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Research Article

Shewanella spp. Genomic Evolution for a Cold Marine Lifestyle and In-Situ Explosive Biodegradation

  • Jian-Shen Zhao mail,

    jianszhao@yahoo.ca (JSZ); jalal.hawari@nrc.ca (JH)

    Affiliation: Biotechnology Research Institute, National Research Council Canada, Montreal, Quebec, Canada

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  • Yinghai Deng,

    Affiliation: Biotechnology Research Institute, National Research Council Canada, Montreal, Quebec, Canada

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  • Dominic Manno,

    Affiliation: Biotechnology Research Institute, National Research Council Canada, Montreal, Quebec, Canada

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  • Jalal Hawari mail

    jianszhao@yahoo.ca (JSZ); jalal.hawari@nrc.ca (JH)

    Affiliation: Biotechnology Research Institute, National Research Council Canada, Montreal, Quebec, Canada

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  • Published: February 08, 2010
  • DOI: 10.1371/journal.pone.0009109

Abstract

Shewanella halifaxensis and Shewanella sediminis were among a few aquatic γ-proteobacteria that were psychrophiles and the first anaerobic bacteria that degraded hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX). Although many mesophilic or psychrophilic strains of Shewanella and γ-proteobacteria were sequenced for their genomes, the genomic evolution pathways for temperature adaptation were poorly understood. On the other hand, the genes responsible for anaerobic RDX mineralization pathways remain unknown. To determine the unique genomic properties of bacteria responsible for both cold-adaptation and RDX degradation, the genomes of S. halifaxensis and S. sediminis were sequenced and compared with 108 other γ-proteobacteria including Shewanella that differ in temperature and Na+ requirements, as well as RDX degradation capability. Results showed that for coping with marine environments their genomes had extensively exchanged with deep sea bacterial genomes. Many genes for Na+-dependent nutrient transporters were recruited to use the high Na+ content as an energy source. For coping with low temperatures, these two strains as well as other psychrophilic strains of Shewanella and γ-proteobacteria were found to decrease their genome G+C content and proteome alanine, proline and arginine content (p-value <0.01) to increase protein structural flexibility. Compared to poorer RDX-degrading strains, S. halifaxensis and S. sediminis have more number of genes for cytochromes and other enzymes related to RDX metabolic pathways. Experimentally, one cytochrome was found induced in S. halifaxensis by RDX when the chemical was the sole terminal electron acceptor. The isolated protein degraded RDX by mono-denitration and was identified as a multiheme 52 kDa cytochrome using a proteomic approach. The present analyses provided the first insight into divergent genomic evolution of bacterial strains for adaptation to the specific cold marine conditions and to the degradation of the pollutant RDX. The present study also provided the first evidence for the involvement of a specific c-type cytochrome in anaerobic RDX metabolism.

Introduction

The oceans and their sediments have long been a sink for wastes from numerous human activities near shore and on the open ocean. Undersea unexploded ordnances (UXO) [1][3] are a source of hexahydro-1,3,5-trinitro-1,3,5-triazine(​RDX),2,4,6-trinitrotoluene (TNT), and dinitrotoluene (DNT) which are toxic to humans and other organisms[4][6]. Shewanella are ubiquitous in surface, coastal, and deep sea water as well as in sediments such as the highly polluted Baltic Sea and the coastal area of North Atlantic (Table 1). Some strains were also found in lake and groundwater environments (Table 1). Shewanella can grow anaerobically using nitrate, manganese dioxide (MnO2), trimethylamine N-oxide (TMAO), and/or dimethyl sulfoxide (DMSO) commonly found in marine sediment environments, as terminal electron acceptors [7][9]. Shewanella are well known for their ability to oxidize organic matter and reduce chlorinated pollutants [10], as well as metal ions including Fe (III) and uranium (VI) [7], [8], [11]. Recently, strains of Shewanella were found to be dominant (8.8% of total cultured bacteria) in a historical UXO-dumping site, Emerald Basin [12], [13], a 250 m deep depression on the continental shelf, and 60 nautical miles south of Halifax, Nova Scotia. Two representative strains were shown to be capable of degrading RDX [12], TNT, DNT, perchlorate (Jian-Shen Zhao et al, unpublished results), and nitrate commonly present in UXO. Subsequent characterizations of these strains revealed that they represent two new species and consequently were designated Shewanella sediminis HAW-EB3 [14] and Shewanella halifaxensis HAW-EB4 [15]. New evidence also showed that incubation of sediment with nitrated compounds such as 2,4-DNT led to enrichment of Shewanella [16]. Although several aerobic RDX-degrading were isolated [17], none of the strains were sequenced for their genomes. S. halifaxensis and S. sediminis were the first anaerobic RDX-mineralizing bacteria known to be dominant in a contaminated UXO site. In the present study, the genomes of the two strains of Shewanella along with two most closely related reference strains not from this contaminated site, Shewanella woodyi [18] and Shewanella pealeana [19], sequenced by the Joint Genomic Institute (JGI) of United States, were compared to determine their novel genomic properties.

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Table 1. Phenotypic properties of Shewanella used for comparative genomic analyses.

doi:10.1371/journal.pone.0009109.t001

All species of Shewanella, isolates or environmental clones, fell into two major clusters based on their 16S rDNA sequences (Fig. 1) as well as phenotypic properties of isolates [14]. Shewanella retrieved from the deep sea, where temperatures are low (4–10°C) and the salt concentrations are high (4%), were included in cluster I. The other Shewanella from environments including shallow coastal area, ocean surface, freshwater lakes and subsurface groundwater were included in cluster II. The water temperature and/or salinity in the above environments varied depending on season, climate zone and depth (Table 1), but usually were higher in temperatures and/or lower in salinity as compared to the deep sea. S. halifaxensis, S. sediminis, S. pealeana and S. woodyi were members of cluster I Shewanella adapted to the colder and deeper part of marine eco-system; they required Na+ and preferred low temperatures for growth and thus considered as cold-adapted obligate marine Shewanella [14], [15]. Other 13 strains of Shewanella listed in Table 1, mostly distributed in cluster II and not found at the UXO-contaminated Halifax site, had no growth requirement for Na+ and low temperature. Most Shewanella in cluster II were considered as non-obligate marine and were available for genomic comparison at the beginning of this study (Table 1). Comparing genomes of obligate marine Shewanella in cluster I with non-obligate marine Shewanella in cluster II (as listed in Table 1) would provide general insight into bacterial evolution for cold and marine adaptation. The overall goals of the present study were to compare genomes of S. halifaxensis and S. sediminis with reference strains (listed in Fig. 2) in order to understand their genomic evolution pathways for adaptation to a UXO-contaminated cold marine sediment site as well as for in-situ degradation of explosive RDX.

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Figure 1. Phylogenetic analysis of partial 16S rDNA sequences of all cultivated and uncultivated Shewanella.

The sequences of Shewanalla, Aeromonas and Moritella were all from GenBank (362 taxa in total). The phylogenetic tree was generated based on pair-wise nucleotide distance of Kimura two-parameter using the neighbour-joining method (pair-wise deletion, 3000 bootstrap value) included in the MEGA3 software package [68].

doi:10.1371/journal.pone.0009109.g001
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Figure 2. Phylogenetic analysis of the complete 16S rDNA sequences of γ-proteobacteria.

Only the 110 strains compared for their genomes were listed. Yellow (coliforms) and orange (soil Pseudomonas) colors indicate bacteria living in warmer environments. Blue colors indicate γ-proteobacteria living in colder marine/aquatic environments. Two 42°C -tolerant Shewanella are indicated by orange triangles. The dark blue colors indicate bacteria adapted to deep cold sea and polar environment. The phylogenetic tree was generated based on pair-wise nucleotide distance of Kimura two-parameter using the neighbour-joining method (complete deletion, 3000 bootstrap value) included in the MEGA3 software package [68].

doi:10.1371/journal.pone.0009109.g002

Results and Discussion

S. halifaxensis and S. sediminis Genomic Evolution

As shown in Figure 2, a comparison of the complete sequences of 16S rDNA genes of S. halifaxensis and S. sediminis with 15 other sequenced Shewanella revealed that the two marine bacteria were most closely related to Na+-requiring marine strains S. woodyi and S. pealeana. Pair-wise whole-genome alignment among the 17 sequenced Shewanella (Table 1) also demonstrated that the complete sequences of S. halifaxensis and S. sediminis were mostly conserved in S. pealeana (Fig 3a) and S. woodyi (Fig 3b). As shown in Figure 3a, S. halifaxensis had 10 very large genomic segments or Locally Collinear Blocks (LCB) ranging from 0.26 to 1.09 Mb conserved in S. pealeana. Gaps between LCBs were small and only five LCBS were inverted in S. pealeana. S. halifaxensis whole genome was also aligned very well with S. sediminis (Fig 3c) and S. woodyi (not shown). However the LCBs of the two pairs were shorter and more inversions occurred (S. sediminis, 30 LCBs, 0.06–0.67 Mb, 12 inversions; S. woodyi, 38 LCBs, 0.05–0.38 Mb, and 14 inversions) as compared to the alignment with S. pealeana. This demonstrates that S. halifaxensis genome is best conserved in S. pealeana than in S. sediminis and S. woodyi. In the case of S. sediminis, its whole genome was best aligned with S. woodyi with 9 large conserved LCBs (0.18–1.8 Mb) and 6 inversions (Fig 3b). In comparison, S. sediminis genome had relatively small LCBs conserved in genomes of S. halifaxensis and S. pealeana with more inversions (S. halifaxensis, 30 LCBs, 0.06 to 0.67 Mb, 15 inversions, Fig 3c; S. pealeana, 30 LCBs, 0.04–0.7Mb, 17 inversions). In contrast, genome of freshwater strain Shewanella oneidensis aligned very poorly with marine strain S. halifaxensis or S. sediminis with very small LCBs, large unaligned gaps between LCBs and many inversions (S. halifaxensis, 0.05 to 0.24 Mb, 43 inversions, Fig 3d; S. sediminis, 0.03 to 0.13Mb, 33 inversions). Poor whole-genome alignment was also observed between the two RDX-degrading marine Shewanella and other non-obligate marine Shewanella in cluster II (data not shown). This clearly demonstrates that the genomes of marine strains of Shewanella are significantly different from the genomes of freshwater and non-obligate marine strains of Shewanella.

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Figure 3. Whole-genome alignment of S.halifaxensis and S. sediminis with related Shewanella.

Progressive-Mauve software 2.2.1 [63] was used to prepare the following alignment (minimal LCB weight, total number of LCBs). a), S. halifaxensis/S. pealeana (35774 base, 12); b) S. sediminis/S. woodyi (4207 base, 28); c) S. halifaxensis/S. sediminis (2693 base, 43); d) S. halifaxensis/S. oneidensis (118 base, 211). The same colored blocks indicate the segments, or Locally Collinear Blocks (LCBs) conserved among the two bacteria compared (linked by same line). Inverted LCBs are linked by lines crossing the mid point of chromosomes and appear on the opposite strand of the genome compared.

doi:10.1371/journal.pone.0009109.g003

To further determine the genomic similarity between the two RDX-degrading obligate marine Shewanella (S. halifaxensis and S. sediminis) and other reference bacteria living in similar or contrasting environments, the sequences of all their deduced proteins were compared using BLAST (cut-off E-value of e-20), to all 623 bacteria that were available for genomic comparison. The total deduced proteins of S. halifaxensis were found best conserved in S. pealeana (83.9%), whereas those of S. sediminis were best conserved in S. woodyi (69.6%) (Table 2). The total deduced proteins of both strains were much less conserved in non-obligate marine Shewanella (58–61%) such as S. oneidensis. This further demonstrates that the genomes of S. halifaxensis and S. sediminis have evolved along with S. pealeana and S. woodyi as an obligate marine lineage of Shewanella, distinct from those in cluster II.

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Table 2. Genomic properties of four obligate marine species of Shewanella sequenced in the present study.

doi:10.1371/journal.pone.0009109.t002

As shown in the phylogenetic tree prepared using the complete sequences of 16S rDNA (Fig. 2), Shewanella spp. were closely related to marine/aquatic γ-proteobacteria Aeromonas, Vibrio, Photobacterium, Pseudoalteromonas, Colwellia, and Psychromonas. To determine the S. halifaxensis and S. sediminis genes conserved in both Shewanella and these related bacteria, reciprocal best hit analysis (with a cut off E-value of -20) was conducted to compare all their deduced proteins with 15 other strains of Shewanella listed in Table 1. S. halifaxensis and S. sediminis genomes were found to share 1814 protein coding sequences (CDS) (42% total CDSs of S. halifaxensis and 40% total CDSs of S. sediminis) (Table 2) with all Shewanella compared, referred to as core Shewanella CDSs (CDSc, Fig. 4a1, b1). CDSc were found highly conserved in the above related γ-proteobacteria, with more in the deep sea psychrophiles including C. psychrerythraea [20] (80%) and P. profundum [21] (79%), and slightly less in Pseudoalteromonas spp [22][24] (78%), Aeromonas spp. (78%) and Vibrio spp. (76%). Only 66–68% CDSc were conserved in non-marine members of γ-proteobacteria including intestinal coliform Serratia (68%) and soil bacteria Pseudomonas (66%) living in warmer environments as compared to marine environment. This indicates that the Shewanella CDSc are vertically inherited from a common γ-proteobacteria ancestor, with closer ties to γ-proteobacterial species adapted to the cold deep sea.

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Figure 4. Circular maps of S.halifaxensis and S. sediminis genes in CDS subsets and laterally transferred.

a1 or b1: cog profiles of CDS sets. CDSc, CDS4, CDS2 and CDS1 sets are explained in Table 2. One-letter abbreviations of cog are listed on the right side of b1. The corresponding color represent the following functional categories [69]: C, energy production and conversion; D, cell cycle control and mitosis; E, amino acid metabolism and transport; F, nucleotide metabolism and transport; G, carbohydrate metabolism and transport; H, coenzyme metabolism; I, lipid metabolism; J, translation; K, transcription; L, replication and repair; M, cell wall/membrane/envelope biogenesis; N, cell motility; O, post-translational modification, protein turnover, chaperone functions; P, inorganic ion transport and metabolism; Q, secondary metabolites biosynthesis, transport and catabolism; R, general functional prediction only; S, function unknown; T, signal transduction. a2,b2: Circular map of genes of lateral transfer. Red, green, brown or yellow color marks the genes in CDSc, CDS4, CDS2, or CDS1, respectively.

doi:10.1371/journal.pone.0009109.g004

As shown in Fig 5a, the top-matches to CDSc of all strains of Shewanella were mainly distributed in six genera including two mesophilic genera (Aeromonas and Vibrio) and four cold-adapted genera (Photobacterium, Colwellia, Pseudoalteromonas [P. haloplanktis, P. atlantica], Psychromonas). Among all strains of Shewanella, the five cold-adapted (S. halifaxensis, S. sediminis, S. pealeana, S. woodyi and S. frigidimarina [25]) had less CDSc best matched in mesophilic Aeromonas but more best matched in the above-mentioned four cold adapted genera (>38% in each genera) and Vibrio (V. fischeri ES114> V. parahaemolyticus RIMD 2210633> V. harveyi ATCC BAA-1116> V. vulnificus~V.cholerae) (Fig 5a). Interestingly, Shewanella amazonensis isolated from the tropical Amazon delta [26] and Shewanella loihica [27] isolated from an active Hawaii sea vent, which were known to tolerate >42°C, had the least CDSc best matched in P. profundum SS9. Among all strains of Shewanella, S. amazonensis capable of tolerating 45°C also had the least CDSc best matched in C. psychrerythraea 34H but the most CDSc best matched in Aeromonas sp. (A. hydrophila ATCC7966 and A. salmonicida subsp. salmonicida A449). This observation suggests that S. halifaxensis and S. sediminis have a unique evolutionary history for adaptation to colder marine environments in contrast to the evolutionary history of Shewanella especially S. amazonensis and S. loihica adapted to warmer parts of marine/coastal environments.

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Figure 5. Major bacteria with proteins best matched to Shewanella.

a, bacteria with top-hits matching proteins coded by CDSc; b, warm-adapted bacteria with top hits matching proteins coded by CDSnc; c, cold-adapted bacteria with top hits matching proteins coded by CDSnc. Bars represent bacteria with top hits matching CDS in strains of Shewanella as indicated on the x-axis (abbreviation listed in Table 1). The bar height indicates the count of hits in the bar-represented bacteria matching CDSnc (b, c) or the percentage of hits relative to the 1814 CDSc (a). The total hits in warm- or cold-adapted bacteria are indicated by the non-filled red or blue bars, respectively.

doi:10.1371/journal.pone.0009109.g005

Of the Shewanella CDSc, 333 were found to be absent in coliform and pseudomonads living in non-marine environments. Half of the 333 non-marine CDSc were functionally uncharacterized and likely novel proteins. Among other half of 333 marine CDSc functionally characterized, some were annotated as membrane proteins related to NaCl-tolerance and biofilm-formation. These included a Na+/H+ exchanger and a GTP-binding protein (Table 3) conserved in all closely related marine γ-proteobacteria including Vibrio, Aeromonas, Colwellia, Pseudoalteromonas, Psychromonas, and Photobacterium. A few other halotolerance-related proteins such as a Na+/H+ antiporter NhaC as well as a chloride channel, were conserved only in some of the above-mentioned marine γ-proteobacteria. Presence of these halotolerance genes in all Shewanella spp is consistent with their ability to tolerate high content of NaCl [9].

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Table 3. S. halifaxensis and S. sediminis proteins for marine adaptation.

doi:10.1371/journal.pone.0009109.t003

More than 60% of total CDSs of S. halifaxensis and S. sediminis were not in CDSc, and were designated as non-core part of CDS (CDSnc). Based on deduced protein sequence similarity, about 58–80% of CDSnc had orthologs in cluster I Shewanella, and only <52% had orthologs in cluster II Shewanella. Therefore, the two RDX-degrading marine strains share more genes with obligate marine Shewanella in cluster I . Unlike CDSc, their CDSnc were less frequent (39–28.7% in each bacterium) in finding orthologs (based on protein sequence blasting) in the genome of Photobacterium, Vibrio, Colwellia, or Aeromonas. However, the top hits to CDSnc were still mainly distributed among the above four genera and Pseudoalteromonas (Fig 5b, c). More infrequent top hits occurred in Psychromonas, Hahella, Idiomarina, Marinomonas or Marinobacter (Fig. 5b,c). These results suggest that many of the CDSnc likely originate via horizontal transfer from the marine gene pool and possibly account for their adaptation to deep sea environments.

Compared to other Shewanella, the cold-adapted obligate marine S. halifaxensis, S. sediminis, S. pealeana and S. woodyi, showed greater homology in CDSnc to psychrophilic P. profundum strain SS9. Among all Shewanella, S. sediminis and S. woodyi also had more CDSnc best matched in psychrophilic C. psychrerythraea strain 34H. The cold-adapted S. frigidimarina in cluster II had a greater identity in CDSnc to cold adapted Pseudoalteromonas. In total, for any of the above five cold-adapted Shewanella, the number of CDSnc best matched in cold-adapted non-Shewanella bacteria (Fig 5c) were higher than the number of CDSnc best matched in warm-adapted bacteria (Fig 5b). In contrast, for any of mesophilic Shewanella mostly in cluster II, the number of CDSnc best matched in mesophilic bacteria (Fig 5b) was higher than those best matched in cold-adapted bacteria (Fig 5c). This suggests that over the course of evolution, the five cold-adapted Shewanella have frequently exchanged their genes with bacteria living in cold environment.

To determine the genes unique to the two marine Shewanella, S. halifaxensis and S. sediminis, their CDSnc were further separated into three non-overlapping subsets (Table 2). The first part was CDS4 shared among the four cold-adapted Shewanella: S. halifaxensis, S. pealeana, S. woodyi, and S. sediminis. The second part was grouped in CDS2, which was CDS4-excluded S. halifaxensis CDSnc shared with S. pealeana (CDS2-hp) or S. sediminis CDSnc shared with S. woodyi (CDS2-sw). The remaining non-CDS4 and non-CDS2 part of CDSnc was referred to as CDS1-ha for S. halifaxensis or CDS1-se for S. sediminis. Blast analyses using protein sequence showed that all three subsets of CDSnc of S. halifaxensis and S. sediminis were best matched in the cold deep sea bacterium P. profundum, with the exception of S. sediminis CDS2-sw that was best matched in cold-adapted marine bacterium C. psychrerythraea. This indicates the influence of the two cold-adapted marine bacteria P. profundum and C. psychrerythraea in shaping the genomes of S. halifaxensis and S. sediminis.

Many S. halifaxensis and S. sediminis CDSs in CDS4, CDS2 and CDS1 (with some in CDSc) were opportunistic genes, not commonly conserved (or best matched) in closely related bacteria. These CDSs were identified, and presented in their circular chromosomal maps (Figure 4a2, 4b2). The annotated functions of these genes are available online from the Scalable Vector Graphics (SVG) Figures (Fig. S1 for S. halifaxensis, Fig. S2 for S. sediminis, supplementary materials). These genes were concentrated in 7–15 major genomic regions or islands on the chromosomes. Many integrase or transposase genes responsible for genomic recombination and rearrangement were found in the midst or near the ends of these islands. This evidence supports that these CDSs are genes likely horizontally transferred from bacteria in the same environment [28][30]. The majority of predicted foreign sources were proteobacteria, mainly in γ-division, with minor contributions from proteobacteria in α-, β-, δ- and ε-divisions, and most of them lived in marine and aquatic environment. Surprisingly, some were even members of gram-positive, spore-forming Firmicute, or photosynthetic bacteria such as Cyanobacteria. Close to 100 of them were freshwater bacteria including 49 terrestrial Pseudomonas, suggesting a history of close contact and relationship of Pseudomonas with the two marine strains of Shewanella over the course of genomic evolution.

Genes for an Obligate Marine Lifestyle

Compared to other strains of Shewanella, obligate marine S. halifaxensis and S. sediminis were predicted to have more and unique CDSs associated with adaptation to sea salts and toxic chemicals (Table 3). The two strains had two common Na+-dependent nutrient symporters [31] found in CDSc of all Shewanella. Unlike most non-obligate marine Shewanella, the two obligate marine strains had many unique Na+-dependent nutrient symporters found in their CDSnc subsets. For example, both strains had eight Na+-dependent nutrient symporters in CDS4 set; and these were shared with obligate marine relatives S. pealeana and S. woodyi. Seven more Na+/nutrient symporters were found in CDS2-hp of S. halifaxensis for transport of dicarboxylate, glutamate [Glu] and nucleosides. Three more Na+/nutrient symporters were found in CDS1-se of S. sediminis for transport of Glu, proline [Pro], dicarboxylate and amino acids. Based on genome annotations of all Shewanella, Glu was predicted to be an essential precursor for biosynthesis of heme, nucleobase (purine, pyrimidine), Pro, peptiglycan, aminosugar, and fatty acids in Shewanella. Glu could also be a precursor to biosynthesis of aspartate (Asp) and lysine (Lys). Glu and Pro were also known osmoprotectants important for bacterial adaptation to salty environments [32][34]. Dicarboxylate and Glu metabolite 2-oxoglurate were part of the Krebs cycle (tricarboxylic acid, TCA) that supplies NADH and building blocks to biosynthesis of lipid, polysaccharides, proteins and nucleic acids. Requirement of Na+ as a motive force for transport of these essential growth substrates are consistent with the nature of S. halifaxensis and S. sediminis being obligate marine bacteria. Detection of many Na+-dependent nutrient symporters in S. halifaxensis and S. sediminis CDSnc strongly demonstrates that these two marine species of Shewanella have evolved significantly for optimal adaptation to marine environment.

On the other hand, to maintain the difference in Na+ concentration across the membrane, marine bacteria have to remove Na+ leaked from sea water into cells [31]. Compared to other Shewanella, the four obligate marine Shewanella were found to have more unique Na+/H+ antiporter and/or exchanger genes[35], [36] (Table 3): 4 in CDS4, 7 in CDS2-hp of S. halifaxensis, 3 in CDS2-sw of S. sediminis and 4 in CDS1-se of S. sediminis. The obligate marine Shewanella CDS4 also included genes for a Na+-translocating oxaloacetate decarboxylase [37] (YP_001673465) (Table 3) and two NADH-dependent Na+-pumps (Table 4) absent in genomes of many other Shewanella. The first Na+-pump (pump A) was a NADH:ubiquinone oxidoreductase ABCDEF system [38] (YP_001673869-73874, Table 4); the second pump (pump B) was composed of three unique NADH dehydrogenases (quinone) (YP_001675561-5569), a Na+/H+ antiporter, a cation antiporter and a multiple resistance and pH regulation protein F. The Na+-pump B system was also found (with homologs) in cold-adapted S. frigidimarina but rarely in other Shewanella. The three unique NADH dehydrogenases of Na+-pump B were most similar to those in α-proteobacteria Parvibaculum lavamentivorans DS-1 [39]. The Na+/H+ antiporter of pump B was closely related to the one in anaerobic mud-dwelling, anoxygenic phototrophic α-proteobacteria Rhodospirillum rubrum ATCC 11170 [40]. These results suggest that these marine Shewanella genomes have recruited the above transporter genes by horizontal gene transfer for better adaptation to marine environment.

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Table 4. S. halifaxensis and S. sediminis proteins involved in electron transfer and biological reduction.

doi:10.1371/journal.pone.0009109.t004

To adapt to the high osmotic pressure of seawater, S. halifaxensis and S. sediminis were also found to have the genes responsible for transport of osmoprotectants betaine/choline/carnitine (BCCT) [32] (Table 3). One BCCT transporter gene was found in genomes of most Shewanella except the freshwater strain S. oneidensis. The CDS4 of the four obligate marine Shewanella had two transporter genes for BCCT and one ABC-type transporter gene for glycine betaine/L−proline also known as osmoprotectants (Table 3). In addition, S. halifaxensis (three in CDS2-hp) and S. sediminis (two in CDS1-se) also had some unique BCCT transporter genes for better osmotic pressure protection (Table 3).

Marine sediment is known to be a final destination of many toxic chemicals in the eco-system. S. halifaxensis and S. sediminis as two marine sediment bacteria were found to have abundant unique genes for acriflavin resistance and toxic compound extrusion (MATE, multidrug and toxic compound extrusion efflux). They had 14 toxin resistance genes found in CDSc shared with all Shewanella. Twenty-five more toxin resistance and efflux genes were predicted in CDS4 set that were unique to all of the four obligate marine Shewanella. More toxin-resistance genes were found in the specific CDSnc subsets of S. halifaxensis (18 in CDS2-hp, 7 in CDS1-ha) and S. sediminis (6 in CDS2-sw, 26 in CDS1-se). Sixteen toxin-resistance genes of the two marine strains (3 in CDS4, 4 in CDS2-hp, 1 in CDS2-sw, 8 in CDS1-sw) were absent in most non-obligate marine Shewanella. Four pairs of the RND family MFP subunits and effluxes were absent in S. oneidensis MR-1 known to adapt to freshwater lakes, indicating their association to marine sediment. Furthermore, the four obligate marine strains had several effluxes for pumping out heavy metals, calcium and potassium which were not found in genomes of many other Shewanella (Table 3).

The present genomic comparison between obligate marine and non-obligate marine species of Shewanella clearly shows that marine species have evolved to contain more unique genes responsible for resistance to toxins and high osmotic pressure. Most importantly the present comparison for the first time demonstrates that obligate marine species have evolved to take advantage of the constantly high content of Na+ in marine environment as a driving force for uptake of essential nutrients.

Amino Acid Composition Profiles of Cold-Adapted γ-Proteobacteria

Thermophilic proteins adapted to higher temperatures were known to have stable structures characterized by having certain amino acid residues substituted by Pro [41], [42] and Arginine (Arg) [43]. Proteins in psychrophiles were believed to have looser structures and increased conformation flexibility to allow for higher specific activity at low temperatures [44][46]. An earlier study showed replacement of Arg by Lysine (Lys) or Serine (Ser), Valine (Val) by Alanine (Ala) or Isoleucine (Ile), Lys by Ser or Asparagine (Asn), and Glu by Ala, in 21 psychrophilic bacterial enzymes as compared to their meso/thermophilic homologs [47].

To provide insight into how bacterial proteins evolve to adapt to cold environment, S. halifaxensis, S. sediminis and three other cold-adapted Shewanella were compared on proteome amino acid composition with 12 other mesophilic strains of Shewanella as well as 93 other γ-proteobacteria living in either warm or cold environments (listed in Fig 2). As shown in Figure 6a1, among the total 110 γ-proteobacteria (including 17 strains of Shewanella) compared, the marine/aquatic γ-proteobacteria living in generally colder environments (marked by the blue color, Fig 2) contrasted to those living in warmer environments (marked by the yellow or orange color, Fig 2) with regards to composition of certain amino acids. The typical warm-adapted bacteria were soil pseudomonads and animal intestinal coliforms known to grow optimally at 30–37°C. Bacteria living in colder environment were found to be lower in the contents of Ala, Pro, Arg, Glycine (Gly) and Leucine (Leu), but higher in contents of Asp, Asn, Ile, Lys and Ser.

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Figure 6. The characteristic profiles of amino acid composition and G+C content in cold-adapted γ-proteobacteria.

Bacterial abbreviations for b1, b2 are listed in Table 1. In general in a1,b1,c1, each axis represents the deviation of one amino acid composition in one bacterium (or CDS set) from the average in all bacteria compared. One line shows the amino acid deviation in one specific bacterium or CDS set. a1, deviation in one bacterium from the average of all 118 proteobacteria as given in Fig 2; b1, deviation in one strain of Shewanella from the average of 17 strains of Shewanella; c1, deviation in one set of CDS from the average of total CDSs in S. sediminis. Warm-adapted bacteria were represented by yellow, orange and red lines and symbols; cold-adapted bacteria were represented by the blue lines and symbols. a2, correlation between amino acid compositions of all 623 sequenced bacteria and their G+C content. Bacteria are represented by their G+C content. Amino acid compositions are displayed in a cumulative format. b2, deviation of G+C content in one strain of Shewanella from the average of all 17 strains of Shewanella; c2, deviation of G+C content of a set of CDS from the value of total CDS in S. sediminis. In a1, b1, blue curve indicates the psychrophilic (or psychrotrophic) bacteria; yellow, orange, and green curves indicate bacteria living in warm environments.

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Interestingly, among the 110 strains compared (Fig 6a1), the amino acid composition profiles of cold-adapted S. sediminis, S. woodyi, S. halifaxensis, S. pealeana and S. frigidimarina were closer to psychrophilic species of other genera than to mesophilic strains of Shewanella in cluster II. This suggests a temperature-driven protein divergent evolution pathway within the same phylogenetic group. This trend was clearly observed among Shewanella and 6 other closely related marine γ-proteobacterial genera (31 strains). The 10 cold adapted bacteria included two strains of Pseudoalteromonas, 5 strains of Shewanella, and one strain of Colwellia, Photobacterium, or Psychromonas (dark blue triangles, Fig 2). The 21 warm-adapted bacteria included 12 strains of Shewanella, 2 strains of Aeromonas and 7 strains of Vibrio. Compared to the warm-adapted marine γ-proteobacteria, the cold-adapted were lower in the contents of Ala, Arg, Pro, Leu, Trp and His, but higher in the contents of Ile, Lys, Asp, Asn, Ser and Tyr. As shown in Table 5, the above differences in total proteins between the two groups of marine γ-proteobacteria were significant because the p-values were less than 0.01.

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Table 5. Amino acid composition and G+C content comparison between cold- and warm-adapted γ-proteobacteria.

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This trend was also true for homologous proteins among the above 31 marine γ-proteobacteria. The p-values on differences in compositions of Ile, Lys Asn, Ser, Ala, Pro, Arg and Trp were lower than 0.01. The lower Leu (p = 0.13) and His (p = 0.11) contents as well as the higher Asp content (p = 0.76) were also observed in cold-adapted marine γ-proteobacteria, but the differences appeared to be insignificant because the p-values were relatively high (>0.05, Table 5).

Furthermore, a difference on composition of above mentioned amino acids was observed between the 5 strains of Shewanella that did not tolerate 30°C and the 12 mesophilic strains of Shewanella that tolerated 30°C. As shown in Table 5, these differences in total proteins were significant with p-values below 0.01 for most of above mentioned amino acids except His (p = 0.09) (Table 5). Among the homologous proteins of the 17 strains of Shewanella (coded by CDSc), the five cold-adapted Shewanella were also clearly lower in Ala, Leu, Pro, and Arg contents, but higher in Ile, Lys, Asn, and Ser contents than the warm-adapted Shewanella (Fig 6b1). The differences on the above amino acids were significant with p values below 0.04 (Table 5). The two most warm-adapted Shewanella, S. amazonensis and S. loihica, which could grow at temperature >42°C, were especially higher in the content of Ala, Leu, Pro, or Arg than the rest Shewanella. The present study shows for the first time that the proteomes of cold-adapted γ-proteobacteria have lower contents of Ala, Arg and Pro as well as higher contents of Ile, Lys and Asn, as compared to closely related γ-proteobacteria adapted to warmer environment. This suggests that this characteristic amino acid profile observed in cold-adapted γ-proteobacteria (or subsets) might be beneficial to protein conformation flexibility of total proteome especially of those proteins produced and active under low temperature conditions [22], [43], [44], [46][47].

Some of the composition differences observed in certain amino acids between warm-adapted and cold-adapted bacteria could be attributed to the differences in the GC content of their genomes. As shown in Figure 6a2, among the 623 sequenced bacteria, Arg, Pro, Ala and Gly contents were proportional to their genome GC contents, that is, the higher the GC content was, the higher the content of the four above-mentioned amino acids were. The opposite was also true for Ile, Lys, Asn, or Tyr. As shown in Table 5, the cold-adapted marine γ-proteobacteria were indeed lower in GC content than mesophilic ones with a p-value <0.001. Among the 17 strains of Shewanella, the five strains that did not tolerate 30°C, were significantly lower in GC content for both total CDS and CDSc than strains of Shewanella that tolerated 30°C (Table 1), with p-value <0.01. As shown in Figure 6b2, S. amazonensis and S. loihica that tolerated >42°C were especially higher in G+C content than the rest of Shewanella. Therefore the low content of Ala, Pro, Arg, and high content of Ile, Lys and Asn observed in cold-adapted bacteria are consistent with their low GC content as compared to warm-adapted bacteria.

As shown in Figure 62a, no correlation was observed between GC content and compositions of other amino acids including Asp, Ser, Leu, Trp and His. The latter amino acids also shifted their compositions in cold adapted bacteria as compared to warm-adapted bacteria especially for total proteins (Table 5, Fig 6). This suggests that bacteria may adjust their protein amino acid compositions to better adapt to changes in temperatures without necessarily affecting or involving changes in their genome GC contents.

For S. sediminis (Fig 6c1) or S. halifaxensis (data not shown), the proteins coded by CDS1 were also lower in Ala, Arg and Pro contents and higher in Ile, Asn, and Ser contents than those coded by CDSc. This trend is similar to those observed between cold-adapted and warm-adapted bacteria as shown in Fig 6a1 and 6b1. These results further suggest that the proteins coded by CDS1 of the two Shewanella are more cold-adapted than those coded by core Shewanella genes (CDSc), inherited from a common proteobacterial ancestor. The lower contents of Ala, Arg and Pro in proteins coded by CDS1 correlated well with the lower GC content of CDS1 in S. halifaxensis (42.8%) or in S. sediminis (45.8%) as compared to CDSc (S. halifaxensis, 45.8%; S. sediminis, 47.0%) (Fig 6c2). As discussed in above sections, many CDS1 of S. halifaxensis and S. sediminis were laterally transferred (Fig 4a2 and b2), mostly from cold-adapted bacteria. These results further provide evidence for adaptation of S. sediminis and S. halifaxensis genomes to the cold sea by recruiting cold-adapted genes from bacteria living in a similar environment during later stage of genomic evolution.

Genes and Proteins Involved in Anaerobic RDX Metabolic Pathways

As two RDX-mineralizing anaerobic bacteria dominant at a UXO-contaminated marine sediment site, S. halifaxensis and S. sediminis were also capable of reducing several other explosives including percholorate (data not shown), dinitrotoluene and trinitrotoluenes (Table 1). For comparison, the three most closely related reference bacteria S. pealeana, S. woodyi and Shewanella hanedai, were tested for their ability to remove explosives. The results showed that the three reference bacteria not from the UXO-contaminated site, where S. halifaxensis and S. sediminis were dominant, displayed more than two times lower RDX-metabolic activity and little percholorate-removal activity under the same experimental conditions (Table 1). Presently, we also found that S. halifaxensis cells had a better viability when they were incubated in the MB-20 marine medium in the presence of a saturated amount of RDX as the sole terminal electron acceptor than in the absence of RDX (Fig. 7). A recent study using the molecular DGGE method also showed that anaerobic incubation with a nitrated compound, 2, 4-dinitrotoluene (DNT) that was reported to be present at the contaminated site, led to enrichment of Shewanella in marine sediment sampled from this Halifax UXO site [16]. These findings together demonstrate that S. halifaxensis and S. sediminis are well-adapted for remediation of explosives (RDX, DNT, TNT, and ClO4) than most closely related reference strains of Shewanella not found at the contaminated site.

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Figure 7. Anaerobic growth of S.halifaxensis HAW-EB4 on RDX as the sole terminal electron acceptor.

CFU, colony-forming unit.

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Remediation of the above explosives requires an initial reductive step involving reductases and electron donors. As shown in Table 4, S. halifaxensis and S. sediminis genomes indeed contained more and unique genes for electron-transfer and reductases than S. pealeana and S. woodyi. For example, S. sediminis had six more subunits of DMSO reductase (five A subunits and one B subunit) than S. woodyi.

C-type cytochrome and RDX denitration pathway.

C-type cytochromes were electron-transferring proteins destined to enter the periplasmic space, and in some cases are secreted to the outer membrane by the Type II protein secretion system [48] for transferring electrons to extra cellular electron acceptors. Strains of Shewanella were known to use c-type cytochrome for periplasmic reduction of nitrate, fumarate [49], TMAO, and extra cellular reduction of DMSO [50] and metal oxides [48], [51][55]. Present genomic analysis showed that S. sediminis (48 reported in Genbank, 26 more identified in this study) and S. halifaxensis (36 reported in Genbank, 14 more identified in the present study) genomes had a higher number of c-type cytochrome genes compared to other strains of Shewanella (Table 4). Many were unique and novel c-type cytochromes shared by the two RDX degraders. They had several tetraheme cytochrome c genes absent in many other Shewanella. Two cytochrome c genes were absent in S. woodyi and S. pealeana (Table 4), but present in S. oneidensis that was also positive for RDX reduction (J. S. Zhao, D. Manno, J. Hawari, unpublished results). S. halifaxensis and S. sediminis also shared four additional pairs of flavo- and tetraheme- cytochrome c genes, one pair absent in any other Shewanella, three others present in the slower RDX-degrading S. pealeana, but not in the much poorer-RDX degrading S. woodyi. The latter three pairs of flavo- and tetraheme- cytochrome c were closely related to those in ε-proteobacteria Wolinella succinogenes DSM 1740 or Campylobacter concisus 13826. S. sediminis had 19 c-type cytochrome genes absent in closely related S. woodyi (Table 4) which displayed a five times lower RDX-metabolic activity (Table 1). Previously, cytochrome-like hemeprotein XplA in Actinomyces [56] and a cytochrome P450 in rabbit liver [57] were reported for aerobic RDX-reduction activity. The xplA was not found in either S. halifaxensis or S. sediminis. Interestingly, c-type cytochromes-abundant freshwater lake sediment bacteria Geobacter (97 in Geobacter sulfurreducens and 63 in Geobacter metallireducens) were also recently detected for their ability to reduce RDX [58].

In an earlier study, we reported that S. halifaxensis cells respiring on TMAO were optimal for removal of RDX, and the total c-type cytochromes were suggested to be involved in RDX reduction [59]. TMAO-grown cells were indeed found to contain higher contents of several c-type cytochromes than the slower RDX-degrading cells pre-grown on other electron acceptors (Fig. 8a). In this study, while we attempted to purify the RDX-reducing protein from TMAO-grown cells, a protein fraction containing a major cytochrome c (M = 52 kDa, indicated by an arrow in Fig. 8b) was found to display a NADH-dependent RDX-reducing activity (0.43 mg · L−1· h−1) (0.15 mg · ml−1 protein). Products analysis showed that RDX was degraded by a mono-denitration pathway to give MEDINA and HCHO (Fig. 8d) as observed for step a1-a2 in whole cells (Fig 9, a3-a4, abiotic reaction [57]). As shown in Figure 8e, the 420 and 552 nm peaks of the reduced form of the c-type cytochrome disappeared during RDX reduction, indicating RDX oxidation of cytochrome. Compared to cells incubated in the absence of any terminal electron acceptor, cells incubated with RDX as the sole terminal e-acceptor produced a higher content of the 52 kDa cytochrome (pointed by an arrow in Fig. 8c), indicating the capacity of RDX to up-regulate biosynthesis of this cytochrome. In the nitrate- and aerobic-grown cells that displayed a lower RDX-degradation activity, this cytochrome was only produced in smaller amounts (pointed by an arrow in Fig. 8a). This demonstrates that the 52 kDa cytochrome is involved in RDX denitration. It should be mentioned that other cytochromes, especially those low molecular weight cytochromes dominant in aerobic and nitrate grown cells, did not catalyze NADH-dependent RDX degradation. Using a proteomic approach, the 52 kDa cytochrome in the SDS-PAGE band was found to have a sequence best matching a multiheme C552 cytochrome (467 amino acids, YP_001673120, Shal_0886) in its genome. An orthologous cytochrome was also found in S. sediminis with a similarity of 86%.

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Figure 8. The 52 kDa cytochrome involved in RDX metabolism.

a-c, heme-stained SDS-PAGE. a, induction by terminal electron acceptors (O2, nitrate, TMAO, none). c, induction by RDX (control, -RDX); b, isolated cytochrome in lane C. d, cytochrome-catalyzed RDX denitration and products. e, UV-visible spectra of the isolated cytochrome during incubation with NADH in the presence (—) or absence (---) of RDX.

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Figure 9. RDX metabolic pathways in S.halifaxensis and the enzymes involved.

This figure was modified from the pathways published previously [57], [59].

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Interestingly, in the present study, RDX degradation activity was also found in a cytochrome c isolated from Saccharomyces cerevisiae (Sigma C2436), removing 0.42 mg L−1 h−1 of RDX under the same protein concentration (0.11 mg ml−1 protein). This further demonstrates the capacity of certain c-type cytochrome to mediate electron transfer from NADH to RDX. This is also consistent with the observation in Figure 7, showing that RDX improved viability of S. halifaxensis. Since RDX was the sole terminal electron acceptor in the carbon and nitrogen-rich MB-20 medium, the better viability of cells is likely caused by a weak RDX-respiring process involving c-type cytochrome.

Nitrite was an intermediate of the RDX denitration metabolic pathway (Fig 9). As shown in Table 4, S. sediminis and S. halifaxensis genomes were found to contain genes coding nitrite reductases. The genomes of the two RDX-adapted Shewanella contained some nitrite reductase genes shared with other Shewanella. They also coded some unique nitrite reductases absent in their close relatives. For example, S. sediminis genome had three genes for ammonia-forming cytochrome nitrite reductases and one gene for nrfD protein of formate-dependent nitrite reductase absent in S. woodyi; S. halifaxensis had two genes for ammonia-forming cytochromes absent in S. pealeana. This observation suggests that the two RDX degraders have evolved to increase their genetic potential to convert the toxic compound RDX to ammonium, a nitrogen source for growth of many bacteria in the marine eco-system including Shewanella.

Nitroreductase and RDX nitroso pathway.

Shewanella were also known to reduce RDX or DNT via a two-electron reduction of the nitro group to give nitroso derivatives (step b1-b3, Fig 9). Earlier studies described that a type I oxygen-insensitive 2e-transfer nitroreductase in coliform Enterobacter cloacae could slowly reduce RDX [60], [61]. Two genes for 2e-transfer nitroreductases were found in genomes of S. sediminis and S. halifaxensis genomes, and they all were conserved in reference strains S. pealeana and S. woodyi: one was coded by CDSc and conserved in all Shewanella, another was coded by CDS4 and absent in many other Shewanella. S. halifaxensis CDS2-hp coded two additional nitroreductases both shared with S. pealeana; one (YP_001673510, Table 4) was conserved in all coliforms (Salmonella, Shigella, Escherichia, Enterobacter, Klebsiella) but absent in all other Shewanella. S. sediminis had one unique nitroreductase gene (in CDS1-se, YP_001474717, Table 4) closely related to the one in Methylibium petroleiphilum PM1 but absent in S. woodyi. On the other hand, old Yellow family enzymes were also reported for their TNT-reducing activity [62]. S. halifaxensis and S. sediminis indeed had Old Yellow family enzymes (NADH: flavin oxidoreductases); several of them were unique to the two explosive degraders. Overall, since the 2e-nitroreductase was only previously reported for a poor RDX reducing activity, and these nitroreductases and Old Yellow family flavo enzymes were conserved in slow RDX-degrading strains of Shewanella as well as coliforms, they were unlikely to contribute significantly to RDX metabolism in S. halifaxensis and S. sediminis.

Aldehyde and formate dehydrogenases for RDX carbon mineralization.

Aldehyde and formate dehydrogenase likely involved in oxidation of HCHO, a ring cleavage product of RDX, to CO2 (Fig. 9, step a5, a6) were also predicted in the genomes of S. sediminis and S. halifaxensis. S. sediminis (Ssed) and S. halifaxensis (Ssed) shared two aldehyde dehydrogenase genes, one located in a betaine metabolic operon (Ssed, YP_001472856- YP_001472860; Shal, YP_001673283-YP_001673287) and another in a proline metabolic operon (Shal, YP_001674771-YP_001674772; Ssed, YP_001473499-YP_001473500). The two RDX-degraders shared two formate dehydrogenase genes, one (Shal: YP_001672333-YP_001672346; Ssed: YP001476145.1-YP001476158.1) conserved in most Shewanella except S. denitrificans, and another (Ssed: YP_001475940-YP_001475948; Shal: YP_001676207- YP_001676223) absent in many Shewanella including S. woodyi and S. pealeana. The formate dehydrogenase operons were composed of genes for c and γ subunits related to P. profundum. Interestingly, S. halifaxensis had four more formate dehydrogenase systems than S. sediminis, consistent with its capacity to mineralize a higher percentage of RDX to CO2 [12]. One system was composed of α,β,γ subunits conserved in S. pealeana and coliform bacteria (YP_001672725- YP_001672735) such as E. coli ATCC 8739, Enterobacter sp. 638, and Citrobacter koseri ATCC BAA-895. Two other systems were composed of γ-subunits conserved in P. profundum SS9 and 4Fe-4S ferredoxin binding domain proteins (YP_001676214-YP_001676222) related to either Desulfitobacterium hafniense Y51 or Aeromonas. The fourth formate dehydrogenase gene (YP_001673633-YP_001673636) was associated with a Fe-only hydrogenase present in Syntrophomonas wolfei subsp. wolfei str. Goettingen. The present genomic analyses show that, as shown in Figure 9, the two Shewanella have evolved to recruit many genes for oxidization of [HCHO], a RDX ring cleavage product, to CO2, yielding NADH. The NADH generated should be sufficient for reduction of NO2- to ammonia. Therefore the two strains of Shewanella are predicted to have the genomic potential to mineralize RDX and use it as an energy and nitrogen source for bacterial growth if other required co-factors are provided.

Conclusions

In summary, the present study represents the first comprehensive genomic comparison of psychrophiles or psychrotrophs with closely related mesophiles within the same genus (Shewanella) or division (γ-proteobacteria). As a result we were able to discover that a shift in GC content and composition of certain amino acids in cold-adapted bacteria. As obligate marine bacteria, the two RDX degraders' genomes were found to be enriched with genes for halotolerance or for Na+-driven import of essential nutrients from the environment. Furthermore, the two strains of Shewanella had genes for c-type cytochromes, nitroreductases, and nitrite reductases for initial RDX reduction, as well as aldehyde and formate dehydrogenases for mineralization of RDX to CO2. These genomic evolution analyses and experimental data presented herein explained why S. halifaxensis and S. sediminis were dominant at UXO contaminated marine sediment sites. These comparative genomic and proteomic analyses represented the first attempt to understand how environmental bacteria were naturally selected in a specific contaminated site for survival and for in-situ remediation of pollutants, the explosive RDX in the present case.

Materials and Methods

Genome Sequencing and Annotation

Sequencing, assembly, finishing, pipeline annotation, and verification were completed by staff members of the US Department of Energy Joint Genome Institute (JGI, Walnut Creek, CA, USA) using standard protocols as published online (http://www.jgi.doe.gov/sequencing/protoc​ols/prots_production.html). Briefly, the whole-genome shotgun sequencing method and the 3-Kb, 8-Kb, and 40-Kb DNA libraries were used for sequencing from both sides of library inserts. Sequences were aligned using genome assemblers to produce draft assembly, followed by gap closing, quality improvement, and assembly verification. Genome annotation was performed by Oak Ridge National Laboratory using automated annotation Genome Portal. The genomes were published in NCBI with accessions listed in Table 1.

Comparative Genomics

In order to determine the complete genomic sequence similarity, and large scale genomic arrangement occurred over the course of evolution between S. halifaxensis, S. sediminis and 15 other species of Shewanella, whole-genome pair wise alignment was conducted using Progressive Mauve (Multiple alignment of conserved genomic sequence) 2.2.1 [63] (http://gel.ahabs.wisc.edu/mauve/mauve-us​er-guide). Genomes of the following related pairs were shown in Figure 3 a:) S. halifaxensis HAW-EB4/S. pealeana ATCC 700345; b) S. sediminis HAW-EB3 /S. woodyi ATCC 51908; c) S. halifaxensis HAW-EB4/S. sediminis HAW-EB3; d) S. halifaxensis/S. oneidensis MR-1. The conserved orthologous segments among bacterial pairs, referred to as Locally Collinear Blocks (LCBs) that may or may not be reordered or inverted in another genome, were identified. Same LCBs between aligned genomes were marked with the same color. Those LCBs inverted in another genome were shown on the opposite side of the axis. The minimum LCB weight was set at the lowest level to prepare the alignment results in Figure 3.

To determine the genes of S. halifaxensis and S. sediminis conserved among all 17 strains or in related strains of Shewanella, local reciprocal (two ways) blast (Basic Local Alignment Search Tool) 2.2.18 was used to compare the sequences of all deduced proteins in one bacterium to 16 other strains of Shewanella (Table 1). The computation was conducted on a station located in the Computational Chemistry and Biology group, Biotechnology Research Institute, National Research Council Canada (Montreal, Canada). The cut off E-value was set at 1e-20. The sets of CDSs that were common first hit (reciprocal blast) among all 17 strains of Shewanella, were identified as the core Shewanella CDS (CDSc), with the rest CDS refereed to as non-core CDSs (CDSnc) (Table 1). In CDSnc, the common first hit among S. halifaxensis, S. pealeana, S. sediminis and S. woodyi were further identified, labelled as CDS4, by deducting CDSc from the total common first hit among S. halifaxensis, S. pealeana, S. sediminis and S. woodyi. In the rest of CDSnc of S. halifaxensis, those common first hit with S. pealeana were also identified, labelled as CDS2-hp, by deducting CDSc and CDS4 from the total common first hit among S. halifaxensis and S. pealeana. The remaining S. halifaxensis CDSs were labelled as CDS1-ha. The same approach was used to obtain CDSc, CDS4, CDS2 and CDS1-se for S. sediminis, except that CDS2 was orthologs to S. woodyi minus those included in CDS4 and CDSc.

To clearly view the physical distribution of different sets of CDS on the chromosomes, Circular Genome Viewer software (CG view) [64] was used to generate their maps. The predicted functions of genes in each CDS set were shown by their colors, each of which represents a cog category (see legend to Fig 4a1 and b1).

To identify the close relatives of the genes in S. halifaxensis and S. sediminis and determine the source of genes of lateral transfer, different CDS sets were compared to 623 other bacterial genomes using local reciprocal (two ways) blast (Basic Local Alignment Search Tool) 2.2.18. The bacteria with the top-matched sequences were identified and considered to be the most likely sources (or origins) of the genes. For S. halifaxensis, the gene was considered to be foreign-originated or horizontally transferred in the following two cases. One case was, if the best-matched bacterium was not a member of Shewanella after excluding 1) S. pealeana, 2) S. pealeana, S. sediminis and S. woodyi, 3) S. pealeana, S. sediminis, S. woodyi and S. loihica. The second case was, if the best matched bacterium was not a member of a marine γ-proteobacteria or a γ-proteobacteria after excluding hits in Shewanella. The same approach was applied to identify the sources of S. sediminis genes except in case 1) S. pealeana was replaced with S. woodyi, and in case 2) S. sediminis was replaced with S. halifaxensis. Most of these identified horizontally transferred genes were presented on circular chromosome maps shown in Figure 4a2 for S. halifaxensis and b2 for S. sediminis. The color of the CDS on the circular map indicated the sets of CDS. The other detailed information of the CDS could be read directly online by opening the SVG format of the supplementary Figures (Fig S1, Fig S2) using Scalable Vector Graphics (SVG) viewer software. The non-Shewanella bacteria top-matched to CDSc or CDSnc) were presented in Figure 5a-c.

To determine the presence or absence of a genome A gene in genome B, the protein sequence coded by the genome A gene was blasted with a cut off E-value of 1e-20 to all proteins of genome B. This gene was considered absent in genome B if no hit (or homolog) was observed (Table 3). To help visualize the presence or absence of a gene in other genomes, heatmap.2 in g-plot and R-package were also used to prepare heatmaps based on blasting results.

Average Amino Acid Composition, GC Content, and Statistics

Perl programs written by YHD were used to calculate 1) the average composition of each amino acid (ACAA, % of total number of amino acids) in all proteins coded by total (or a subset) CDS of a bacterium (or a group of bacteria), 2) the average G+C (or A+G) content of total CDSs (or a subset) of each genome published in Genbank (dada presented in Fig 6a2 and Table 5). The deviations of ACAA for each amino acid in one bacterium (or one CDS set) were obtained by deducting the average value of the same amino acid in all bacteria (or all CDS sets) compared. The data were presented in Figure 6a1, b1, and c1. The deviation of GC content in each bacterium (or a group of bacteria, a CDS set) was calculated by deducting the average GC content of all genomes (Fig 6b2 and Fig 5c2). T-test of R package was used to calculate the difference as well as the p-value in ACAA and GC content, between the cold-adapted and warm adapted groups of marine γ-proteobacteria (or Shewanella) (Table 5). The cold-adapted Shewanella included S. halifaxensis, S. pealeana, S. sediminis, S. woodyi, and S. frigidimarina. The other 12 strains of Shewanella (as listed in Table 1) were considered as warm-adapted. A similar approach was applied to orthologous proteins (or genes) among 1) marine γ-proteobacteria, 2) 17 strains of Shewanella), 3) CDSc, CDS4, CDS2 and CDS1 set of S. halifaxensis and S. sediminis.

RDX Metabolic Activities in Shewanella spp

Shewanella spp (see below) were grown for 19 h anaerobically in MB-20 medium (peptone, 16 g L−1; yeast extract, 4 g L−1; sea salts, 40 g L−1; pH 7.3; Tris, 20 mM) in the presence of TMAO (100 mM) as previously described [48]. Cells were harvested by centrifugation and washed twice with 4% sea salts (pH 7.2), followed by re-suspension in the same sea salts solution. The reaction solution contained 90 µM RDX, 4.8–5.8 OD600 of cells and a pH of 7.5 (OD600 of cell suspensions: S. halifaxensis 5.1; S. pealeana, 5.6; S. sediminis, 4.8; S. woodyi, 5.1; Shewanella hanedai, 5.8). All solutions used were degassed and placed under argon prior to use. Tests were incubated at 10°C, 150 rpm, away from light, and run in triplicate. Rates (nM h−1) were measured based on removal of RDX within the first 5 hours of reaction.

S. halifaxensis Growth on RDX as the Sole Terminal Electron Acceptor

Growth of S. halifaxensis on RDX was carried out in serum bottles (60-mL, autoclaved prior to use) containing MB-20 marine medium (sterilized by passing through a 0.22 µm sterile filter membrane, 50 mL, no TMAO). RDX powder (50 mg) was added to above bottles for an oversaturated concentration of 1000 mg L−1. The serum bottles were sealed and made anaerobic by repeated degassing and charging with argon. S. halifaxensis cells pre-grown aerobically in MB-20 medium at 10°C were inoculated into above anaerobic media in the serum bottles through syringes. The initial OD600 in all bottles were controlled at a value close to 0.1. The cultures were incubated anaerobically at 10°C, 150 rpm, and away from light. To monitor bacterial growth, 1 mL of culture was sampled periodically in the anaerobic glove box; the samples were diluted using sterile 4% sea salts and plated on the MB-20 agar plates (MB-20 medium solidified with 15 g L-1 agar). The colonies were counted after 6 days of aerobic incubation at 10°C. Controls were also prepared in the same manner as described above, except no RDX was used in the medium. All tests were run in triplicate.

RDX Reaction with Cytochrome from S. halifaxensis and Saccharomyces cerevisiae

All of the following steps for cytochrome isolation from S. halifaxensis were carried out in an anaerobic glove box using anaerobic solutions where applicable. The periplasmic proteins were prepared from whole cells using a protocol as described previously [59]. Total cytochromes were precipitated from 75 mL of periplasmic protein solution with 45–65% (NH4)2SO4 saturation [65]. The precipitate was harvested by centrifugation at 20,000 g for 30 min, and re-suspended in 7.5 mL of TDG buffer containing 20 mM Tris-HCl, 5 mM dithiothreitol (DTT) and 10% glycerol (pH 7.1). The latter solution was desalted using a PD-10 desalting column (GE Healthcare) and TDG buffer according to the manufacturer's instructions. The above suspension (1.5 mL) was separated by gravity flow on the Q Sepharose Fast Flow Resin (GE Healthcare) (7.6 mL bed volume, 15 mm in diameter×53 mm in height). Twenty four milliliters of each of the following NaCl TDG buffer solutions was used as an elutant: 0.00, 0.05 (A), 0.10 (B) and 0.20 (C), 0.30 (D), 0.40 (E) and 0.6 (F) mol L−1. Fractions between 4 mL and 16 mL (12 ml in total) were collected and condensed using a Microcon centrifugal filter device (Ultracel YM-10, Millipore) to 0.8 mL for subsequent analysis and RDX reaction. The SDS-PAGE analyses, heme-staining and scanning of cytochrome UV-visible spectra were conducted as previously described [59].

The above prepared cytochrome c and from S. cerevisiae (Sigma, 86% purity) were tested for RDX degradation activity under the following assay conditions. All buffer, stock solutions of RDX, cytochrome and NADH were made anaerobic by repeated degassing and charging with argon before use in the anaerobic glove box for preparation of the reaction medium. The anaerobic reaction solutions were composed of cytochrome c, NADH (Sigma, 98% purity) (1 mM), and RDX in serum bottles (6-mL) in the following amount [organism, reaction volume in µl, cytochrome concentration in mg mL−1, reaction time in h, initial RDX conc as mg L−1]: S. cerevisiae, 750, 0.11, 23, 26. S. halifaxensis, 500, 0.15, 5, 5.5. All ran in duplicate at 23°C at 90 rpm (away from light). RDX was also incubated in two controls: one contained no NADH and another contained no cytochrome. The headspace (250 µL) was sampled for N2O analysis by GC and the liquid phase for analysis RDX and metabolites as previously described [12].

Proteomic Approach for Identification of c-Cytochrome

The SDS-PAGE band containing the 52 kDa cytochrome, once cut, was in-gel digested with Trypsin and subjected to LC-MS/MS analysis carried out in the Genome Quebec Proteomics facility. The peptide extracts were desalted on-line with a Zorbax C18 5×0.8 mm trapping column (Agilent) prior to injection onto a 10×0.75 mm Biobasic Picofrit column (New Objective). The gradient used was from 10 to 100% Solvent B (95% acetonitrile: 0.1% Formic acid) in 30 minutes. Tandem mass spectrometry analysis was done with a MicroQtof (Waters) using data directed acquisition. All MS/MS data was peaklisted with Mascot distiller v2.1 and peptide identification was carried out using Mascot v2.1 (Matrix Science, London, UK). The mascot .dat files were imported into Scaffold (Scaffold_2_02_03, Proteome Software Inc., Portland) and an X! Tandem (www.thegpm.org; version 2007.01.01.1) search was carried out. The searches were done on a subset of the NCBI nr database from 20081006 filtered for bacterial sequences (3568264 sequences). Search tolerances of 0.50 Da for the parent mass and 0.50 Da for fragment mass was set for both Mascot and X1Tandem searches. Carbamidomethylation of cysteine was set as fixed modification and oxidation of methionines as variable modification. Scaffold was used to validate MS/MS based peptide and protein identifications so as to generate a list of protein identifications that satisfy the rules of parsimony. Protein identifications were accepted if they could be established at greater than 90.0% probability as specified by the Peptide Prophet algorithm [66] and contained at least 1 identified peptide. Protein probabilities were assigned by the Protein Prophet algorithm [67].

Supporting Information

Figure S1.

S. halifaxensis genes of lateral transfer. The gene's function, CDS set (h1 = CDS1, h2 = CDS2, h4 = CDS4, h17 = CDSc), and most closely related non-Shewanella bacteria can be read by pointing mouse on any selected gene. The cog legends on the upper right corner were generated during preparation of the map and do not indicate the functions of the genes. Instead, the color of Q, P, E or I corresponds to CDS1, CDS2, CDS4, or CDSc, respectively. The light blue arrows mark genes on the reverse strand, and red arrows mark genes on forward strand of DNA.

doi:10.1371/journal.pone.0009109.s001

(8.99 MB XML)

Figure S2.

S. sediminis genes of lateral transfer. The gene's function, CDS set (h1 = CDS1, h2 = CDS2, h4 = CDS4, h17 = CDSc), and most closely related non-Shewanella bacteria can be read by pointing mouse on any selected gene. The cog legends on the upper right corner were generated during preparation of the map and do not indicate the functions of the genes. Instead, the color of Q, P, E or I corresponds to CDS1, CDS2, CDS4, or CDSc, respectively. The light blue arrows mark genes on the reverse strand, and red arrows mark genes on forward strand of DNA.

doi:10.1371/journal.pone.0009109.s002

(9.71 MB XML)

Acknowledgments

The authors acknowledge the critical reading of the manuscript by Drs Jim K. Fredrickson and Margaret F Romine. LC-MS/MS and proteomic analyses were performed by Dr Marcos Di Falco and Proteomics Platform of the McGill University and Genome Quebec Innovation Centre.

Author Contributions

Conceived and designed the experiments: JSZ. Performed the experiments: JSZ YD DM. Analyzed the data: JSZ. Contributed reagents/materials/analysis tools: JSZ YD JH. Wrote the paper: JSZ JH.

References

  1. 1. Beddington J, Kinloch AJ (2005) Munitions dumped at sea: a literature review. London: IC Consultants Ltd). Available at: http://www.mod.uk/NR/rdonlyres/77CEDBCA-​813A-4A6C-8E59-16B9E260E27A/0/ic_munitio​ns_seabed_rep.pdf.
  2. 2. Darrach MR, Chutjian A, Plett GA (1998) Trace explosives signatures from World War II unexploded undersea ordnance. Environ Sci Technol 32: 1354–1358.
  3. 3. USEPA (United States Environmental Protection Agency) (2000) Used or Fired Munitions and Unexploded Ordnance at Closed, Transferred, and Transferring Military Ranges. . Report and Analysis of EPA Survey Results. Washington DC: Office of Solid Waste and Emergency Response. (EPA-505-R-00-01).
  4. 4. Robidoux PY, Svendsen C, Caumartin J, Hawari J, Ampleman G, et al. (2000) Chronic toxicity of energetic compounds in soil determined using the earthworm (Eisenia Andrei) reproduction test. Environ Toxicol Chem 19: 1764–1773.
  5. 5. Talmage SS, Opresko DM, Maxwell CJ, Welsh CJE, Cretella FM, et al. (1999) Nitroaromatic munition compounds: environmental effects and screening values. Rev Environ Contam Toxicol 161: 1–156.
  6. 6. Rosemond ZA, Wong D (1998) Toxicological Profile for 2,4- and 2,6 Dinitrotoluene. Atlanta: Division of Toxicology / Toxicology Information Branch, Agency for Toxic Substances and Disease Registry.
  7. 7. Hau HH, Gralnick JA (2007) Ecology and Biotechnology of the Genus Shewanella. Annu Rev Microbiol 61: 237–258.
  8. 8. Nealson KH, Scott JH (2005) Ecophysiology of the genus Shewanella. In: Dworkin M, Falkow S, Rosenberg E, Schleifer K-H, Stackebrandt E, editors. The Prokaryotes: A Handbook on the Biology of Bacteria. Vol. 6. New York: Springer. pp. 1133–1151. Proteobacteria: Gamma Subclass.
  9. 9. Venkateswaran K, Moser DP, Dollhopf ME, Lies DP, Saffarini DA, et al. (1999) Polyphasic taxonomy of the genus Shewanella and description of Shewanella oneidensis sp. nov. Int J Syst Bacteriol 49: 705–724.
  10. 10. Picardal FW, Arnold RG, Couch H, Little AM, Smith ME (1993) Involvement of cytochromes in the anaerobic biotransformation of tetrachloromethane by Shewanella putrefaciens 200. Appl Environ Microbiol 59: 3763–3770.
  11. 11. Marshall MJ, Beliaev AS, Dohnalkova AC, Kennedy DW, Shi L, et al. (2006) C-type cytochrome-dependent formation of U(IV) nanoparticles by Shewanella oneidensis. PLoS Biol 4: 1324–1333.
  12. 12. Zhao J-S, Spain J, Thiboutot S, Ampleman G, Greer C, et al. (2004) Phylogeny of cyclic nitramine-degrading psychrophilic bacteria in marine sediment and their potential role in the natural attenuation of explosives. FEMS Microbiol Ecol 49: 349–357.
  13. 13. Keigwin LD, Sachs JP, Rosenthal Y (2003) A 1600-year history of the Labrador Current off Nova Scotia. Clim Dyn 21: 53–62.
  14. 14. Zhao J-S, Manno D, Beaulieu C, Paquet L, Hawari J (2005) Shewanella sediminis sp. nov., a novel Na+-requiring and hexahydro-1,3,5-trinitro-1,3,5-triazine-​degradingbacterium from marine sediment. Int J Syst Evol Microbiol 55: 1511–1520.
  15. 15. Zhao J-S, Manno D, Hawari J (2006) Shewanella halifaxensis sp. nov, a novel obligately respiratory and denitrifying psychrophile. Int J Syst Evol Microbiol 56: 205–212.
  16. 16. Yang H, Zhao J-S, Hawari J (2009) Effect of 2,4-dinitrotoluene on the anaerobic bacterial community in marine sediment. J Appl Microbiol 107: 1799–1808.
  17. 17. Crocker FH, Indest KJ, Fredrickson HL (2006) Biodegradation of the cyclic nitramine explosives RDX, HMX, and CL-20. Appl Microbiol Biotechnol 73: 274–290.
  18. 18. Makemson JC, Fulayfil NR, Landry W, Van Ert LM, Wimpee CF, et al. (1997) Shewanella woodyi sp. nov., an exclusively respiratory luminous bacterium isolated from the Alboran Sea. Int J Syst Bacteriol 47: 1034–1039.
  19. 19. Leonardo MR, Moser DP, Barbieri E, Brantner CA, MacGregor BJ, et al. (1999) Shewanella pealeana sp. nov., a member of the microbial community associated with the accessory nidamental gland of the squid Loligo pealei. Int J Syst Bacteriol 49: 1341–1351.
  20. 20. Deming JW, Somers LK, Straube WL, Swartz DG, MacDonell MT (1988) Isolation of an obligately barophilic bacterium and description of a new genus, Colwellia gen. nov. Syst Appl Microbiol 10: 152–160.
  21. 21. Nogi Y, Masui N, Kato C (1998) Photobacterium profundum sp. nov., a new, moderately barophilic bacterial species isolated from a deep-sea sediment. Extremophiles 2: 1–71.
  22. 22. Médigue C, Krin E, Pascal G, Barbe V, Bernsel A, et al. (2005) Coping with cold: the genome of the versatile marine Antarctica bacterium Pseudoalteromonas haloplanktis TAC125. Genome Res 15: 1325–35.
  23. 23. Akagawa-Matsushita M, Matsuo M, Koga Y, Yamasato K (1992) Alteromonas atlantica sp. nov. and Alteromonas carrageenovora sp. nov., bacteria that decompose algal polysaccharides. Int J Syst Bacteriol 42: 621–627.
  24. 24. Gauthier G, Gauthier M, Christen R (1995) Phylogenetic analysis of the genera Alteromonas, Shewanella , and Moritella using genes coding for small-subunit rRNA sequences and division of the genus Alteromonas into two genera, Alteromonas (emended) and Pseudoalteromonas gen. nov., and proposal of twelve new species combinations Int J Syst Bacteriol 45: 755–61.
  25. 25. Bowman JP, McCammon SA, Nichols DS, Skerratt JH, Rea SM, et al. (1997) Shewanella gelidimarina sp. nov. and Shewanella frigidimarina sp. nov., novel Antarctic species with the ability to produce eicosapentaenoic acid (20 : 5v3) and grow anaerobically by dissimilatory Fe(III) reduction. Int J Syst Bacteriol 47: 1040–1047.
  26. 26. Venkateswaran K, Dollhopf ME, Aller R, Stackebrandt E, Nealson KH (1998) Shewanella amazonensis sp. nov., a novel metal-reducing facultative anaerobe from Amazonian shelf muds. Int J Syst Bacteriol 48: 965–972.
  27. 27. Gao H, Obraztova A, Stewart N, Popa R, Fredrickson JK, et al. (2006) Shewanella loihica sp. nov., isolated from iron-rich microbial mats in the Pacific Ocean. Int J Syst Evol Microbiol 56: 1911–1916.
  28. 28. Dobrindt U, Hochhut B, Hentschel U, Hacker J (2004) Genomic islands in pathogenic and environmental microorganisms. Nat Rev Microbiol 2: 414–424.
  29. 29. Jain R, Rivera MC, Moore JE, Lake JA (2003) Horizontal gene transfer accelerates genome innovation and evolution. Mol Biol Evol 20: 1598–1602.
  30. 30. Simonson AB, Servin JA, Skophammer RG, Herbold CW, Rivera MC, et al. (2005) Decoding the genomic tree of life. Proc Natl Acad Sci U S A 102: 6608–6613.
  31. 31. Häse CC, Fedorova ND, Galperin MY, Dibrov PA (2001) Sodium ion cycle in bacterial pathogens: evidence from cross-genome comparison. Microbiol Mol Biol Rev 65: 353–370.
  32. 32. Yancey PH, Clark ME, Hand SC, Bowlus RD, Somero GN (1982) Living with water stress: Evolution of osmolyte systems. Science 217: 1214–1222.
  33. 33. Kempf B, Bremer E (1998) Uptake and synthesis of compatible solutes as microbial stress responses to high-osmolality environments. Arch Microbiol 170: 319–330.
  34. 34. Makemson JC, Hastings JW (1979) Glutamate functions in osmoregulation in a marine bacterium. Appl Environ Microbiol 38: 178–180.
  35. 35. Padana E, Venturib M, Gerchmana Y, Dover Nir (2001) Na+/H+ antiporters. Biochim Biophy Acta 1505: 144–157.
  36. 36. Wiebe CA, Dibattista ER, Fliegel L (2001) Functional role of polar amino acid residues in Na+/H+ exchangers. Biochem J 357: 1–10.
  37. 37. Laussermair E, Schwarz E, Oesterhelt D, Reinke H, Beyreuther K, et al. (1989) The sodium ion translocating oxaloacetate decarboxylase of Klebsiella pneumoniae. Sequence of the integral membrane-bound subunits β and γ. J Biol Chem 264: 14710–14715.
  38. 38. Hayashi M, Nakayama Y, Unemoto T (2001) Recent progress in the Na+-translocating NADH-quinone reductase from the marine Vibrio alginolyticus. Biochim Biophy Acta 1505: 37–44.
  39. 39. Schleheck D, Tindall B, Rossello-Mora R, Cook AM (2004) Parvibaculum lavamentivorans gen. nov., sp. nov., a novel heterotroph that initiates catabolism of linear alkylbenzenesulfonate. Int J Syst Evol Microbiol 54: 1489–1497.
  40. 40. Pfennig N, Truper HG (1971) Type and neotype strains of the species of phototrophic bacteria maintained in pure culture. Int J Syst Bacteriol 21: 19–24.
  41. 41. Watanabe K, Chishiro K, Kitamura K, Suzuki Y (1991) Proline Residues Responsible for Thermostability Occur with High Frequency in the Loop Regions of an Extremely Thermostable Oligo- 1,6-glucosidase from Bacillus thermoglucosidasius KP1006 J Biol Chem 266: 24287–24294.
  42. 42. Zhu GP, Xu C, Teng MK, Tao LM, Zhu XY, et al. (1999) Increasing the thermostability of D-xylose isomerase by introduction of a proline into the turn of a random coil. Protein Eng 12: 635–638.
  43. 43. Perl D, Mueller U, Heinemann U, Schmid FX (2000) Two exposed amino acid residues confer thermostability on a cold shock protein. Nat Struct Biol 7: 380–383.
  44. 44. Gerday C, Aittaleb M, Bentahir M, Chessa J-P, Claverie P, et al. (2000) Cold-adapted enzymes: from fundamentals to biotechnology. TIBTECH 18: 103–107.
  45. 45. Leiros H-KS, Pey AL, Innselset M, Moe E, Leiros I, et al. (2007) Structure of phenylalanine hydroxylase from Colwellia psychrerythraea 34H; a monomeric cold active enzyme with local flexibility around the active site and high overall stability. J Biol Chem 282: 21973–21986.
  46. 46. Lonhienne T, Gerday C, Feller G (2000) Psychrophilic enzymes: revisiting the thermodynamic parameters of activation may explain local flexibility. Biochim Biophy Acta 1543: 1–10.
  47. 47. Gianese G, Argos P, Pascarella S (2001) Structural adaptation of enzymes to low temperatures. Protein Eng 14: 141–148.
  48. 48. Shi L, Deng S, Marshall MJ, Wang Z, Kennedy DW, et al. (2008) Direct Involvement of Type II Secretion System in Extracellular Translocation of Shewanella oneidensis Outer Membrane Cytochromes MtrC and OmcA. J Bacteriol 190: 5512–5516.
  49. 49. Myers CR, Myers JM (1997) Cloning and sequence of cymA, a gene encoding a tetraheme cytochrome c required for reduction of iron(III), fumarate, and nitrate by Shewanella putrefaciens MR-1. J Bacteriol 179: 1143–1152.
  50. 50. Gralnick JA, Vali H, Lies DP, Newman DK (2006) Extracellular respiration of dimethyl sulfoxide by Shewanella oneidensis strain MR-1. Proc Natl Acad Sci U S A 103: 4669–4674.
  51. 51. Gralnick JA, Newman DK (2007) Extracellular respiration, Mol Microbiol 65: 1–11.
  52. 52. Myers CR, Myers JM (2003) Cell surface exposure of the outer membrane cytochromes of Shewanella oneidensis MR-1. Lett Appl Microbiol 37: 254–258.
  53. 53. Myers CR, Myers JM (2004) The outer membrane cytochromes of Shewanella oneidensis MR-1 are lipoproteins. Lett Appl Microbiol 39: 466–470.
  54. 54. Hartshorne RS, Jepson BN, Clarke TA, Field SJ, Fredrickson J, et al. (2007) Characterization of Shewanella oneidensis MtrC: a cell-surface decaheme cytochrome involved in respiratory electron transport to extracellular electron acceptors. J Biol Inorg Chem 12: 1083–1094.
  55. 55. Xiong Y, Shi L, Chen B, Mayer MU, Lower BH, et al. (2006) High-affinity binding and direct electron transfer to solid metals by the Shewanella oneidensis MR-1 outer membrane c-type cytochrome. OmcA. J Am Chem Soc 128: 13978–13979.
  56. 56. Jackson RG, Rylott EL, Fournier D, Hawari J, Bruce NC (2007) Exploring the biochemical properties and remediation applications of the unusual explosive-degrading P450 system XplA/B. Proc Natl Acad Sci U S A 104: 16822–16827.
  57. 57. Bhushan B, Trott S, Spain JC, Halasz A, Paquet L, et al. (2003) Biotransformation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by a rabbit liver cytochrome P450: insight into the mechanism of RDX biodegradation by Rhodococcus sp. strain DN22. Appl Environ Microbiol 69: 1347–1351.
  58. 58. Kwon MJ, Finneran KT (2006) Microbially-mediated biodegradation of hexahydro-1,3,5-trinitro-1,3,5-triazine by extra-cellular electron shuttling compounds. Appl Environ Microbiol 72: 5933–5941.
  59. 59. Zhao J-S, Manno D, Hawari J (2008) Regulation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) metabolism in Shewanella halifaxensis HAW-EB4 by terminal electron acceptor and involvement of c-type cytochrome. Microbiology (SGM) 154: 1026–1037.
  60. 60. Bryant C, DeLuca M (1991) Purification and characterization of an oxygen-insensitive NAD(P)H nitroreductase from Enterobacter cloacae. J Biol Chem 266: 4119–4125.
  61. 61. Kitts CL, Green CE, Otley RA, Alvarez MA, Unkefer PJ (2000) Type I nitroreductases in soil enterobacteria reduce TNT (2,4,6,-trinitrotoluene) and RDX (hexahydro-1,3,5-trinitro-1,3,5-triazine​). Can J Microbiol 46: 278–282.
  62. 62. Williams RE, Rathbone DA, Scrutton NS, Bruce NC (2004) Biotransformation of explosives by the old yellow enzyme family of flavoproteins. Appl Environ Microbiol 70: 3566–3574.
  63. 63. Darling ACE, Mau B, Blattner FR, Perna NT (2004) Mauve: Multiple alignment of conserved genomic sequence with rearrangements. Genome Res 14: 1394–1403.
  64. 64. Stothard P, Wishart DS (2005) Circular genome visualization and exploration using CG View. Bioinformatics 21: 537–539.
  65. 65. Rosenberg IM (1996) Protein analysis and purification:benchtop techniques (Birkhäuser, Boston, Massachusetts).
  66. 66. Keller A, Nesvizhskii AI, Kolker E, Aebersold R (2002) 74. : 5383–92. Empirical statistical model to estimate the accuracy of peptide identifications made by MS/MS and database search, Anal Chem.
  67. 67. Nesvizhskii AI, Keller A, Kolker E, Aebersold R (2003) A statistical model for identifying proteins by tandem mass spectrometry. Anal Chem 75: 4646–58.
  68. 68. Kumar S, Tamura K, Nei M (2004) MEGA3: integrated software for molecular evolutionary genetics analysis and sequence alignment. Brief Bioinform 5: 150–163.
  69. 69. Tatusov RL, Fedorova ND, Jackson JD, Jacobs AR, Kiryutin B[2003] The COG database: an updated version includes eukaryotes. BMC Bioinformatics 4: 41. doi:10.1186/1471-2105-4-41.
  70. 70. Brettar I, Christen R, Höfle MG (2002) Shewanella denitrificans sp. nov., a vigorously denitrifying bacterium isolated from the oxic–anoxic interface of the Gotland Deep in the central Baltic Sea. Int J Syst Evol Microbiol 52: 2211–2217.
  71. 71. Brettar I, Moore ERB, Höfle MG (2001) Phylogeny and abundance of novel denitrifying bacteria isolated from the water column of the central Baltic Sea. Microb Ecol 42: 295–305.