and complicated chemistry of iron. Organically complexed iron is known to dominate the dissolved iron pool, and microorganisms must access some component of this iron to maintain observed growth rates (2, 23, 32, 42). The iron acquisition strategies employed by marine microorganisms may provide greater insight into the forms and cycling of oceanic iron, as competition for iron is expected to result in selection of uptake mechanisms capable of accessing iron species which are abundant in an organism's environment. The presence of putative heme transporters in bacteria from taxa which are abundant on particles and their absence in free-living bacteria indicate that heme is primarily available in or near particles but is not present in seawater at significant concentrations in the dissolved form (Fig. 5). This hypothesized distribution is consistent with the hydrophobic, light-sensitive nature of heme, its tendency to form aggregates, and preliminary data on iron-porphyrin distributions in aquatic environments (3, 51, 53). As a major intracellular form of iron, heme may be an important iron source for bacteria living in association with other organisms, although the actual distribution of heme in the ocean has yet to be determined (17). Cell lysis or death may free heme for use by other bacteria, though its light sensitivity and hydrophobicity will likely minimize its importance in the dissolved phase. Particle-associated bacteria play an important role in the marine iron cycle, directly recycling cellular iron forms such as heme from phytoplankton or detritus which might otherwise be lost from the ecosystem due to sinking fluxes (50).
We thank the Moore Foundation for sequencing the M. marina genome and Margo Haygood, who initiated and oversaw the genome project. Sheila Podell, Terry Gasterlaand, Christine Anderson, and Chris Dupont assisted with bioinformatic analyses. Information on bacterial taxa associated with Trichodesmium colonies in the field was provided prior to publication by Elizabeth Mann. Assistance with RNA isolation and Q-PCR techniques from Rhona Stuart and Lisa Sudek was much appreciated. Two undergraduates, Joshawna Nunnery and Kristine Lim, helped develop the radiolabeled heme synthesis and conducted preliminary uptake experiments. We are grateful for helpful discussions and advice from Chris Dupont and Brian Palenik.
Published ahead of print on 29 August 2008. ![]()
Supplemental material for this article may be found at http://aem.asm.org/. ![]()
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