Abstract
Microbial Mn(II) oxidation has important biogeochemical consequences in marine, freshwater, and terrestrial environments, but many aspects of the physiology and biochemistry of this process remain obscure. Here, we report genomic insights into Mn(II) oxidation by the marine alphaproteobacterium Aurantimonas sp. strain SI85-9A1, isolated from the oxic/anoxic interface of a stratified fjord. The SI85-9A1 genome harbors the genetic potential for metabolic versatility, with genes for organoheterotrophy, methylotrophy, oxidation of sulfur and carbon monoxide, the ability to grow over a wide range of O2 concentrations (including microaerobic conditions), and the complete Calvin cycle for carbon fixation. Although no growth could be detected under autotrophic conditions with Mn(II) as the sole electron donor, cultures of SI85-9A1 grown on glycerol are dramatically stimulated by addition of Mn(II), suggesting an energetic benefit from Mn(II) oxidation. A putative Mn(II) oxidase is encoded by duplicated multicopper oxidase genes that have a complex evolutionary history including multiple gene duplication, loss, and ancient horizontal transfer events. The Mn(II) oxidase was most abundant in the extracellular fraction, where it cooccurs with a putative hemolysin-type Ca2+-binding peroxidase. Regulatory elements governing the cellular response to Fe and Mn concentration were identified, and 39 targets of these regulators were detected. The putative Mn(II) oxidase genes were not among the predicted targets, indicating that regulation of Mn(II) oxidation is controlled by other factors yet to be identified. Overall, our results provide novel insights into the physiology and biochemistry of Mn(II) oxidation and reveal a genome specialized for life at the oxic/anoxic interface.
Mn(II)-oxidizing bacteria are thought to be responsible for catalyzing the formation of most naturally occurring Mn oxides, minerals that are abundant in both marine and terrestrial environments (67). As strong adsorptive scavengers, Mn oxides control the distribution and availability of many trace elements, and as the strongest environmentally relevant oxidant after oxygen, they serve as electron acceptors for anaerobic respiration (67). Because of the broad influence that Mn oxides exert on biogeochemical cycles, it is important to understand the biological mechanism of their formation. The ability of microorganisms to oxidize Mn(II) has been recognized for over a century, and more recently, this activity has been identified in phylogenetically diverse bacteria (70). Despite the biogeochemical and microbiological significance of Mn(II) oxidation, details of the biochemistry of this process have only recently emerged, and the physiological function of Mn(II) oxidation remains mysterious. Mn(II) oxidation by O2 is thermodynamically favorable and has long been hypothesized to support chemolithoautotrophic growth, but to date, no link between autotrophy and Mn(II) oxidation has been clearly demonstrated.
The marine alphaproteobacterium Aurantimonas sp. strain SI85-9A1 is to date the most compelling candidate for a Mn(II)-oxidizing autotroph. Isolated from the oxic/anoxic interface (120-m depth) of Saanich Inlet in 1985 based on its ability to oxidize Mn(II) to Mn(III/IV) oxides during heterotrophic growth, it also has genes for ribulose-1,5-bisphosphate carboxylase/oxygenase (RubisCO) (12), a key enzyme of CO2 fixation by the Calvin-Benson cycle (65). These genes confer RubisCO activity to Escherichia coli cells in which they are heterologously expressed, but no RubisCO activity has been detected in cultures of SI85-9A1 (12). Though unable to grow with Mn(II) as the sole energy source under the laboratory conditions tested to date, SI85-9A1 has remained of interest because of the possibility that its RubisCO protein is linked to Mn(II) oxidation either under unknown conditions or during mixotrophic growth.
SI85-9A1 is one of a growing number of diverse Mn(II) oxidizers to be recognized within the Alphaproteobacteria (Fig. 1), where mechanisms of Mn(II) oxidation have only recently been investigated (25, 31, 42, 56). Mn(II)-oxidizing bacteria sharing >99% 16S rRNA gene nucleotide sequence with SI85-9A1 are widely distributed in diverse marine environments, from surface waters off the Oregon coast to dorsal hairs of the deep-sea hydrothermal vent tube worm Alvinella pompejana (Fig. 1, SI85-9A1 cluster) (21). Biochemical and genetic evidence suggests that Mn(II) oxidation by two other Alphaproteobacteria, strain SD-21 (25) and Pedomicrobium strain ACS 3067 (42, 56), is catalyzed by a multicopper oxidase (MCO) enzyme as in other Mn(II)-oxidizing bacteria (70). Still, the biochemical mechanism and physiological function of Mn(II) oxidation by Alphaproteobacteria, especially the SI85-9A1 group, remain largely unexplored.
FIG. 1.
Phylogeny of Mn(II)-oxidizing Alphaproteobacteria based on the16S rRNA gene. Mn(II) oxidizers are denoted with “+,” and isolates that have been tested and do not oxidize Mn(II) are denoted with “−.” 16S rRNA gene sequences and Mn(II) oxidation data were compiled from references 21, 25, 31, 42, and 71.
In this study, we present an analysis of the genome sequence of SI85-9A1, the first report of genome-wide insights into Mn(II) oxidation. Though the focus is on Mn(II) oxidation and related processes, we briefly summarize general genome features and overall metabolism in order to place Mn(II) oxidation into the broader context of cellular physiology. In addition to providing insights into physiological, biochemical, evolutionary, and regulatory aspects of Mn(II) oxidation, a prominent finding of this study is that the SI85-9A1 genome harbors the genetic potential to utilize diverse electron donors and carbon sources. Consistent with this view of SI85-9A1 as a metabolic generalist, we present evidence that SI85-9A1 benefits energetically from Mn(II) oxidation and suggest that this strategy might be a subtle yet environmentally relevant mode of metabolism.
MATERIALS AND METHODS
Genome sequencing, annotation, and bioinformatic analysis.
DNA for genome sequencing was extracted with a Qiagen DNeasy tissue kit. Shotgun cloning and sequencing were performed by the J. Craig Venter Institute as part of the Gordon and Betty Moore Foundation Marine Microbial Genome Sequencing Project (https://research.venterinstitute.org/moore/). Automated annotation and complete manual curation of the SI85-9A1 genome were done with the MAGPIE system (29).
DNA binding sites for metal-sensitive transcription regulators Fur (ferric uptake regulator), Mur (manganese uptake regulator), Irr (iron-responsive repressor), RirA (rhizobial iron regulator), Iron-Rhodo, and IscR (iron-sulfur cluster regulator) were predicted using profile hidden Markov models (HMMs), generated using the hmmbuild function of software package HMMER 2.3.2 (24). Input sequences included both experimentally verified and predicted examples specific to Alphaproteobacteria, as described in supplementary Tables 1 to 7 of Rodionov et al. (58). The numbers of sequences used to construct the patterns were as follows: Irr, 221; Fur, 133; Iron-Rhodo, 126; RirA, 117; Mur, 43; IscR-1, 18; Scr-2, 7; and Mnt, 5. Trusted cutoff values were based on scores for experimentally verified examples. Putative cutoff scores were based on interspecies sequence conservation, the homology of downstream regions to genes known to be transcriptionally regulated by metal-sensitive elements, and the proximity of multiple different metal-transcription regulatory binding elements within the same upstream region.
TABLE 1.
General genome features
Parameter | Value |
---|---|
Total no. of protein-coding sequences | 3,653 |
No. (%) of proteins similar to those of | |
known function | 2,804 (77) |
No. (%) of conserved hypothetical proteins | 565 (15) |
No. (%) of hypothetical proteins | 284 (8) |
No. of rRNA operons | 3 |
No. of tRNA genes | 50 |
% GC content | 67 |
Phylogenetic analysis.
moxA homologs were identified with BLAST (minimum score of >300 and E value of <3E−83). Alignments and phylogenetic trees based on 16S rRNA gene and MoxA predicted protein sequences were constructed with a Kimura two-parameter model, using MEGA 3.1 (39). The phylogenetic methods included neighbor joining, parsimony, minimum evolution, and the unweighted-pair group method using average linkages and were tested by bootstrapping (1,000 replications). Gaps and ambiguously aligned regions were not considered.
Growth experiments.
All growth experiments were done with J medium (68) supplemented with either methanol (0.5 to 2.5%, vol/vol), glycerol, succinate, acetate, formate, or glucose (10 mM each). Where indicated, Mn was added as MnCl2 to give a final concentration of 100 μM. Optical density was measured at 600 nm. To avoid interference of Mn oxide, cultures containing Mn were reduced with 1 mM ascorbic acid prior to measurement of optical density. Oxidized Mn was quantified using the leukoberbelin blue (LBB) method (68).
Biochemical analysis.
Cultures for biochemical analysis were grown on either J medium (supplemented with 10 mM succinate or glycerol) or M medium (68). Cultures (500 ml to 1 liter) were pelleted by centrifugation at 10,000 × g, and supernatant (1 to 4 liters) was concentrated by ultrafiltration (50-kDa molecular-mass cutoff; Millipore). Cells were lysed by passage through a French pressure cell four times at 20,000 lb/in2. Mn(II)-oxidizing activity was assayed by the LBB method (68). Sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE; 10%) analysis and the in-gel activity assay (zymogram) were done with concentrated supernatant from stationary-phase cells grown on J-glycerol (without Mn added) as described previously (26). The zymogram was submerged in LBB to identify the presence of a Mn oxide band.
In-gel trypsin digestion and liquid chromatography-MS/MS.
In-gel trypsin digestion of Coomassie and zymogram bands and liquid chromatography-tandem mass spectrometry (MS/MS) were performed as described previously (22). MS/MS spectra were analyzed with Analyst QS 1.1/ProID 1.1 (66) and BioAnalyst 1.1.5/ProBlast 1.1 (60) (Applied Biosystems).
Nucleotide sequence accession number.
Nucleotide sequence and manual annotations have been deposited in GenBank under accession number NZ_AAPJ00000000.
RESULTS AND DISCUSSION
General genome features of SI85-9A1.
Shotgun sequencing of Aurantimonas sp. strain SI85-9A1 genome DNA resulted in 4,325,257 bp of sequence that assembled into one major contiguous sequence and 23 small fragments (41,471 bp total). A combination of automated annotation and extensive manual curation predicted 3,653 protein-coding sequences, the majority of which are most similar (at the protein level, based on BLAST scores) to genes from another recently sequenced marine bacterium, Fulvimarina pelagi (Tables 1 and 2). Three rRNA operons and a complete set of 50 tRNA genes were identified (Table 1). The genome encodes proteins for motility, including 16 predicted chemotaxis proteins and 33 predicted flagellar proteins. Mobile genetic elements are also prevalent; 73 transposons, 9 integrase/recombinases, and 11 phage-related proteins were annotated.
TABLE 2.
Genomes with most top BLAST hits
Organism or result | No. (%) of best hits from SI85-9A1 | Total no. of genes in subject genome |
---|---|---|
Fulvimarina pelagi HTCC2506 | 1,797 (54) | 3,812 |
Mesorhizobium loti MAFF303099 | 158 (5) | 7,352 |
Mesorhizobium sp. strain BNC1 | 117 (4) | 4,686 |
Sinorhizobium meliloti 1021 | 90 (3) | 6,293 |
Sinorhizobium medicae WSM419 | 79 (2) | 6,587 |
Other species | 1,087 (33) | |
No significant BLAST hitsa | 325 (9) |
Significance defined as an E value of <1E−5 plus >60% coverage of the query sequence by the alignment.
Organic carbon metabolism.
Strain SI85-9A1 was isolated as a chemoorganoheterotrophic bacterium capable of oxidizing Mn(II) while growing aerobically on organic carbon. In laboratory culture, it is able to grow on a wide variety of organic carbon compounds, including organic acids (succinate, acetate, and formate), glycerol, and sugars, such as glucose. Its ability to lead an organoheterotrophic lifestyle is reflected in the genome sequence by a large number of high-affinity transporters (ABC type and TRAP [tripartite ATP-independent periplasmic transporter] type) for dicarboxylates, amino acids, peptides, and carbohydrates. An especially abundant transporter found in the SI85-9A1 genome is the predicted TRAP-type C4-dicarboxylate transport system, of which there are 19 copies. All genes required for the Embden-Meyerhof pathway (glycolysis), citric acid cycle, and pentose phosphate cycle are present, accounting for the ability to break down organic substrates and generate central precursor metabolites. Genes for key enzymes of the glyoxylate cycle (isocitrate lyase and malate synthase) were located, providing a mechanism for regenerating oxaloacetate during growth on C2 or C3 compounds.
Electron transport and respiration.
A complete electron transport chain was reconstructed, including complexes I through V; therefore, all machinery for oxidative phosphorylation and aerobic respiration is present. Twenty-three genes were annotated as cytochromes, including 17 c-type cytochromes. Genes for multiple predicted terminal oxidases are present: one cytochrome bd-type quinol oxidase, two cytochrome c oxidases, and a cbb3-type cytochrome c oxidase are each encoded by clusters of three genes. In two other instances, a pair of genes annotated as cytochrome c oxidase subunits I and II are present, but not subunit III. The cbb3-type oxidase, encoded by genes fixN, fixO, and fixP, is predicted to have a high affinity for O2, having been found to have a Km of 7 nM in other rhizobia (54). Expression of these and other genes required for microaerobic processes is presumably mediated by the oxygen-sensitive two-component regulatory system encoded by genes fixL and fixJ (9), which are present at a separate chromosomal location. In N2-fixing rhizobia, the FixL/FixJ system also regulates the expression of genes required for nitrogen fixation, but no nif genes were detected in the genome of SI85-9A1, and this organism is unable to grow without supplemental fixed nitrogen. In the laboratory, SI85-9A1 is typically grown under fully aerobic conditions. Thus, SI85-9A1 appears well equipped to deal with a wide range of redox conditions, from O2 saturated to microaerobic, that might be encountered in its natural habitat at an oxic/anoxic interface. The ability of SI85-9A1 to grow at low O2 tension has potential significance for the biogeochemical cycling of Mn, as was recently demonstrated in the suboxic zone of the Black Sea, where rapid oxidation of Mn takes place at submicromolar O2 levels (14). No evidence of anaerobic respiration was found.
Genetic potential for utilization of inorganic and C1 compounds as electron donors.
In addition to an organotrophic lifestyle, genome analysis revealed that SI85-9A1 encodes the genetic potential for utilization of several inorganic and one-carbon compounds as electron donors (Table 3). The complete suite of genes required for the oxidation of methanol to carbon dioxide is present: methanol dehydrogenase, formaldehyde dehydrogenase, and formate dehydrogenase (Table 3). Putative genes for methanol sensing and regulation were also detected. No methane monooxygenase genes were found, and key genes for the serine and ribulose monophosphate pathways of C1 assimilation (phosphoenolpyruvate carboxylase and 3-hexulose phosphate synthase, respectively) were also absent. SI85-9A1 is able to grow to a limited extent with methanol as the sole energy and carbon source; therefore, carbon assimilation may occur via the energetically inefficient Calvin cycle (for which the genes are present as discussed below), as in some other facultative methylotrophs (18).
TABLE 3.
Genetic potential for metabolic versatility
Process | Protein(s) | GenBank accession no. |
---|---|---|
Putative electron donation | ||
Sulfur oxidation | SoxTRSVWXYZABCDEFGH | ZP_01225759 to ZP_01225774 |
CO oxidation | Aerobic CO dehydrogenase | ZP_01227909 to ZP_01227911, ZP_01228739 |
Methylotrophy | ||
Methanol sensing | MoxY | ZP_01228286 |
Methanol regulation | MoxX | ZP_01228287 |
Methanol oxidation | Methanol dehydrogenase | ZP_01228289 to ZP_01228291, ZP_01228705 |
Formaldehyde oxidation | Formaldehyde dehydrogenase | ZP_01228291, ZP_01228274, ZP_01225718, ZP_01227698 |
Formate oxidation | Formate dehydrogenase | ZP_01228971, ZP_01226368, ZP_01226369, ZP_01226481, ZP_01226482 |
Carbon fixation | ||
Calvin cycle | CbbRFPTALSXE | ZP_01227925 to ZP_01227933 |
Calvin cycle? | RubisCO, large subunit | ZP_01226398 |
Unknown | RubisCO-like protein | ZP_01229072 |
Mn(II) oxidation | MCO (MoxA1) | ZP_01227197 |
MCO (MoxA2) | ZP_01225555 | |
MCO | ZP_01225909 | |
MCO-like protein | ZP_01227202 | |
Extracellular hemolysin-type Ca2+-binding peroxidase | ZP_01225898 | |
Type II secretion | ZP_01225900 to ZP_01225907 | |
PQQ biosynthesis | ZP_01226711 to ZP_01226713 |
The SI85-9A1 genome contains several genes that were initially annotated as encoding the large subunit (CoxL) of carbon monoxide dehydrogenase (Table 3), the enzyme responsible for oxidizing CO to CO2 in carboxydotrophic bacteria (37). Phylogenetic analysis of coxL showed that one of these genes clusters strongly with form II, another falls between form I and form II, and two others are only distantly related to CO dehydrogenase and are thus likely molybdenum hydroxylases with specificity for substrates other than CO (see Fig. S1 in the supplemental material). The form II coxL gene occurs in an operon along with genes for the small (coxS) and medium (coxM) subunits in an arrangement (coxSLM) that is common for form II. As in other genomes containing form II coxL, accessory genes (coxBCDEFGHI) are not present in this operon but homologs are found scattered throughout the genome (37). Although there is evidence that form II coxL encodes a functional CO dehydrogenase enzyme, the substrate specificity and function of these genes remain unresolved (37). The second coxL gene (GenBank accession no. ZP_01228739), which falls phylogenetically between forms I and II, is present at a separate chromosomal location and without accompanying coxM and comS genes; thus, its function is unknown.
Another potential source of inorganic energy revealed through genomic analysis is reduced sulfur. The complete set of genes for sulfur oxidation is present in an arrangement (soxTRSVWXYZABCDEFGH) identical to that found in the model facultative sulfur oxidizer Paracoccus pantotrophus (28). These genes are a faithful genetic marker of the ability of bacteria to oxidize sulfur (28); thus, their presence implies that under some conditions SI85-9A1 carries out this process. Utilization of sulfur compounds could potentially account for a substantial fraction of SI85-9A1's energy generation in its natural habitat, an oxic/anoxic interface where reduced sulfur species are abundant. Attempts to grow strain SI85-9A1 autotrophically with CO or thiosulfate as the sole electron donor have been unsuccessful so far; therefore, further physiological and biochemical work is required to determine the significance of the sox and cox genes that we report here. One possibility is that SI85-9A1 utilizes CO and sulfur as energy supplements during heterotrophic growth, as has been recently shown to occur in other marine Alphaproteobacteria (48, 64).
Autotrophy.
The complete Calvin-Benson-Bassham cycle for carbon fixation is carried in an operon of genes in the order cbbRFPTALSXE (Table 3). This includes genes for the key CO2-fixing enzyme ribulose-1,5-bisphosphate carboxylase oxygenase (RubisCO, encoded by cbbL and cbbS) as well as genes for regeneration of the CO2 acceptor ribulose 1,5-bisphosphate: fructose-bisphosphate phosphatase (cbbF) and phosphoribulokinase (cbbP). The pentose 5-phosphate and gluconeogenesis pathways are present, allowing for the interconversion of sugar phosphates and synthesis of glucose, respectively. The presence of a gene encoding the regulator CbbR is consistent with tight control of the cbb operon, as in other facultative autotrophs that are metabolically versatile (40). The cbbL and cbbS genes were cloned and sequenced from SI85-9A1 previously and found to encode a functional form I, type C/D RubisCO protein when expressed in E. coli (12). However, no RubisCO enzyme activity has been detected in cultures of SI85-9A1 (12), and efforts to grow SI85-9A1 autotrophically on Mn(II), thiosulfate, or carbon monoxide have been unsuccessful so far. Nevertheless, the presence of the complete cbb operon as described here suggests that these RubisCO genes are involved in carbon fixation and are not relics of an autotrophic descendant, a possibility that was surmised previously (12). As discussed earlier (utilization of C1 compounds), the Calvin-Benson-Bassham cycle could be active in carbon fixation during growth on methanol, but further experimental work is required to investigate this and other possible roles for the cbb genes. A second copy of cbbL (of unknown function) is also present, as is a predicted RubisCO-like protein (form IV) which does not function in carbon fixation but rather is thought to be involved in either sulfur metabolism, defense against reactive oxygen species, or biosynthesis (4, 32, 44).
Mn(II) oxidation and effect of Mn(II) on growth.
Most Mn(II)-oxidizing bacteria that have been studied to date oxidize Mn(II) during late-exponential or stationary phase or upon sporulation (70). In contrast, strain SI85-9A1 oxidizes Mn(II) at an early stage of growth (Fig. 2), similar to Pedomicrobium sp. strain ACM 3067 (42). Mn(II) oxidation occurs during growth on organic acids (formate, succinate, and acetate) and glycerol but not during growth on glucose, despite the fact that growth is fastest on that substrate. Growth on glycerol is extremely slow but is dramatically increased upon addition of MnCl2 (Fig. 2). A stimulation of growth by Mn(II) has also been observed in the Mn(II)-oxidizing alphaproteobacterium Erythrobacter sp. strain SD-21, but in contrast to what was found for SI85-9A1, the increase in growth was slight and occurred only at the onset of stationary phase (25). Mn is a cofactor in many enzymes and also plays a prominent biological role in protecting cells from reactive oxygen species; thus, Mn may be a growth-limiting micronutrient under certain conditions (1, 15-17, 33, 35). However, these are unlikely explanations for the Mn-stimulated growth of SI85-9A1 that we observe here. The fact that Mn(II) stimulates SI85-9A1 only during growth on glycerol, where SI85-9A1 may be energy limited, is consistent with conditions for chemolithoheterotrophy, in which inorganic compounds serve as sources of supplemental energy, allowing greater heterotrophic efficiency (3, 38, 48, 64). Mn(II) oxidation by O2 is an energy-yielding reaction and could be beneficial as an energy source. Though autotrophic growth on Mn(II) has not been detected, Mn(II) oxidation could benefit the cell as an energy supplement by generating ATP or by pumping ions for gradient-driven processes, such as high-affinity transport or motility. During growth on glycerol, such a role for Mn(II) oxidation can be envisioned because ATP is required by glycerol kinase, which catalyzes the first step of glycerol utilization. Mn(II)-derived electrons could enter the electron transport chain and drive a proton gradient, consistent with cytochromes being required for Mn(II) oxidation by several Mn(II)-oxidizing species (13, 67-70). This hypothesis is supported by the presence of c-type cytochromes in close proximity to both copies of the putative Mn(II) oxidase (see below). Further physiology experiments are under way to investigate the nature of the stimulation of growth by Mn and to determine whether energy is derived from Mn(II) oxidation by strain SI85-9A1.
FIG. 2.
(A) Growth of SI85-9A1 on glycerol with 100 μM MnCl2 (closed circles), without added Mn (open circles), and with 100 μM MnCl2 added to replicates of the no-Mn-added culture in the middle of the growth curve (closed triangles). Growth on glucose is much faster and is not stimulated by Mn(II) (data not shown; cultures reach optical densities of ∼0.1 by 200 h and ∼0.8 by 600 h). (B) Mn oxide formation by the glycerol plus MnCl2 culture shown in panel A. Error bars represent standard deviations for triplicate cultures.
Mechanism of Mn oxidation.
The majority of Mn(II)-oxidizing activity was recovered from growth medium supernatant of pelleted cultures rather than from whole cells or crude cell extracts, indicating that the Mn(II)-oxidizing enzyme is exported across the outer membrane or loosely associated with the outer membrane. SDS-PAGE analysis of concentrated cell-free growth media revealed seven distinct Coomassie-stainable bands in this extracellular fraction (Fig. 3). Six bands were unambiguously identified by mass spectrometry, whereas a seventh band contained peptides from two different proteins. Peptides from five bands (A to E) all belong to one large (predicted 350-kDa) protein that has hemolysin-type calcium-binding region signatures (Table 3) and belongs to the animal heme peroxidase superfamily (Pfam accession no. PF03098, PROSITE accession no. PDOC00394). While the role of this peroxidase is unknown, an intriguing possibility is that it may function in extracellular oxidation reactions that are related to Mn(II) oxidation. In fungi, Mn(II) serves as the reducing substrate for Mn peroxidase, which oxidizes Mn(II) to Mn(III) in the presence of organic chelators (75). Another possibility is cooperation between a Mn(II) oxidase and peroxidase, as previously reported for a litter-decaying basidiomycete: the product of Mn(II) oxidation, Mn(III), abiotically generates H2O2, which then serves as a substrate for Mn peroxidase in the biodegradation of lignin and xenobiotics (59). The cooccurrence of a Mn(II) oxidase (see below) and a peroxidase in the extracellular fraction of SI85-9A1 cultures suggests that a similar process may be at work. Although Mn peroxidase is best known to occur in fungi, it has also been reported to occur in bacteria (45). Two other bands in the extracellular fraction seem unrelated to Mn(II) oxidation. One band (F) was identified as a putative periplasmic substrate-binding protein from an ABC-type transporter (GenBank accession no. ZP_01228804), and another (G) contained peptides from two proteins, the putative periplasmic substrate-binding protein and a hypothetical protein (GenBank accession no. ZP_01228927).
FIG. 3.
SDS-PAGE analysis of the SI85-9A1 extracellular fraction during growth on glycerol. The gel was cut and one-half stained with Coomassie (left) and one-half screened with an in-gel Mn(II) oxidation activity assay (right). The latter was then immersed in LBB, which reacts specifically with Mn oxide to produce a cobalt blue color (H and I).
SDS-PAGE gels of the extracellular protein fraction were also screened with an in-gel activity assay (zymogram) for Mn oxidation (26), revealing one gray Mn oxide band. The composition of this band was confirmed to be Mn oxide by immersing the gel in LBB, a colorimetric indicator that reacts specifically with oxidized Mn to produce a cobalt blue color (Fig. 3) (68). This in-gel Mn oxide formation indicates a Mn(II)-oxidizing enzyme with an apparent molecular mass of ∼50 kDa. The gray color is unusual as all other Mn oxide bands identified by zymogram to date are brown or orange (26); this unique color may indicate that the structure or particle size of the primary biogenic Mn oxide produced by SI85-9A1 is distinct from those of the better-studied orange/brown Mn oxides produced by Bacillus spores (5, 77). A second, light, LBB-positive band was apparent at >250 kDa, indicating the presence of oxidized Mn in the gel at that location as well. Since no Mn oxide band was visible at that spot prior to LBB staining, it is unclear whether this LBB band is indicative of a small quantity of Mn oxide or the presence of oxidized Mn(III) or -(IV) in some other state (e.g., bound to a protein). No peptides were recovered from either LBB-positive band; therefore, their identities are uncertain. These results are consistent with a Mn(II) oxidase being present at a very low abundance despite high Mn(II)-oxidizing activity, a characteristic observed in other Mn(II)-oxidizing bacteria (22). We are unable to discern whether the LBB-positive bands correspond to any of the Coomassie bands, because the Coomassie-stained samples shown in Fig. 3 were boiled prior to SDS-PAGE (boiling was required to get well-defined bands), but samples for the zymogram were not boiled (because boiling eliminated activity) and therefore are expected to migrate differently during electrophoresis.
All Mn(II)-oxidizing bacteria studied to date require MCO genes for Mn oxidation (70), and the MCO MnxG was recently demonstrated to be the direct catalyst of Mn(II) oxidation by spores of a marine Bacillus species (22). MCOs utilize Cu as a cofactor in coupling four one-electron substrate oxidations to the four-electron reduction of O2 to H2O (63). MCOs are a large family of enzymes with high sequence divergence; however, the amino acids involved in coordinating Cu ions are highly conserved and easily recognizable. The SI85-9A1 genome contains three genes coding for proteins that contain the four Cu-binding amino acid motifs indicative of MCOs (HXH, HXH, HXXHXH, and HCHXXXH) (63), and a fourth gene encodes an MCO-like protein with three of the four MCO motifs (missing HXXHXH) (see Table 3 for GenBank accession numbers). Two of the MCOs are nearly identical to each other (95% at the amino acid [aa] level) and show significant similarity (65% aa identity) to the MoxA protein, an MCO that was found to be essential for Mn(II) oxidation in Pedomicrobium sp. strain ACM 3067 (56). The predicted 51-kDa sizes of the SI85-9A1 MoxA homologs (referred to hereafter as MoxA1 and MoxA2 or collectively as MoxA1/2) match the size of the Mn(II)-oxidizing enzyme identified by the Mn(II) oxidation zymogram (Fig. 3). Based on their similarity to MoxA from Pedomicrobium and the fact that they are predicted to be the same size as the Mn(II) oxidase, we infer that MoxA1/2 are the Mn(II)-oxidizing enzymes. In addition to being required for Mn(II) oxidation, moxA is required for the oxidation of the laccase substrate 2,2′-azino-bis(3-ethylbenzthiazonline-6-sulfonic acid) (ABTS) (56). Therefore, we suspect that the putative Mn(II) oxidase(s) catalyzes the laccase-like oxidation of Mn(II) to Mn(III), but the function of the duplicate copies and their role in the oxidation of Mn(III) to Mn(IV) remain unexplained. MoxA1/2 each contain two methionine-rich regions following two of the Cu-binding regions. Methionine-rich regions have been hypothesized to play a role in binding extra Cu ions (46) that are thought to play a regulatory role in the E. coli MCO CueO (57).
At their N termini, MoxA1/2 have twin arginine signal peptides characteristic of the TAT secretory pathway consensus sequence (8). Whereas the TAT system targets fully folded proteins to the periplasm, it has been shown that proteins transported to the periplasm by the TAT system can be recognized and subsequently exported across the outer membrane by the type II protein secretion pathway (74), as would be expected for extracellular Mn(II)-oxidizing activity. Indeed, studies of Pseudomonas putida strain GB-1 have demonstrated the requirement for the type II secretion system in the transport of a Mn(II)-oxidizing enzyme, an MCO with a TAT leader sequence, across the outer membrane (10, 19). An operon encoding homologs of type II protein secretion machinery is present in SI85-9A1 (Table 3). Similar to the P. putida region described in the above-mentioned study, the SI85-9A1 operon is flanked by genes that are potentially involved in Mn(II) oxidation. At one end, after a transposon, is the gene for the hemolysin-type Ca2+-binding peroxidase identified by MS/MS. At the other end of the operon lies a gene for an MCO (GenBank accession no. ZP_01225909) and a gene (GenBank accession no. ZP_01225908) from the Sco1/SenC family of Cu chaperones that has been associated with Mn(II)-oxidizing gene regions (19, 73). The MCO in this region is most closely related to genes found in the genomes of the Mn(II)-oxidizing Pseudomonas putida strains GB-1 and KT2440. Although this MCO has not been experimentally implicated in Mn(II) oxidation, its genomic context and similarity to genes from distantly related Mn(II) oxidizers make it very interesting in this regard. The discovery of multiple MCOs in the SI85-9A1 genome, including two variants of the putative Mn(II) oxidase (MoxA1/2), highlights the need for a better understanding of the exact roles of these enzymes in the biochemical mechanism of Mn(II) oxidation.
Homologs of MoxA are found in many Alphaproteobacteria genomes, but experimental data on the function of these genes are available for only a few distantly related MCOs (Table 4). The closest relative of MoxA (60% aa identity) is a protein (Orf4) that was recently discovered based on its involvement in Cu resistance in the plant pathogen Xanthomonas campestris pv. vesicatoria (6). The orf4 gene is induced by Cu and is carried on the chromosome in an operon of Cu resistance genes that also share similarity with MoxA neighbors (further discussed below). Other MoxA1/2 homologs that have been experimentally associated with a function are more distantly related (Table 4). Typically, they are involved in Cu resistance, although as pointed out by Huston et al. (34), in many cases the resistance conferred is only marginal. This invites speculation that the Cu-sensitive phenotype is due to indirect effects and that the MCO may in fact have other physiological functions. Indeed, these enzymes often exhibit broad specificity, oxidizing substrates such as Fe (34), Cu (62), and organic compounds, including siderophores (30). Therefore, it has been difficult to discern whether phenotypes of MCO mutants are due to a direct role in Cu homeostasis or to loss of some other function, such as iron uptake (as demonstrated by reference 34) or siderophore oxidation.
TABLE 4.
Most closely related homologs of MoxA for which there are experimental data available
Protein | GenBank accession no. | Organism | % Identitya | Function | Source or reference |
---|---|---|---|---|---|
MoxA1 | ZP_01227197 | Aurantimonas strain SI85-9A1 | 100 | Mn oxidation | This study |
MoxA2 | ZP_01225555 | Aurantimonas strain SI85-9A1 | 98 | Mn oxidation | This study |
MoxA | CAJ19378 | Pedomicrobium sp. strain ACM 3067 | 65 | Mn oxidation | 56 |
Orf4 | AAP42069 | Xanthomonas campestris pv. Vesicatoria | 60 | Cu resistance | 6 |
PcoA | Q47452 | E. coli | 24 | Cu resistance | 11 |
Pmco | AAN52530 | Pseudomonas aeruginosa | 24 | Fe(II) uptake | 34 |
Orf1 | AAA72013 | Xanthomonas campestris pv. juglandis | 23 | Cu resistance | 43 |
CueO | P36649 | E. coli | 23 | Cu resistance | 62 |
CopA | P12374 | Pseudomonas syringae | 23 | Cu resistance | 46 |
CopA | AAF32269 | Aeromonas veronii bv. sobria | 23 | Slightly increased Cu tolerance | 27 |
Percent protein sequence identity to MoxA1.
Another area of interest with regard to Mn(II) oxidation is an operon of three genes for the biosynthesis of pyrroloquinoline quinone (PQQ), a cofactor traditionally associated with alcohol and amine dehydrogenases (2) (Table 3). This quinone has recently been found to play a role in Mn(II) oxidation by the marine alphaproteobacterium Erythrobacter sp. strain SD-21 (36), but the involvement of PQQ in Mn(II) oxidation by SI85-9A1 has not yet been investigated.
mox gene context and duplication.
moxA1 and moxA2 occur at two separate chromosomal sites in clusters of homologous genes (Fig. 4). In both clusters, upstream of moxA there are genes coding for predicted proteins that are similar to MoxB (40% aa identity), also found upstream of moxA in Pedomicrobium sp. strain ACM 3067 (56). MoxB shows some similarity to the TolC family of proteins that are involved in type I secretion, and MoxB has been suggested to be involved in transport of the Mn(II) oxidase (56). However, the TolC system is also involved in the efflux of many types of molecules, including AQDS (anthraquinone-2,6-disulfonate), antibiotics, detergents, dyes, and phenazines (reference 61 and references therein). Further, SI85-9A1's MoxB protein also shares 31% aa identity with Orf3 from Xanthomonas campestris pv. vesicatoria, a protein thought to be involved in Cu resistance and to be induced by low levels of Cu (6); therefore, a number of physiological roles for MoxB seem feasible. Downstream of moxA is a gene encoding a small predicted protein (∼18 kDa) with similarity to COG4454, an uncharacterized Cu-binding protein. This protein is similar (47% aa identity) to Orf5 of Xanthomonas campestris pv. vesicatoria, also thought to play a role in Cu resistance (6). The cooccurrence of moxA, moxB, and the Cu-binding-protein-encoding gene in close proximity to each other (moxA and moxB overlap by 3 bp, whereas the Cu-binding protein is 46 bp downstream in both gene clusters) in multiple species suggests that these genes are functionally related. The location of the moxA gene adjacent to genes that appear to be involved in Cu resistance may indicate that this putative Mn(II) oxidase also plays a role in Cu resistance. Alternatively, linkage of the MCO and the Cu homeostasis genes could merely arise from the MCO's requirement for Cu as a cofactor since these Cu resistance genes could actually be involved in Cu acquisition or sequestration.
FIG. 4.
Duplicated regions surrounding the mox genes; shown are the Mox-1 region (top) and the Mox-2 region (bottom). Predicted open reading frames are represented by arrows. Percentages indicate identity of predicted protein sequence between duplicated genes.
The duplicated mox genes are part of larger duplicate regions (10.6 and 19.1 kb) containing genes that share significant predicted protein sequence with each other (73 to 98%) (Fig. 4). The duplicated regions share high sequence similarity, even in intergenic regions, and the Mox-1 region is flanked by transposons, suggesting that it was recently duplicated from Mox-2. Among the duplicated genes are several hypothetical and conserved hypothetical proteins as well as a c-type cytochrome. Cytochromes are required for Mn(II) oxidation in several Mn(II)-oxidizing bacteria (70), and it is tempting to speculate that the genetic linkage of a c-type cytochrome to the Mn(II)-oxidizing system reflects linkage of Mn(II)-derived electrons to the electron transport chain, as discussed above. There are also differences in gene content between the two duplicated regions, including some genes that appear to be related to Mn(II) oxidation and/or metal homeostasis (see Fig. 4 for accession numbers). In the Mox-1 region, there is an MCO-like protein that has some sequence similarity to MoxA but lacks one of the four Cu-binding regions. In the Mox-2 region upstream of moxA, there are nine nonduplicated genes, including a permease of the major facilitator family predicted to be a nickel resistance protein. Here, there is also a putative sensory histidine protein kinase and a two-component response regulator that show some limited similarity to the CopR/PcoR and CopS/PcoS proteins, respectively, which are involved in regulating Cu resistance systems (47, 49). Genes involved in metal resistance are also present near the Mox-1 region; less than 3 kb from the region shown in Fig. 4, there is a putative heavy metal transcriptional regulator, as well as a mercury transport protein (MerT) and a mercury reductase (MerA) (GenBank accession no. ZP_01227189 to ZP_01227191).
Distribution and evolutionary history of moxA genes.
A survey of completed and ongoing microbial sequencing genome projects revealed that moxA-like genes are widespread throughout the Proteobacteria, including the Alpha- (17/86 genomes), Beta- (21/53 genomes), Gamma- (1/159 genomes), and Deltaproteobacteria (2/19 genomes) subdivisions. Phylogenetic analysis of moxA and 16S rRNA gene sequences revealed stark incongruities between these two genes, indicating that moxA genes have been horizontally transferred in several cases (Fig. 5). The most notable examples are the Gammaproteobacteria Xanthomonas campestris pv. vesicatoria and Pseudomonas mendocina, whose moxA genes clearly cluster with the Betaproteobacteria, and the alphaproteobacterium Mariaculis maris, which has a moxA gene that is decidedly not of the Alphaproteobacteria type. This evidence for horizontal gene transfer is firm based on high bootstrap values that support the phylogeny (Fig. 5). In contrast, phylogenetic results for the clade of Alphaproteobacteria containing SI85-9A1 show that there are no prevalent incongruities between moxA and 16S rRNA genes, suggesting that moxA has evolved vertically in SI85-9A1 and close relatives for which genome sequences are currently available (Fig. 5). The program DarkHorse, a tool for surveying genomes for recently acquired genes (53), was used to analyze the SI85-9A1 genome. Results indicate that the number of genes in SI85-9A1 acquired through lateral transfer is relatively low, and scores for the mox genes were consistent with the genes having not been recently acquired from a phylogenetically distant source (see Fig. S2 in the supplemental material). Finally, percent G+C content and Karlin signatures of the mox regions are indistinguishable from the characteristic signatures of the overall SI85-9A1 genome, further supporting the notion that these regions have not been recently acquired. In organisms that possess multiple copies of the moxA gene, the two copies often cluster together (e.g., SI85-9A1), suggesting relatively recent duplication (Fig. 5B), though in a few cases, copies of moxA within a genome are very divergent (e.g., Myxococcus xanthus). The distribution of moxA-like genes is extremely scattered; in genera and species for which multiple genome sequences are available, such as Burkholderia or Rhodopseudomonas palustris, moxA is often found in some genomes but not others. Overall, these results suggest a complex evolutionary history of moxA, with numerous gene acquisition, loss, and duplication events. If moxA is indeed a genetic marker for the ability to oxidize Mn(II), this spotty distribution could explain the polyphyletic nature of Mn(II)-oxidizing bacteria (Fig. 1) (67, 68, 70).
FIG. 5.
Neighbor-joining phylogenetic trees based on 16S rRNA gene (A) and predicted MoxA protein sequences (B). Bootstrap values are the result of 1,000 replicates. Similar tree topologies resulted from all phylogenetic methods tested, including parsimony, minimum evolution, and the unweighted-pair group method using average linkages. In panel A, Burkholderia pseudomallei includes strains 1106b, 1710b, and K96243. In panel B, MoxA sequences with phylogenies apparently different from those of the 16S rRNA gene from that organism are indicated with symbols representing their 16S rRNA lineages: α, Alphaproteobacteria; γ, Gammaproteobacteria.
Metal homeostasis.
The SI85-9A1 genome sequence presents an opportunity to better understand how this organism manages the uptake, storage, and availability of Mn, Fe, and other metals. Motivation for placing Mn(II) oxidation into the broader context of cellular metal homeostasis derives from several areas of recent research. First, the putative Mn(II) oxidase is an MCO, a family of enzymes known to be involved in Fe (34) and Cu (55, 62) homeostasis and siderophore degradation (30). Second, Mn(III), an intermediate of Mn(II) oxidation (76), is bound by some siderophores with even greater affinity than their intended target, Fe(III); thus, Mn(II) oxidation may influence Fe bioavailability (23, 51). Conversely, the formation of Mn oxides is inhibited by siderophores and thus depends on Fe bioavailability (50). Mn(II) oxidation also appears to be regulated in some cases by the concentrations of other metals, such as Zn and Pb (R. Verity and B. M. Tebo, unpublished).
SI85-9A1 has genes coding for high-affinity, siderophore-mediated ferric iron uptake systems. There are three siderophore receptors, three ABC-type siderophore transporters, and a four-gene cluster encoding siderophore biosynthesis proteins. The siderophore biosynthesis genes are most similar to those of Rhodopseudomonas palustris and are predicted to encode a rhizobactin-like siderophore (41). It will be interesting to determine whether this siderophore has a high affinity for Mn(III) as in other Mn(II)-oxidizing bacteria (23, 51).
The SI85-9A1 genome contains three genes of the ferric uptake regulator (Fur) family. One of these (GenBank accession no. ZP_01228946) is most similar to Fur homologs recently found to function in Mn uptake regulation (Mur) rather than Fe uptake regulation in Alphaproteobacteria (7, 20, 52). The major targets of this regulator, the sitABCD genes, encode a Mn2+-specific ABC-type transporter present in the SI85-9A1 genome (GenBank accession no. ZP_01226419 to ZP_01226422) and recently shown to be required for protection against oxidative stress (17). A second Fur family protein (GenBank accession no. ZP_01225776) is a putative Zn uptake regulator (Zur) that occurs immediately upstream of a putative ABC-type Zn transporter system, and the third Fur family protein (GenBank accession no. ZP_01228417) clusters phylogenetically with iron response regulator (Irr) proteins that are involved in heme biosynthesis (52). SI85-9A1 also has two RirA-like proteins, additional Fe-responsive regulators that do not have any sequence similarity to Fur (72).
Robust methods for computationally identifying trace metal ion-sensitive transcription factor binding sites have recently been developed (58). Using consensus binding sequences assembled by Rodionov et al. (58), we developed an HMM to search for binding sites for transcriptional regulators Fur, Mur, Irr, Mnt, RirA, Iron-Rhodo, and IscR. Thirty-nine putative targets were identified, the majority of which have functions related to metal metabolism or are of unknown function (see Table S1 in the supplemental material), supporting the accuracy of the HMM model. Although regulation of the targets identified in the genome-wide bioinformatic search was not verified experimentally for SI85-9A1, metal-dependent regulation of homologs of many of these targets has been experimentally verified for closely related organisms (reference 58 and references therein). Among the Mur targets identified were MUR itself (GenBank accession no. ZP_01228946) and the Mn2+-specific ABC-type transporter (GenBank accession no. ZP_01226419 to ZP_01226422). RirA-binding sites were detected upstream of one of the CopA-type ATPases adjacent to the Mox region (GenBank accession no. ZP_01227209) and upstream of the extracellular hemolysin-type Ca2+-binding peroxidase discussed earlier. Notably, the putative Mn(II) oxidase (mox) genes were not among the targets predicted by our computational search of the SI85-9A1 genome. This suggests that expression of the Mn(II) oxidase is not regulated by Fe or Mn concentration, consistent with our finding that Mn(II)-oxidizing activity does not depend on the presence of added Mn(II).
Overall, the regulatory players of metal homeostasis in this marine Mn(II) oxidizer appear to be similar to those in its terrestrial rhizobial relatives Rhizobium leguminosarum (7, 20) and Sinorhizobium meliloti (52), for which the view of metal regulation is dynamic but clearly distinct from that in the better-known Escherichia coli and Pseudomonas aeruginosa systems. These N2-fixing rhizobia require large amounts of Fe to satisfy the demands of nitrogenase; although SI85-9A1 does not have nitrogenase, apparently it retains similar mechanisms for acquiring and regulating trace metals.
Conclusions.
The genome sequence of the alphaproteobacterium strain SI85-9A1 provides novel insights into bacterial Mn(II) oxidation and the metabolic and physiological adaptations of this organism to life in a marine oxic/anoxic interface. Previously unrecognized genetic potential for the oxidation of carbon monoxide and sulfur was revealed; along with Mn(II), these compounds represent putative sources of electrons for energy generation. Genetic markers for utilization of O2 at submicromolar concentrations suggest an ability to access such reduced compounds under redox conditions found at the oxic/anoxic interface where SI85-9A1 was isolated. Inorganic compounds, such as Mn(II), reduced sulfur species, and carbon monoxide, may provide SI85-9A1 with an energy supplement, allowing greater heterotrophic efficiency (“chemolithoheterotrophy”), as suggested for CO and sulfur in another marine alphaproteobacterium, Silicibacter pomeroyi (48). An additional twist on this theme is that SI85-9A1 appears, based on genome sequence, to be capable of carbon fixation via the Calvin cycle, though the electron donor and the conditions under which this occurs remain to be determined. To our knowledge, the genomic evidence of sulfur oxidation presented here is the first reported link of this ability to a Mn(II)-oxidizing bacterium. This raises some intriguing microbial biogeochemistry questions; reduced sulfur species may select for or stimulate the activities of such organisms and therefore stimulate Mn(II) oxidation rates at oxic/anoxic interfaces where Mn cycling is prevalent. Further experimental research is required to test these genome-generated hypotheses.
Two nearly identical copies of an MCO gene that putatively encodes a Mn(II) oxidase were identified. moxA appears to represent a new family of MCOs (56) that are widespread in isolates from diverse environments, suggesting that these genes serve important physiological and biogeochemical functions and underscoring the need for a better understanding of their function. The implication of moxA in Mn(II) oxidation by two phylogenetically diverse Alphaproteobacteria, SI85-9A1 and Pedomicrobium strain ACS 3067, may indicate that the MoxA-like family of enzymes are broadly capable of Mn(II) oxidation. Determination of the specificity and function of this family of enzymes requires further investigation, but an intriguing possibility is that Mn(II) oxidation is a more common trait among bacteria than is currently recognized. Overall, this study indicates that SI85-9A1 offers attractive opportunities as a model organism for furthering understanding of the physiology and biochemical mechanism of bacterial Mn(II) oxidation. In addition to the insights presented here, the genome sequence enables functional genomic approaches, such as microarrays and proteomics, that promise to address many of the hypotheses generated by this study.
Supplementary Material
Acknowledgments
We thank the Gordon and Betty Moore Foundation and the J. Craig Venter Institute for funding and genome sequencing via the Marine Microbial Genome Sequencing program.
This work was supported by awards to B.M.T. from the Superfund Basic Research Program (NIEHS grant ES10337 to UCSD) and the NSF (OCE-0352081/0635493 and MCB-0422232/0630355). G.J.D. was supported by an NSF Graduate Research Fellowship.
Footnotes
Published ahead of print on 14 March 2008.
Supplemental material for this article may be found at http://aem.asm.org/.
REFERENCES
- 1.Al-Maghrebi, M., I. Fridovich, and L. Benov. 2002. Manganese supplementation relieves the phenotypic deficits seen in superoxide-dismutase-null Escherichia coli. Arch. Biochem. Biophys. 402:104-109. [DOI] [PubMed] [Google Scholar]
- 2.Anthony, C. A. 1996. Quinoprotein-catalysed reactions. Biochem. J. 320:697-711. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Arp, D. J., P. S. G. Chain, and M. G. Klotz. 2007. The impact of genome analyses on our understanding of ammonia-oxidizing bacteria. Annu. Rev. Microbiol. 61:503-528. [DOI] [PubMed] [Google Scholar]
- 4.Ashida, H., A. Danchin, and A. Yokota. 2005. Was photosynthetic RuBisCO recruited by acquisitive evolution from RuBisCO-like proteins involved in sulfur metabolism? Res. Microbiol. 156:611-618. [DOI] [PubMed] [Google Scholar]
- 5.Bargar, J. R., B. M. Tebo, U. Bergmann, S. M. Webb, P. Glatzel, V. Q. Chiu, and M. Villalobos. 2005. Biotic and abiotic products of Mn(II) oxidation by spores of the marine Bacillus sp. strain SG-1. Am. Mineral. 90:143-154. [Google Scholar]
- 6.Basim, H., G. V. Minsavage, R. E. Stall, J. Wang, S. Shanker, and J. B. Jones. 2005. Characterization of a unique chromosomal copper resistance gene cluster from Xanthomonas campestris pv. vesicatoria. Appl. Environ. Microbiol. 71:8284-8291. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Bellini, P., and A. M. Hemmings. 2006. In vitro characterization of a bacterial manganese uptake regulator of the Fur superfamily. Biochemistry 45:2686-2698. [DOI] [PubMed] [Google Scholar]
- 8.Berks, B. C., F. Sargent, and T. Palmer. 2000. The Tat protein export pathway. Mol. Microbiol. 35:260-274. [DOI] [PubMed] [Google Scholar]
- 9.Bobik, C., E. Meilhoc, and J. Batut. 2006. FixJ: a major regulator of the oxygen limitation response and late symbiotic functions of Sinorhizobium meliloti. J. Bacteriol. 188:4890-4902. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Brouwers, G. J., E. W. de Vrind-De Jong, P. L. A. M. Corstjens, and E. W. V. Jong. 1998. Involvement of genes of the two-step protein secretion pathway in the transport of the manganese-oxidizing factor across the outer membrane of Pseudomonas putida strain GB-I. Am. Mineral. 83:1573-1582. [Google Scholar]
- 11.Brown, N. L., S. R. Barret, J. Camakaris, B. T. O. Lee, and D. A. Rouch. 1995. Molecular genetics and transport analysis of the copper-resistant determinant (pco) from Escherichia coli plasmid pRJ1004. Mol. Microbiol. 17:1153-1166. [DOI] [PubMed] [Google Scholar]
- 12.Caspi, R., M. G. Haygood, and B. M. Tebo. 1996. Unusual ribulose-1,5-bisphosphate carboxylase/oxygenase genes from a marine manganese-oxidizing bacterium. Microbiology 142:2549-2559. [DOI] [PubMed] [Google Scholar]
- 13.Caspi, R., B. M. Tebo, and M. G. Haygood. 1998. c-type cytochromes and manganese oxidation in Pseudomonas putida strain MnB1. Appl. Environ. Microbiol. 64:3549-3555. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Clement, B. G. 2006. Microbial Mn(II) oxidation. Ph.D. dissertation. University of California, San Diego, La Jolla.
- 15.Daly, M. J., E. K. Gaidamakova, V. Y. Matrosova, A. Vasilenko, M. Zhai, R. D. Leapman, B. Lai, B. Ravel, S. W. Li, K. M. Kemner, and J. K. Fredrickson. 2007. Protein oxidation implicated as the primary determinant of bacterial radioresistance. PLoS Biol. 5:e92. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Daly, M. J., E. K. Gaidamakova, V. Y. Matrosova, A. Vasilenko, M. Zhai, A. Venkateswaran, M. Hess, M. V. Omelchenko, H. M. Kostrandarithes, K. S. Makarova, L. P. Wackett, J. K. Fredrickson, and D. Ghosal. 2004. Accumulation of Mn(II) in Deinococcus radiodurans facilitates gamma-radiation resistance. Science 306:1025-1028. [DOI] [PubMed] [Google Scholar]
- 17.Davies, B. W., and G. C. Walker. 2007. Disruption of sitA compromises Sinorhizobium meliloti for manganese uptake required for protection against oxidative stress. J. Bacteriol. 189:2101-2109. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Dedysh, S. N., K. V. Smirnova, V. N. Khmelenina, N. E. Suzina, W. Liesack, and Y. A. Trotsenko. 2005. Methylotrophic autotrophy in Beijerinckia mobilis. J. Bacteriol. 187:3884-3888. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.de Vrind, J., A. de Groot, G. J. Brouwers, J. Tommassen, and E. de Vrind-de Jong. 2003. Identification of a novel Gsp-related pathway required for secretion of the manganese-oxidizing factor of Pseudomonas putida strain GB-1. Mol. Microbiol. 47:993-1006. [DOI] [PubMed] [Google Scholar]
- 20.Diaz-Mireles, E., M. Wexler, J. D. Todd, D. Bellini, A. W. B. Johnston, and R. G. Sawers. 2005. The manganese-responsive repressor Mur of Rhizobium leguminosarum is a member of the Fur-superfamily that recognizes an unusual operator sequence. Microbiology 151:4071-4078. [DOI] [PubMed] [Google Scholar]
- 21.Dick, G. J. 2006. Microbial manganese(II) oxidation: biogeochemistry of a deep-sea hydrothermal plume, enzymatic mechanism, and genomic perspectives. Ph.D. dissertation. University of California, San Diego, La Jolla.
- 22.Dick, G. J., J. W. Torpey, T. J. Beveridge, and B. M. Tebo. 2008. Direct identification of a bacterial manganese(II) oxidase, the multicopper oxidase MnxG, from spores of several different marine Bacillus species. Appl. Environ. Microbiol. 74:1527-1534. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Duckworth, O. W., and G. Sposito. 2005. Siderophore-manganese(III) interactions. I. Air oxidation of manganese(II) promoted by desferrioxamine B. Environ. Sci. Technol. 39:6037-6044. [DOI] [PubMed] [Google Scholar]
- 24.Eddy, S. R. 1998. Profile hidden Markov models. Bioinformatics 14:755-763. [DOI] [PubMed] [Google Scholar]
- 25.Francis, C. A., E.-M. Co, and B. M. Tebo. 2001. Enzymatic manganese(II) oxidation by a marine α-proteobacterium. Appl. Environ. Microbiol. 67:4024-4029. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26.Francis, C. A., and B. M. Tebo. 2002. Enzymatic manganese(II) oxidation by metabolically dormant spores of diverse Bacillus species. Appl. Environ. Microbiol. 68:874-880. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27.Francki, K. T., B. J. Chang, B. J. Mee, P. J. Collignon, V. Susai, and P. K. Keese. 2000. Identification of genes associated with copper tolerance in an adhesion-defective mutant of Aeromonas veronii biovar sobria. FEMS Immunol. Med. Microbiol. 29:115-121. [DOI] [PubMed] [Google Scholar]
- 28.Friedrich, C. G., F. Bardischewsky, D. Rother, A. Quentmeier, and J. Fisher. 2005. Prokaryotic sulfur oxidation. Curr. Opin. Microbiol. 8:253-259. [DOI] [PubMed] [Google Scholar]
- 29.Gaasterland, T., and C. W. Sensen. 1996. Fully automated genome analysis that reflects user needs and preferences. A detailed introduction to the magpie system architecture. Biochimie 78:302-310. [DOI] [PubMed] [Google Scholar]
- 30.Grass, G., K. Thakali, P. E. Klebba, D. Thieme, A. Muller, G. F. Wildner, and C. Rensing. 2004. Linkage between catecholate siderophores and the multicopper oxidase CueO in Escherichia coli. J. Bacteriol. 186:5826-5833. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Hansel, C. M., and C. A. Francis. 2006. Coupled photochemical and enzymatic Mn(II) oxidation pathways of a planktonic Roseobacter-like bacterium. Appl. Environ. Microbiol. 72:3543-3549. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Hanson, T. E., and F. R. Tabita. 2001. A ribulose-1,5-bisphosphate carboxylase/oxygenase (RubisCO)-like protein from Chlorobium tepidium that is involved in sulfur metabolism and the response to oxidative stress. Proc. Natl. Acad. Sci. USA 98:4397-4402. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Horsburgh, M. J., S. J. Wharton, M. Karavolos, and S. J. Foster. 2002. Manganese: elemental defence for a life with oxygen? Trends Microbiol. 10:496-501. [DOI] [PubMed] [Google Scholar]
- 34.Huston, W. M., M. P. Jennings, and A. G. McEwan. 2002. The multicopper oxidase of Pseudomonas aeruginosa is a ferroxidase with a central role in iron acquisition. Mol. Microbiol. 45:1741-1750. [DOI] [PubMed] [Google Scholar]
- 35.Imagawa, M., Y. Oku, H. I. EL-Belbasi, M. Teraoka, T. Nishihara, and M. Kondo. 1985. Synthesis and deposition of spore coat proteins during sporulation of Bacillus megaterium. Microbiol. Immunol. 29:1151-1162. [DOI] [PubMed] [Google Scholar]
- 36.Johnson, H. A., and B. M. Tebo. 2008. In vitro studies indicate a quinone is involved in bacterial Mn(II) oxidation. Arch. Microbiol. 189:59-69. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37.King, G. M., and C. F. Weber. 2007. Distribution, diversity, and ecology of aerobic CO-oxidizing bacteria. Nat. Rev. Microbiol. 5:107-118. [DOI] [PubMed] [Google Scholar]
- 38.Kuenen, G. 1999. Oxidation of inorganic compounds by chemolithotrophs, p. 249. In J. W. Lengeler, G. Drews, and H. G. Schlegel (ed.), Biology of the prokaryotes. Thieme Stuttgart, New York, NY.
- 39.Kumar, S., K. Tamura, and M. Nei. 2004. MEGA3: integrated software for molecular evolutionary genetics analysis and sequence alignment. Brief. Bioinform. 5:150-163. [DOI] [PubMed] [Google Scholar]
- 40.Kusian, B., and B. Bowien. 1997. Organization and regulation of cbb CO2 assimilation genes in autotrophic bacteria. FEMS Microbiol. Ecol. 21:135-155. [DOI] [PubMed] [Google Scholar]
- 41.Larimer, F. W., P. Chain, L. Hauser, J. Lamerdin, S. Malfatti, L. Do, M. L. Land, D. A. Pelletier, J. T. Beatty, A. S. Lang, F. R. Tabita, J. L. Gibson, T. E. Hanson, C. Bobst, J. L. T. Torres, C. Peres, F. H. Harrison, J. Gibson, and C. R. Harwood. 2004. Complete genome sequence of the metabolically versatile photosynthetic bacterium Rhodopseudomonas palustris. Nat. Biotechnol. 22:55-61. [DOI] [PubMed] [Google Scholar]
- 42.Larsen, E. I., L. I. Sly, and A. G. McEwan. 1999. Manganese(II) adsorption and oxidation by whole cells and a membrane fraction of Pedomicrobium sp. ACM 3067. Arch. Microbiol. 171:257-264. [Google Scholar]
- 43.Lee, Y., M. Hendson, N. Panopoulos, and M. Schroth. 1994. Molecular cloning, chromosomal mapping, and sequence analysis of copper resistance genes from Xanthomonas campestris pv. juglandis: homology with small blue copper proteins and multicopper oxidase. J. Bacteriol. 176:173-188. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Li, H., M. R. Sawaya, F. R. Tabita, and D. Eisenberg. 2005. Crystal structure of a RuBisCO-like protein from the green sulfur bacterium Chlorobium tepidum. Structure 13:779-789. [DOI] [PubMed] [Google Scholar]
- 45.Magliozzo, R. S., and J. A. Marcinkeviciene. 1997. The role of Mn(II)-peroxidase activity of mycobacterial catalase-peroxidase in activation of the antibiotic isoniazid. J. Biol. Chem. 272:8867-8870. [DOI] [PubMed] [Google Scholar]
- 46.Mellano, M. A., and D. A. Cooksey. 1988. Nucleotide sequence and organization of copper resistance genes from Pseudomonas syringae pv. tomato. J. Bacteriol. 170:2879-2883. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 47.Mills, S. D., C. A. Jasalavich, and D. A. Cooksey. 1993. A two-component regulatory system required for copper-inducible expression of the copper resistance operon of Pseudomonas syringae. J. Bacteriol. 175:1656-1664. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48.Moran, M. A., A. Buchan, J. M. Gonzalez, J. F. Heidelberg, W. B. Whitman, R. P. Kiene, J. R. Henriksen, G. M. King, R. Belas, C. Fuqua, L. Brinkac, M. Lewis, S. Johri, B. Weaver, G. Pai, J. A. Eisen, E. Rahe, W. M. Sheldon, W. Ye, T. R. Miller, J. Carlton, D. A. Rasko, I. T. Paulsen, Q. Ren, S. C. Daugherty, R. T. Deboy, R. J. Dodson, A. S. Durkin, R. Madupu, W. C. Nelson, S. A. Sullivan, M. J. Rosovitz, D. H. Haft, J. Selengut, and N. Ward. 2004. Genome sequence of Silicibacter pomeroyi reveals adaptations to the marine environment. Nature 432:910-913. [DOI] [PubMed] [Google Scholar]
- 49.Munson, G. P., D. L. Lam, F. W. Outten, and T. V. O'Halloran. 2000. Identification of a copper-responsive two-component system on the chromosome of Escherichia coli K-12. J. Bacteriol. 182:5864-5871. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.Parker, D. L., T. Morita, M. L. Mozafarzadeh, R. Verity, J. K. McCarthy, and B. M. Tebo. 2007. Inter-relationships of MnO2 precipitation, siderophore-Mn(III) complex formation, siderophore degradation, and iron limitation in Mn(II)-oxidizing bacterial cultures. Geochim. Cosmochim. Acta 71:5672-5683. [Google Scholar]
- 51.Parker, D. L., G. Sposito, and B. M. Tebo. 2004. Manganese(III) binding to a siderophore produced by a manganese(II)-oxidizing bacterium. Geochim. Cosmochim. Acta 68:4809-4820. [Google Scholar]
- 52.Platero, R., L. Peixoto, M. R. O'Brian, and E. Fabiano. 2004. Fur is involved in manganese-dependent regulation of mntA (sitA) expression in Sinorhizobium meliloti. Appl. Environ. Microbiol. 70:4349-4355. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Podell, S., and T. Gaasterland. 2007. DarkHorse: a method for genome-wide prediction of horizontal gene transfer. Genome Biol. 8:R16. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Preisig, O., R. Zufferey, C. A. A. Linda Thöny-Meyer, and H. Hennecke. 1996. A high-affinity cbb3-type cytochrome oxidase terminates the symbioses-specific respiratory chain of Bradyrhizobium japonicum. J. Bacteriol. 178:1532-1538. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Rensing, C., and G. Grass. 2003. Escherichia coli mechanisms of copper resistance in a changing environment. FEMS Microbiol. Rev. 27:197-213. [DOI] [PubMed] [Google Scholar]
- 56.Ridge, J. P., M. Lin, E. I. Larsen, M. Fegan, A. G. McEwan, and L. I. Sly. 2007. A multicopper oxidase is essential for manganese oxidation and laccase-like activity in Pedomicrobium sp. ACM 3067. Environ. Microbiol. 9:944-953. [DOI] [PubMed] [Google Scholar]
- 57.Roberts, S. A., G. F. Wildner, G. Grass, A. Weichsel, A. Ambrus, C. Rensing, and W. R. Montfort. 2003. A labile regulatory copper ion lies near the T1 copper site in the multicopper oxidase CueO. J. Biol. Chem. 279:31958-31963. [DOI] [PubMed] [Google Scholar]
- 58.Rodionov, D. A., M. S. Gelfand, J. D. Todd, A. R. J. Curson, and A. W. B. Johnston. 2006. Computational reconstruction of iron- and manganese-responsive transcriptional networks in alpha-proteobacteria. PLoS Comput. Biol. 2:e163. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 59.Schlosser, D., and C. Höfer. 2002. Laccase-catalyzed oxidation of Mn2+ in the presence of natural Mn3+ chelators as a novel source of extracellular H2O2 production and its impact on manganese peroxidase. Appl. Environ. Microbiol. 68:3514-3521. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Shevchenko, A., S. Sunyaev, A. Loboda, A. Shevchenko, P. Bork, W. Ens, and K. G. Standing. 2001. Charting the proteomes of organisms with unsequenced genomes by MALDI-quadrupole time-of-flight mass spectrometry and BLAST homology searching. Anal. Chem. 73:1917-1926. [DOI] [PubMed] [Google Scholar]
- 61.Shyu, J. B. H., D. P. Lies, and D. K. Newman. 2002. Protective role of tolC in efflux of the electron shuttle anthraquinone-2,6-disulfonate. J. Bacteriol. 184:1806-1810. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62.Singh, S. K., G. Grass, C. Rensing, and W. R. Montfort. 2004. Cuprous oxidase activity of CueO from Escherichia coli. J. Bacteriol. 186:7815-7817. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 63.Solomon, E. I., U. M. Sundaram, and T. E. Machonkin. 1996. Multicopper oxidases and oxygenases. Chem. Rev. 96:2563-2605. [DOI] [PubMed] [Google Scholar]
- 64.Sorokin, D. Y. 2003. Oxidation of inorganic sulfur compounds by obligately organotrophic bacteria. Microbiology 72:641-653. [PubMed] [Google Scholar]
- 65.Tabita, F. R. 1999. Microbial ribulose 1,5-bisphosphate carboxylase/oxygenase: a different perspective. Photosynth. Res. 60:1-28. [Google Scholar]
- 66.Tang, W. H., B. R. Halpern, I. V. Shilo, S. L. Seymour, S. P. Keating, A. Loboda, A. A. Patel, D. A. Schaeffer, and L. M. Nuwaysir. 2005. Discovering known and unanticipated protein modifications using MS/MS database searching. Anal. Chem. 77:3931-3946. [DOI] [PubMed] [Google Scholar]
- 67.Tebo, B. M., J. R. Bargar, B. G. Clement, G. J. Dick, K. J. Murray, D. Parker, R. Verity, and S. M. Webb. 2004. Biogenic manganese oxides: properties and mechanisms of formation. Annu. Rev. Earth Planet. Sci. 32:287-328. [Google Scholar]
- 68.Tebo, B. M., B. G. Clement, and G. J. Dick. 2007. Biotransformations of manganese, p. 1223-1238. In C. J. Hurst, R. L. Crawford, J. L. Garland, D. A. Lipson, A. L. Mills, and L. D. Stetzenbach (ed.), Manual of environmental microbiology, 3rd ed. ASM Press, Washington, DC.
- 69.Tebo, B. M., W. C. Ghiorse, L. G. van Waasbergen, P. L. Siering, and R. Caspi. 1997. Bacterially mediated mineral formation: insights into manganese(II) oxidation from molecular genetic and biochemical studies, p. 225-266. In J. F. Banfield and K. H. Nealson (ed.), Geomicrobiology: interactions between microbes and minerals, vol. 35. Mineralogical Society of America, Washington, DC. [Google Scholar]
- 70.Tebo, B. M., H. A. Johnson, J. K. McCarthy, and A. S. Templeton. 2005. Geomicrobiology of manganese(II) oxidation. Trends Microbiol. 13:421-428. [DOI] [PubMed] [Google Scholar]
- 71.Templeton, A. S., H. Staudigel, and B. M. Tebo. 2005. Diverse Mn(II)-oxidizing bacteria isolated from submarine basalts at Loihi Seamount. Geomicrobiol. J. 22:127-139. [Google Scholar]
- 72.Todd, J. D., G. Sawers, and A. W. B. Johnston. 2005. Proteomic analysis reveals the wide-ranging effects of the novel, iron-responsive regulator RirA in Rhizobium leguminosarum bv. viciae. Mol. Genet. Genomics 273:197-206. [DOI] [PubMed] [Google Scholar]
- 73.van Waasbergen, L. G., M. Hildebrand, and B. M. Tebo. 1996. Identification and characterization of a gene cluster involved in manganese oxidation by spores of the marine Bacillus sp. strain SG-1. J. Bacteriol. 178:3517-3530. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Voulhoux, R., G. Ball, B. Ize, M. L. Vasil, A. Lazdunski, L. Wu, and A. Filloux. 2001. Involvement of the twin-arginine translocation system in protein secretion via the type II pathway. EMBO J. 20:6735-6741. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 75.Wariishi, H., K. Valli, and M. H. Gold. 1992. Manganese(II) oxidation by manganese peroxidase from the basidiomycete Phanerochaete chrysosporium. Kinetic mechanism and role of chelators. J. Biol. Chem. 267:23688-23695. [PubMed] [Google Scholar]
- 76.Webb, S. M., G. J. Dick, J. R. Bargar, and B. M. Tebo. 2005. Evidence for the presence of Mn(III) intermediates in the bacterial oxidation of Mn(II). Proc. Natl. Acad. Sci. USA 102:5558-5563. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 77.Webb, S. M., B. M. Tebo, and J. R. Bargar. 2005. Structural characterization of biogenic Mn oxides produced in seawater by the marine Bacillus sp. strain SG-1. Am. Mineral. 90:1342-1357. [Google Scholar]
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