Genomic and microarray analysis of aromatics degradation in Geobacter metallireducens and comparison to a Geobacter isolate from a contaminated field site
© Butler et al; licensee BioMed Central Ltd. 2007
Received: 30 October 2006
Accepted: 19 June 2007
Published: 19 June 2007
Groundwater and subsurface environments contaminated with aromatic compounds can be remediated in situ by Geobacter species that couple oxidation of these compounds to reduction of Fe(III)-oxides. Geobacter metallireducens metabolizes many aromatic compounds, but the enzymes involved are not well known.
The complete G. metallireducens genome contained a 300 kb island predicted to encode enzymes for the degradation of phenol, p-cresol, 4-hydroxybenzaldehyde, 4-hydroxybenzoate, benzyl alcohol, benzaldehyde, and benzoate. Toluene degradation genes were encoded in a separate region. None of these genes was found in closely related species that cannot degrade aromatic compounds. Abundant transposons and phage-like genes in the island suggest mobility, but nucleotide composition and lack of synteny with other species do not suggest a recent transfer. The inferred degradation pathways are similar to those in species that anaerobically oxidize aromatic compounds with nitrate as an electron acceptor. In these pathways the aromatic compounds are converted to benzoyl-CoA and then to 3-hydroxypimelyl-CoA. However, in G. metallireducens there were no genes for the energetically-expensive dearomatizing enzyme. Whole-genome changes in transcript levels were identified in cells oxidizing benzoate. These supported the predicted pathway, identified induced fatty-acid oxidation genes, and identified an apparent shift in the TCA cycle to a putative ATP-yielding succinyl-CoA synthase. Paralogs to several genes in the pathway were also induced, as were several putative molybdo-proteins. Comparison of the aromatics degradation pathway genes to the genome of an isolate from a contaminated field site showed very similar content, and suggested this strain degrades many of the same compounds. This strain also lacked a classical dearomatizing enzyme, but contained two copies of an eight-gene cluster encoding redox proteins that was 30-fold induced during benzoate oxidation.
G. metallireducens appears to convert aromatic compounds to benzoyl-CoA, then to acetyl-CoA via fatty acid oxidation, and then to carbon dioxide via the TCA cycle. The enzyme responsible for dearomatizing the aromatic ring may be novel, and energetic investments at this step may be offset by a change in succinate metabolism. Analysis of a field isolate suggests that the pathways inferred for G. metallireducens may be applicable to modeling in situ bioremediation.
Some bacteria can metabolize the toxic aromatic compounds that are present in groundwater contaminated by petroleum or by landfill leachate [1–4]. The bacteria use these contaminants as the carbon and energy sources for growth, and they can oxidize many aromatic compounds completely to carbon dioxide. Both the species that accomplish this bioremediation and the mechanism with which they degrade these stable compounds are being investigated.
The benzene-ring structure of aromatic compounds must be dearomatized before they can be fully degraded. While oxygen can be used to attack the ring, many contaminated environments are anaerobic, so a different mechanism is needed . The best-studied anaerobic species that catalyze this reaction couple the oxidation of aromatics to the reduction of high potential compounds like nitrate [4, 6, 7]. This metabolism provides enough energy to allow the dearomatization of the benzene-ring by an enzyme that uses two ATP and two low potential electrons instead of oxygen [8–10].
However, insoluble Fe(III)-oxides are the primary electron acceptor in many contaminated environments [11–14], and the energy gained from reducing Fe(III)-oxides (ΔE°' ≅ 200 mV) is less than that from nitrate (ΔE°' = 420 mV). It has been suggested that bacteria that use lower potential electron acceptors like Fe(III) or sulfate, or bacteria that ferment aromatic compounds, require a less energetically expensive mechanism to dearomatize the aromatic ring [15–17]. These enzymes have not yet been identified.
Molecular analyses have shown that members of the Geobacter family are the most abundant species in contaminated environments where Fe(III) is the electron acceptor [14, 18, 19]. Geobacter metallireducens was the first pure-culture organism found to anaerobically oxidize an aromatic hydrocarbon, toluene . This species is also able to completely oxidize the aromatic compounds phenol, p-cresol, 4-hydroxybenzaldehyde, 4-hydroxybenzoate, benzyl alcohol, benzaldehyde, and benzoate, all with Fe(III) serving as the sole electron acceptor [20, 21].
Two recent studies sought to identify enzymes involved in benzoate oxidation in G. metallireducens, specifically the enzyme that catalyzes the dearomatization of the benzene-ring [22, 23]. Comparison of protein abundance in G. metallireducens growing by benzoate versus acetate oxidation identified 14 proteins that were more abundant during benzoate metabolism . The genes encoding these proteins were located on two contigs in the partially completed G. metallireducens genome, and an additional 19 nearby genes were shown to have increased transcript levels in the presence of benzoate compared to acetate . Several of the induced genes and proteins had clear sequence homology to those that catalyze benzoate metabolism in the nitrate-reducer Thauera aromatica, with one exception. No proteins similar to known benzoyl-CoA reductases, the enzyme that catalyzes the ring reduction, were found to have increased expression during benzoate oxidation, and no benzoyl-CoA reductase activity was detected in cell extracts .
A separate study suggests that genes for a benzoyl-CoA reductase were present elsewhere in the G. metallireducens genome . Degenerate primers were designed from known benzoyl-CoA reductase α subunits, and used to amplified sequence from G. metallireducens genomic DNA . Analysis of the corresponding gene and its flanking region led to the conclusion that the gene was the α subunit of the benzoyl-CoA reductase. The same analysis was done with a Geobacter species that cannot degrade aromatic compounds, and no such gene could be amplified .
The aim of this study is to use the completed genome sequence of G. metallireducens to predict the pathways for degradation of toluene, phenol, p-cresol, 4-hydroxybenzaldehyde, 4-hydroxybenzoate, benzyl alcohol, benzaldehyde, and benzoate. Support for the predicted pathways is provided by analysis of genome-wide changes in transcript levels by DNA microarray in cells oxidizing benzoate. The relevance of the G. metallireducens pathways to in situ environmental bioremediation is examined by comparison to a recently sequenced Geobacter isolate from a contaminated site.
Results and discussion
The 300 kb island of aromatics-degradation genes
The two gene clusters previously identified as encoding proteins and genes with increased expression during benzoate oxidation  were encoded ca. 60 kb apart in the completed genome (see Additional file 1) (accession NC_007517) . These clusters were part of a 300 kb, 244-gene region (Gmet_2037-Gmet_2284) in which very few of the encoded proteins had orthologs in the genome of G. sulfurreducens, a closely related Geobacter species that cannot metabolize aromatic compounds (see Additional file 1). Orthologs were defined as proteins that were reciprocal best matches when all proteins from both genomes were aligned, with a minimum alignment of 60% of both proteins. Across the whole G. metallireducens genome, 2130 proteins (60.3%) had orthologs in G. sulfurreducens, but in this region of the genome only 20 (8%) had orthologs in the G. sulfurreducens genome (see Additional file 1).
When the 244 proteins encoded in this region were aligned against the entire non-redundant protein database from NCBI, many had highest sequence similarity to enzymes involved in aromatics degradation in the nitrate-reducing organisms Thauera aromatica and Azoarcus sp. EbN1 (see Additional file 1). However, the overall organization of the genes in the island was not found to be conserved when compared to any other organism. Analysis of the composition and structure of this region is discussed below.
Phenol, p-cresol, 4-hydroxybenzaldehyde, 4-hydroxybenzoate, benzyl alcohol, and benzaldehyde metabolism
In previously studied bacteria, p-cresol is metabolized by conversion to 4-hydroxybenzoate via 4-hydroxybenzaldehyde. A flavocytochrome p-cresol methylhydroxylase creates 4-hydroxybenzaldehyde, which is then oxidized via a 4-hydroxybenzaldehyde dehydrogenase [28, 29]. In G. metallireducens, homologs to the two-subunit methylhydroxylase (Gmet_2125-Gmet_2126) are encoded just upstream of the putative dehydrogenase (Gmet_2131), all within the aromatics island of the genome (Figure 1, Additional file 1). These genes have high sequence similarity to those in Azoarcus-related species and Pseudomonas putida [28, 29].
In T. aromatica, 4-hydroxybenzoate, benzyl alcohol, and benzaldehyde are all metabolized to the central intermediate benzoyl-CoA. 4-hydroxybenzoate is converted via a Co-A ligase and a well-studied reductase . In G. metallireducens, a three-gene cluster in the aromatics island of the genome (Gmet_2134-Gmet_2136) had identical organization and high sequence similarity to the 4-hydroxybenzoyl-CoA reductase operon in T. aromatica (Figure 1, Additional file 1). In G. metallireducens, the dehydrogenase genes predicted to be responsible for the conversion of benzyl alcohol and benzaldehyde to benzoate (Gmet_2235 and Gmet_2131) have closest homologs to those enzymes in Azoarcus-related species and Pseudomonas species (Figure 1, Additional file 1) [29, 31]. The specificity of the CoA ligases for 4-hydroxybenzoate and benzoate is difficult to predict based on sequence identity alone. However, the benzoate CoA ligase (BclA) was previously identified and characterized , and in the completed genome is encoded by Gmet_2143 (Figure 1, Additional file 1).
The putative benzoyl-CoA reductase
The pathways that can be inferred from the analysis presented above predict that, like nitrate-reducing species, all of the aromatic compounds that G. metallireducens is capable of degrading are converted to the central metabolite benzoyl-CoA (Figure 1). However, benzoyl-CoA is still aromatic, and dearomatization of the benzene-ring structure is the central step in the degradation pathways. The enzyme that catalyzes this reaction in nitrate-reducing species, the benzoyl-CoA reductase, has been well studied [5, 9]. Previously, a gene predicted to encode this enzyme in G. metallireducens was identified (NCBI accession YP_383512) , and in the completed genome, this gene was encoded by Gmet_0544. This gene was not located in the aromatics island of the genome.
Examination of this gene, its closest phylogenetic relatives, and the adjacent genes indicate that this gene does not appear to be part of a classical benzoyl-CoA reductase. Gmet_0544 had highest amino acid identity to the ATP-binding activator subunit of 2-hydroxyglutaryl-CoA dehydratases, an enzyme involved in the fermentation of glutamate via the hydroxyglutarate pathway . Gmet_0544 was more similar to the characterized activator subunits from Clostridia symbiosum  and Acidaminococcus fermentans  (ca. 30%), than to the benzoyl-CoA reductase proteins from T. aromatica, Azoarcus species, or R. palustris (ca. 17%).
G. metallireducens proteins most similar to the benzoyl-CoA pathway proteins from T. aromaticaa
Benzoyl-CoA pathway protein
closest Gmet ORF
% a.a. ID
Metabolism of the non-aromatic products
In other anaerobic aromatics degraders the reduction of benzoyl-CoA produces cyclohexa-1,5-diene-1-carbonyl-CoA, which is then converted to 3-hydroxypimelyl-CoA . In G. metallireducens, homologs to the proteins that catalyze this conversion are expressed during benzoate oxidation . These genes, the cyclohexa-1,5-diene-1-carbonyl-CoA hydratase (dch, Gmet_2150), 6-hydroxycylohex-1-en-1-carbonyl-CoA dehydrogenase (had, Gmet_2151), and 6-oxocyclohex-1-ene-1-carbonyl-CoA hydratase (oah, Gmet_2088), are all located in the aromatics region of the genome (Table 1).
The 3-hydroxypimelyl-CoA that results from this pathway enters into the beta fatty acid oxidation pathway, where it is converted to acetyl-CoA . In G. metallireducens, there are several clusters in the aromatics island that encode genes predicted to be involved in fatty acid oxidation, including Gmet_2057-Gmet_2075, Gmet_2194-Gmet_2213, and Gmet_2268-Gmet_2270. Putative acyl-CoA dehydrogenases, enoyl-CoA hydratases, thiolases, and Co-A transferases were all present in multiple copies with high sequence similarities (see Additional file 1). However, unlike the other genes predicted to be involved in aromatics degradation in G. metallireducens, the closest homologs in the NCBI database are not from known aromatics degraders. Closest homologs to these genes were found in a variety of species including Clostridia, gamma Proteobacteria, and Actinobacteria (see Additional file 1).
Thus, while G. metallireducens lacks the central enzyme of the pathway, the ATP-dependent benzoyl-CoA reductase, it contains genes for the oxidation of the product of benzoyl-CoA reduction, including dch, had, oah, and fatty acid pathway genes (Figure 1).
Paralogs of the enzymes BamB, BamC, and Oah
It has been suggested that an uncharacterized protein called BamB (Gmet_2087) could be a possible alternative to the benzoyl-CoA reductase, because it was shown to be more abundant in benzoate-grown cells of G. metallireducens than cells grown on acetate . Analysis of the completed genome showed that there was a second protein with homology to BamB encoded outside of the aromatics island of the genome. Gmet_1802 encoded a protein of identical length to Gmet_2087, with 66% amino acid identity. This gene was encoded in a small region that lacked orthologs in G. sulfurreducens (Gmet_1784-Gmet_1815). This cluster also contained a close homolog to the putative Fe-S protein that is encoded upstream of bamB, called BamC. BamC and its paralogs (Gmet_1803) have 64% amino acid identity to each other.
A second enzyme predicted to be involved in the central part of the pathway of benzoate oxidation in G. metallireducens was also found to have a homologous gene outside of the aromatics region of the genome. Gmet_3305, with 86% amino acid identity to Oah (Gmet_2088) in the aromatics island, was found distant in the genome in a 30-gene region that lacked orthologs in G. sulfurreducens (Gmet_3280-Gmet_3309).
The organization and duplication of these central genes in the benzoyl-CoA pathway are unique to G. metallireducens. In T. aromatica, Azoarcus species, R. palustris, and Magnetospirillum magnetotacticum, the central genes in the pathway (the benzoyl-CoA reductase, Dch, Had, and Oah) are always encoded in a large cluster [7, 39, 40]. G. metallireducens lacks the reductase, and the roles of BamB and its newly identified homolog cannot be predicted based on sequence analysis alone. The dch and had genes are adjacent, but neither is near either of the two very similar oah homologs.
The toluene degradation genes
In addition to the aromatics compounds described above, G. metallireducens can also degrade the hydrocarbon toluene . The genes in G. metallireducens are similar to those for conversion of toluene to benzoyl-CoA in other organisms, and have been described previously (Figure 1) . There are two apparent operons encoded next to each other, for the benzylsuccinate synthase (bssCAB, Gmet_1538-Gmet_1540) and for benzylsuccinate oxidation to benzyl-CoA (bbsABCD, Gmet_1528-1531, and bbsEFGH, Gmet_1521-Gmet_1524). In the completed genome, these genes were not located near the other aromatics degradation genes. Instead, they were encoded 556 kb upstream, in a region that, like the large island, lacked orthologs in G. sulfurreducens. In this 167 kb region, Gmet_1435-Gmet_1572, only 25 of 133 genes (19%) had orthologs in the G. sulfurreducens genome.
Characterization of the large genomic island
Genes for aromatics degradation have been found as parts of catabolic transposons . In an effort to understand the origin of the aromatics degradation genes in G. metallireducens, analysis of local compositional heterogeneity and identification of potential mobile genetic elements were performed [43, 44].
Transposons and repetitive sequences
There were 9 transposase insertion sequence elements flanked with perfect inverted repeats (IS) in the large aromatics island (Figure 5). At the 3' end of the large aromatics island was a putative two gene transposase operon, Gmet_2272-Gmet_2273, of the istAB-type . Exact copies of this pair, with 100% nucleic acid identity including the flanking inverted repeats, were found in two other places in the genome: upstream of the bamB homolog (Gmet_1788-Gmet_1789), and upstream of the oah homolog (Gmet_3281-Gmet_3282).
The eight other IS elements in the large aromatics island were Gmet_2039, Gmet_2073, Gmet_2091, Gmet_2093, Gmet_2160, Gmet_2166, Gmet_2240, and Gmet_2284 (Figure 5). Based on sequence similarity, these transposons belong to a variety of families, including IS4, IS5, ISl3, IS21, and IS110 [45, 46]. Two pairs of these IS elements had 100% nucleic acid identity to each other (Gmet_2091 to Gmet_2240 and Gmet_2166 to Gmet_2284). These identical pairs could form a larger, composite transposon that would include all the intervening genes (Figure 5).
There was a 131 bp direct repeat in the aromatics island, with the left copy at the 5' end of the island between Gmet_2036 and Gmet_2037 (coordinates 2280680–2280810), and the right copy between Gmet_2166 and Gmet_2168 (Figure 5). There was also a 130 bp inverted repeat, with the left copy between Gmet_2092 and Gmet_2093 (coordinates 2280680–2280810), and the right copy within Gmet_2271 (Figure 5).
All four regions of aromatics metabolism genes were flanked on at least one side by tRNA genes. tRNA genes are often associated with genomic islands , and are often target sites for phage attachment and integration . The 3' end of the large aromatics island was flanked by a tRNA-Gly gene, and a pseudo tRNA was found 6.6 kb upstream (Figure 5). Three genes with homology to phage integrases were encoded nearby (Gmet_2271, Gmet_2278, Gmet_2279) (Figure 5).
There was a tRNA-Gly near the bamB homolog (Gmet_1802), as well as a putative phage integrase (Gmet_1783). The region that contained the oah homolog had a tRNA-Ala at the 5' end. The toluene region was flanked on both sides by tRNA genes: a tRNA-Met at the 5' end and a tRNA-Val at the 3' end.
Thus, the 300 kb region that contains the predicted aromatics degradation genes shows many of the hallmarks of genomic islands . The genes in these regions are species-specific; they have no orthologs in the closely related species, G. sulfurreducens, which cannot degrade aromatics. The genes are encoded in large, discrete units, flanked by genes with atypical nucleotide composition, tRNA genes, and phage-like integrases. The region shows signs of potential genetic mobility, including identical transposons and repetitive sequences. However, the genes predicted to be involved in aromatics metabolism do not have atypical composition compared to the rest of the genome, and they lack synteny with the genes from other aromatics degraders. This implies that if there were horizontal gene transfer event(s) from distantly related organisms, the genes have since ameliorated [43, 49].
Gene expression changes during benzoate metabolism
G. metallireducens genes for which transcription was induced at least 10-fold with benzoate as the sole electron and carbon donor, relative to acetate
Conserved hypothetical protein
Conserved hypothetical protein
Aldehyde ferredoxin oxidoreductase
Bacterial regulatory proteins, IclR
Succinyl-CoA synthetase, alpha
NAD(P) diaphorase, HoxF
NAD(P) diaphorase, HoxU
hydrogenase, delta subunit; HTH mo
4Fe-4S binding, FAD binding
4Fe-4S binding, cysteine rich
Aldehyde ferredoxin oxidoreductase
Electron transfer flavoprotein, alpha
Electron transfer flavoprotein, beta
Response regulator receiver
Succinyl-CoA synthetase, alpha sub
The Thauera-like benzoate pathway
Previously, 14 proteins were identified as having increased expression during benzoate oxidation in G. metallireducens . The microarray analysis identified increased transcript abundance in 13 of the genes that encode these proteins (see Additional file 2). 10 of these were among the very few ORFs in the genome that showed an increase of at least 10-fold during benzoate oxidation (Table 2).
The dch and had genes (Gmet_2150, Gmet_2151) were among the most strongly induced of all genes, with about 30-fold increase during benzoate oxidation (Figure 1, Table 2). Because the array was designed based on a draft version of the genome, a probe was created for only one of the two oah homologs, Gmet_3305. Like dch and had, this gene was found to be among the most strongly induced genes during benzoate oxidation, with a 27 fold change in transcript levels (Figure 1, Table 2). The other homolog to oah, Gmet_2088, has previously been shown to have increased expression during benzoate oxidation . Thus, it appears that both oah homologs have increased expression during benzoate oxidation.
The induced proteins  were encoded in two small clusters inside the aromatics island, and an additional 19 genes within these clusters have been shown by RT-PCR to be induced by benzoate oxidation . Microarray analysis identified 14 of these as induced during benzoate oxidation (see Additional file 2). In addition, microarray analysis also identified increases in transcript levels in several other genes in these two clusters that were not previously identified (see Additional file 2). Like the 13 genes identified by protein analysis, most of these genes were also at least 10-fold more abundant in benzoate oxidizing cells (Table 2). Transcripts for the benzoate-CoA ligase (Gmet_2143) had a smaller increase in abundance, 4.9 fold, than the other genes predicted to be involved in the benzoate oxidation pathway, (Figure 1, Additional file 2). Thus, microarray analysis of transcript abundance changes during benzoate oxidation reliably identified the genes predicted to be involved in benzoate oxidation (Figure 1).
Unlike the other genes in the predicted benzoyl-CoA pathway, the gene previously identified as the α subunit of the benzoyl-CoA reductase (Gmet_0544)  had no change in abundance during benzoate oxidation (see Additional file 2). Neither did any of the neighboring genes (see Additional file 2). This result supports the analysis presented earlier that shows that this gene is not likely to be part of the pathway of aromatics degradation, and is not the benzoyl-CoA reductase.
bamB and bamC homologs
Analysis of whole genome transcript changes during growth with benzoate showed that bamB had the second highest increase, 36.4-fold, of all genes (Table 2). In addition, the cluster of seven genes (Gmet_2080-Gmet_2087) that bamB was a part of was the most highly up-regulated cluster in the genome, ca. 25-fold (Figure 7, Table 2). As described above, a homolog to bamB was found outside the aromatics island of the genome. This homolog, Gmet_1802, also had a large increase in transcript levels, 23.6-fold, during growth on benzoate (Table 2). The cluster that contained bamB2 (Gmet_1795-Gmet_1810) was the only large gene cluster outside of the aromatics region that had a significant increase in transcript levels during growth on benzoate (see Additional file 2). Directly upstream of both bamB homologs were the homologous genes, bamC and bamC2, both encoding putative 4Fe-4S cluster proteins (Gmet_2086 and Gmet_1803). These genes were also induced more than 15-fold in the presence of benzoate (Table 2). Thus, like the two oah homologs, the two bamB and bamC homologs both have large increases in expression during growth by benzoate oxidation.
Fatty acid oxidation
The completed genome of G. metallireducens contained several copies of genes predicted to be involved in fatty acid oxidation. Only one set, Gmet_2057-Gmet_2075, had marked increases in abundance during benzoate oxidation (see Additional file 2). This set included the gene with the greatest increase in transcript levels during growth on benzoate, a 50-fold induced thiolase (Gmet_2074) (Table 2). Also induced more than 15-fold were another thiolase (Gmet_2058), two acyl-CoA dehydrogenases (Gmet_2072, Gmet_2075), and two enoyl-CoA hydratases (Gmet_2057, Gmet_2071) (Table 2). Thus, though there are several homologs to beta fatty acid oxidation genes in the genome, only one cluster showed increases in expression during benzoate oxidation (Figure 5).
Changes in the TCA cycle
The oxidation of one benzoate molecule via the benzoyl-CoA and fatty acid pathways results in three molecules of acetyl-CoA . Acetate, another electron donor used by Geobacter species, is also converted to acetyl-CoA. In G. sulfurreducens, acetyl-CoA is oxidized to carbon dioxide via TCA cycle reactions, and in G. metallireducens most of the TCA cycle enzymatic activities have also been identified [50, 51].
During growth with acetate as the electron donor, the TCA cycle of G. sulfurreducens does not include an ATP-yielding succinyl-CoA synthetase . In other organisms, this enzyme catalyzes the conversion of succinyl-CoA to succinate and produces the only substrate-level phosphorylation of the TCA cycle. Instead, in Geobacter species, an acetate:succinyl-CoA transferase is used to convert succinyl-CoA to succinate coupled to the activation of acetate to acetyl-CoA . Thus, there is no substrate-level ATP generation during acetyl-CoA oxidation.
However, analysis of the genome of G. metallireducens showed that there were three sets of genes predicted to encode the two-subunit ATP-yielding succinyl-CoA synthetase enzyme: Gmet_0729-Gmet_0730, Gmet_2068-Gmet_2069, and Gmet_2260-Gmet_2261. The latter two pairs were found in the aromatics island of the genome and shared 92% sequence identity (Supplementary Table 1). The third set of genes, Gmet_0729-Gmet_0730, was only ca. 55% identical to the pairs inside the aromatics island. At least one of the subunits of each of these pairs was shown to have increased transcript abundance during benzoate oxidation, with increases of 8 to 32 fold (see Additional file 2).
The ortholog in G. metallireducens to the acetate:succinyl-CoA transferase of G. sulfurreducens was encoded by Gmet_3044. This gene was one of the relatively few genes that had decreased abundance during benzoate oxidation, with a 2.2 fold decrease (see Additional file 2). When considered together, these two results – the decrease in the transferase gene and the increase in the synthetase genes – suggest that the enzyme that catalyzes the conversion of succinyl-CoA to succinate is changed when benzoate is the electron donor. Since the product of benzoate oxidation is likely acetyl-CoA and not acetate, there would be no need for an acetate:succinyl-CoA transferase. The exclusive use of a succinyl-CoA synthetase instead would allow for the generation of an ATP by substrate level phosphorylation for each of the three acetyl-CoA molecules predicted to be produced from benzoate oxidation.
Molybdenum has been shown to be required for benzoate oxidation in the sulfate-reducer D. multivorans, but is not required for nitrate-reducers . A recent study showed only a slight decrease in growth in G. metallireducens cultured without molybdenum supplementation, but these results were qualified due to molybdenum impurities in the growth media .
Several putative molybo-proteins had higher transcript levels during growth on benzoate in G. metallireducens (see Additional file 2). As described above, both of the BamB homologs (Gmet_2087 and Gmet_1802) are related to tungsto- and molybo-proteins, and both had ca. 30-fold induction during benzoate oxidation. Nearby bamB2 were genes for a putative molybdenum cofactor biosynthesis protein (Gmet_1804) with 4.5-fold higher transcript level during growth on benzoate, and for a putative molybdopterin oxidoreductase, Gmet_1810, with 2.0-fold induction (see Additional file 2). Though no 4-hydroxybenzoate was supplied to the cultures, the genes for the molybdo-enzyme 4-hydroxybenzoate reductase (Gmet_2134-Gmet_2136) had ca. 2.5-fold transcript levels during growth on benzoate (see Additional file 2). In addition, a putative nitrate reductase operon, also a molybdo-enzyme (Gmet_0329-Gmet_0334) had ca. 3-fold higher transcript levels during growth on benzoate, though no nitrate was supplied (see Additional file 2).
As mentioned above, the enzyme predicted to be required for acetate activation, an acetate-CoA transferase was down-regulated 2.2 fold in the absence of acetate (see Additional file 2). Two apparent operons were also down-regulated: Gmet_1380-Gmet_1381, encoding proteins similar to those involved in disulfide bond formation, and Gmet_1753-Gmet_1756, encoding proteins similar to the glutamate synthases found in methanogens (see Additional file 2). Two putative transcriptional regulators were down-regulated, one of which shows similarity to the IclR family of regulators involved in acetate metabolism in Escherichia coli . Also down-regulated were eight hypothetical or conserved hypothetical proteins (see Additional file 2).
Genes in a Geobacter species from an aromatics-contaminated field site
A strain of Geobacter was recently isolated from sediments from the Department of Energy's Field Research Center in Oak Ridge, Tennessee (Geobacter strain FRC-32, Joel Kostka, personal communication). This site is contaminated with uranium, metals, and fuel hydrocarbons including toluene, and bioremediation by in situ bacteria is being studied there. Geobacter species have been shown to be present in sediments from the site [53, 54], and the Geobacter population has been shown to increase by two orders of magnitude during stimulation of Fe(III) and uranium reduction . The draft sequence of the Geobacter strain FRC-32 genome has recently been released (NCBI Accession number AASH00000000). The sequence of the 16S rRNA gene of Geobacter strain FRC-32 is 99.4 – 99.8 % identical to the Geobacter 16S rRNA gene sequences cloned from the contaminated site . The genome is 4.0 Mb, with 3396 open reading frames in 164 contigs, each with sequence coverage of at least 10×.
To evaluate the possibility of extrapolating the predicted pathways of aromatics degradation in G. metallireducens to an environment of bioremediation, the genes from G. metallireducens were compared to those encoded in the Geobacter strain FRC-32 genome. Geobacter strain FRC-32 encoded proteins with high sequence similarity and orthology to those in G. metallireducens for the oxidation of toluene, phenol, p-cresol, 4-hydroxybenzoate, and benzoate (Figure 1, Additional file 1). As with G. metallireducens, these compounds are predicted to be funneled to the central intermediate of benzoyl-CoA. In Geobacter strain FRC-32, there were also very similar orthologs to Dch, Had, Oah, and the fatty acid proteins that had higher transcript levels during benzoate oxidation in G. metallireducens, indicating that the dearomatized intermediate could also be oxidized to 3-hydroxypimelyl-CoA then acetyl-CoA (Figure 1, Additional file 1).
The pathways of aromatics degradation in the Fe(III)-reducing, obligate anaerobe G. metallireducens appear to be similar to those from nitrate-reducing organisms that use more favorable electron acceptors. The genes are more closely related to those that have been studied in the nitrate-reducing beta Proteobacteria than to the nitrate-reducing or photosynthetic alpha Proteobacteria species. Toluene, phenol, p-cresol, 4-hydroxybenzaldehyde, 4-hydroxybenzoate, benzyl alcohol, benzaldehyde, and benzoate are all predicted to be channeled to the central intermediate benzoyl-CoA. De-aromatized products are predicted to be oxidized to 3-hydroxypimelyl-CoA.
However, there is one notable exception to this similarity. The reaction which has been shown to be the most energetically expensive in nitrate-reducing organisms, and which has been hypothesized to be different in obligate anaerobes, must be different in G. metallireducens. The completion of the genome sequence proves that G. metallireducens encodes no classical benzoyl-CoA reductase, the ATP-dependent enzyme that catalyzes the breaking of the aromatic bonds in benzoyl-CoA. Phylogenetic analysis, subunit content, and expression studies contradict the previous report that a benzoyl-CoA reductase was present in G. metallireducens, and support the previous report that no benzoyl-CoA reductase activity was found in G. metallireducens metabolizing benzoate.
The enzyme that dearomatizes benzoyl-CoA in G. metallireducens remains unknown. The 30-fold increase in transcript levels of the bamB-bamI cluster, and its phylogenetic relationship to genes in a benzoate-fermenter and in a field-isolate, support a role for these genes in benzoate oxidation. However, the lack of sequence similarity of these genes to characterized enzymes, and the discovery of highly induced paralogs in the genome indicate that further analysis of both sets of genes is necessary. Regardless of the mechanism, the dearomatization of benzoyl-CoA remains the most difficult step of the pathway, and G. metallireducens may offset energetic costs of this step by changing the way the acetyl-CoA produced by the pathway is oxidized.
The aromatics genes are organized in G. metallireducens in an island that shows substantial evidence of potential genetic mobility, and they are not found in closely related Geobacteraceae species that do not oxidize aromatic compounds. However, no evidence that these aromatics genes were recently transferred into the genome was found. The enzymes in the pathway up to the last step before fatty acid oxidation appear to be most similar to Thauera-like species, but the genes for fatty acid and TCA cycle oxidation, and the bamB-bamI cluster genes, though nearby, are more closely related to other organisms. Perhaps the genes were assembled in G. metallireducens from existing functional units into a new combination, as has been suggested for other catabolic pathways [55, 56]. The continued effort to sequence other environmentally relevant Geobacteraceae species should allow a more detailed reconstruction of the evolutionary history of the genes.
The motivation for analyzing the genes of aromatics metabolism in G. metallireducens is to better understand in situ bioremediation by bacteria . Similarity in the genes for aromatics degradation between G. metallireducens and the Geobacter species isolated from a toluene-contaminated bioremediation site suggests that the analyses presented here may be applied more broadly to the Geobacter community that predominates during bioremediation. A method for quantifying gene transcript levels in Geobacter species in the subsurface was recently developed [58, 59], but has yet to be applied to the metabolism of aromatics. Hopefully, these results provide candidates for this type of study, to help clarify the physiological state and metabolic rates of the in situ species during bioremediation.
Genome analysis and annotation of genes
The complete G. metallireducens genome sequence was acquired from NCBI (accession NC_007517) . Refinements of the automatically generated functional predictions for genes putatively involved in aromatics metabolism were made. Most similar sequences in other genomes were identified using BLASTp  with the non-redundant protein database  and UniProt . Identification of functional domains and motifs was made using InterPro . Transmembrane motifs and signal sequences were predicted with PsortB . Comparisons to characterized proteins from aromatics metabolism were made with BLASTp  and alignments were made with ClustalX . Phylogenetic relationships were inferred by distance based analysis using the neighbor joining method  in the Mega program . Orthologs were defined as reciprocal best matches from BLASTp between two genomes that aligned over at least 60% of their length [68, 69]. Total GC content, first codon position GC content and third codon position GC content were determined for each ORF in the genome using the cusp program in EMBOSS . Effective number of codons (Nc) used was determined for each ORF in the genome using the chips program in EMBOSS . Dinucleotide relative abundance difference with respect to the genome average was calculated using delta-rho . GC content and GC skew (G-C/G+C) were calculated in a window of 20 kb with a step size of 5 kb.
G. metallireducens from our laboratory culture collection was cultured at 30°C in electron donor limited chemostats as previously described . The dilution rate was 0.05 h-1 with acetate (5 mM) or benzoate (1.25 mM) provided as the electron donor and ferric citrate (55 mM) as the electron acceptor. Acetate concentrations were measured with HPLC (Bio-Rad Aminex HPX-87H column), Fe(II) concentrations were measured by ferrozine assay, and protein concentrations were measured by bicinchoninic acid assay, all as previously described . During growth with acetate, Fe(II) was 37.83 ± 1.88 mM, protein was 0.030 ± 0.005 mg/mL, and acetate was below detection limit (50 uM). During growth with benzoate, Fe(II) was 34.45 ± 6.58 mM and protein was 0.023 ± 0.002 mg/mL. Cells were harvested from three replicate chemostats for each of the electron donors.
Gene expression analysis
RNA extraction, purification, and labeling were performed independently on each cell sample, as previously described . Total cellular RNA from each replicate was isolated using TRIZOL (Invitrogen) and purified using RNeasy Mini Kit (Qiagen) with on-column DNase digestion performed with RNase-free DNase Set (Qiagen). 10 μg of purified total RNA was labeled as previously described , using random hexamers (Invitrogen) for priming and either Cy3-dUTP or Cy5-dUTP as the fluorophor. After labeling, RNA was removed by NaOH treatment and cDNA was purified with a PCR purification kit (Qiagen). The labeling efficiency was monitored by measuring the absorbance at 260 nm (for DNA concentration), 550 nm (for Cy3), or 650 nm (for Cy5). Two samples of each total RNA preparation were labeled, one with Cy3-dUTP and another with Cy5-dUTP for microarray hybridization.
DNA microarrays covering 3434 of the 3530 annotated protein-coding sequences of the completed G. metallireducens genome were constructed with 70mer oligonucleotide probes, designed as previously described [73, 75]. All designed oligonucleotides were commercially synthesized without modification by MWG Biotech Inc. (High Point, NC). Oligonucleotides were adjusted to 100 pmol/μl in 50% DMSO, and two replicates per probe were spotted onto UltraGAPS glass slides (Corning Life Science, NY) using a Microgrid II robotic arrayer (Genomic Solutions Inc., MI) and fixed by UV cross-linking (600 mJ). Additionally, 6 concentrations (5, 25, 50, 100, 200, and 300 ng/μl) of genomic DNA were spotted (8 duplicates of each concentration per slide) as positive controls.
Microarray hybridization, washing, and scanning were carried out as previously described . Cy5-dUTP-labeled cDNA targets from one benzoate culture were mixed with the Cy3-dUTP-labeled cDNA targets from one acetate culture and vice versa (dye swap). Equal amounts of Cy3- or Cy5-labeled probes were mixed and incubated at 95-98°C for 5 min, centrifuged to collect condensation, kept at 50°C, and applied onto microarray slides. Hybridization was carried out in hybridization chambers (Corning Life Sciences, Corning, NY) at 45°C for 16–20 h. Microarray slides were washed according to the instructions by the manufacturer (Corning), and dried with N2. The fluorescence intensity of both the Cy5 and Cy3 fluorophores was scanned using the ScanArray Express microarray analysis system (Perkin Elmer, Boston, MA).
Signal intensities were determined using 16-bit TIFF scanned images and ImaGene version 6.0 (Biodiscovery, Marina Del Rey, Calif.) to quantify spot signal, spot quality, and background fluorescent intensities. Empty spots, poor spots, and negative spots were flagged according to instructions and removed in subsequent analysis, as previously described . Lowess normalization was performed on each slide using GeneSpring version 5.1 (Silicon Genetics, Redwood City, Calif.), and the results for the triplicate cultures were used for statistical analysis. Student t-test was used to calculate a p-value to test the null hypothesis that the expression level was unchanged for each spot. P values equal to or less than 0.01 were considered significant. Results were submitted to NCBI Gene Expression Omnibus, accession GSE5401.
We thank Trevor Woodard for technical assistance. This research was supported by the Office of Science (BER), U.S. Department of Energy, Grant No. DE-FC02-02ER63446.
- Diaz E: Bacterial degradation of aromatic pollutants: a paradigm of metabolic versatility. Int Microbiol. 2004, 7: 173-180.PubMedGoogle Scholar
- Chakraborty R, Coates JD: Anaerobic degradation of monoaromatic hydrocarbons. Appl Microbiol Biotechnol. 2004, 64: 437-446. 10.1007/s00253-003-1526-x.PubMedView ArticleGoogle Scholar
- Harwood CS, Gibson J: Shedding light on anaerobic benzene ring degradation: a process unique to prokaryotes?. J Bacteriol. 1997, 179: 301-309.PubMed CentralPubMedGoogle Scholar
- Heider J, Fuchs G: Anaerobic metabolism of aromatic compounds. Eur J Biochem. 1997, 243: 577-596. 10.1111/j.1432-1033.1997.00577.x.PubMedView ArticleGoogle Scholar
- Boll M: Dearomatizing benzene ring reductases. J Mol Microbiol Biotechnol. 2005, 10: 132-142. 10.1159/000091560.PubMedView ArticleGoogle Scholar
- Gibson J, Harwood CS: Metabolic diversity in aromatic compound utilization by anaeroic microbes. Annu Rev Microbiol. 2002, 56: 345-369. 10.1146/annurev.micro.56.012302.160749.PubMedView ArticleGoogle Scholar
- Harwood CS, Burchhardt G, Herrmann H, Fuchs G: Anaerobic metabolism of aromatic compounds via the benzoyl-CoA pathway. FEMS Microbiol Rev. 1999, 22: 439-458. 10.1111/j.1574-6976.1998.tb00380.x.View ArticleGoogle Scholar
- Dorner E, Boll M: Properties of 2-oxoglutarate:ferredoxin oxidoreductase from Thauera aromatica and its role in enzymatic reduction of the aromatic ring. J Bacteriol. 2002, 184: 3975-3983. 10.1128/JB.184.14.3975-3983.2002.PubMed CentralPubMedView ArticleGoogle Scholar
- Boll M, Fuchs G: Benzoyl-coenzyme A reductase (dearomatizing), a key enzyme of anaerobic aromatic metabolism. ATP dependence of the reaction, purification and some properties of the enzyme from Thauera aromatica strain K172. Eur J Biochem. 1995, 234: 921-933. 10.1111/j.1432-1033.1995.921_a.x.PubMedView ArticleGoogle Scholar
- Boll M, Fuchs G: Identification and characterization of the natural electron donor ferredoxin and of FAD as a possible prosthetic group of benzoyl-CoA reductase (dearomatizing), a key enzyme of anaerobic aromatic metabolism. Eur J Biochem. 1998, 251: 946-954. 10.1046/j.1432-1327.1998.2510946.x.PubMedView ArticleGoogle Scholar
- Albrechtsen HJ, Christensen TH: Evidence for microbial iron reduction in a landfill leachate-polluted aquifer (Vejen, Denmark). Appl Environ Microbiol. 1994, 60: 3920-3925.PubMed CentralPubMedGoogle Scholar
- Lovley DR, Baedecker MJ, Lonergan DJ, Philips EJ, Siegel DI: Oxidation of aromatic contaminants coupled to microbial iron reduction. Nature. 1989, 339: 297-300. 10.1038/339297a0.View ArticleGoogle Scholar
- Ludvigsen L, Albrechtsen H, Ringelberg DB, Ekelund F, Christensen TH: Distribution and composition of microbial populations in a landfill leachate contaminated aquifer (Grindsted, Denmark). Microb Ecol. 1999, 37 (3): 197-207. 10.1007/s002489900143.PubMedView ArticleGoogle Scholar
- Roling WF, van Breukelen BM, Braster M, Lin B, van Verseveld HW: Relationships between microbial community structure and hydrochemistry in a landfill leachate-polluted aquifer. Appl Environ Microbiol. 2001, 67: 4619-4629. 10.1128/AEM.67.10.4619-4629.2001.PubMed CentralPubMedView ArticleGoogle Scholar
- Elshahed MS, Bhupathiraju VK, Wofford NQ, Nanny MA, McInerney MJ: Metabolism of benzoate, cyclohex-1-ene carboxylate, and cyclohexane carboxylate by "Syntrophus aciditrophicus" strain SB in syntrophic association with H(2)-using microorganisms. Appl Environ Microbiol. 2001, 67: 1728-1738. 10.1128/AEM.67.4.1728-1738.2001.PubMed CentralPubMedView ArticleGoogle Scholar
- Peters F, Rother M, Boll M: Selenocysteine-containing proteins in anaerobic benzoate metabolism of Desulfococcus multivorans. J Bacteriol. 2004, 186: 2156-2163. 10.1128/JB.186.7.2156-2163.2004.PubMed CentralPubMedView ArticleGoogle Scholar
- Schocke L, Schink B: Energetics and biochemistry of fermetative benzoate degradation by Syntrophus gentianae. Arch Microbiol. 1999, 171: 331-337. 10.1007/s002030050718.View ArticleGoogle Scholar
- Snoeyenbos-West OL, Nevin KP, Anderson RT, Lovley DR: Enrichment of Geobacter species in response to stimulation of Fe(III) reduction in sandy aquifer sediments. Microb Ecol. 2000, 39 (2): 153-167. 10.1007/s002480000018.PubMedView ArticleGoogle Scholar
- Rooney-Varga JN, Anderson RT, Fraga JL, Ringelberg D, Lovley DR: Microbial communities associated with anaerobic benzene degradation in a petroleum-contaminated aquifer. Appl Environ Microbiol. 1999, 65: 3056-3063.PubMed CentralPubMedGoogle Scholar
- Lovley DR, Lonergan DJ: Anaerobic oxidation of toluene, phenol, and p-cresol by the dissimilatory iron-reducing organism, GS-15. Appl Environ Microbiol. 1990, 56: 1858-1864.PubMed CentralPubMedGoogle Scholar
- Lovley DR, Giovannoni SJ, White DC, Champine JE, Phillips EJ, Gorby YA, Goodwin S: Geobacter metallireducens gen. nov. sp. nov., a microorganism capable of coupling the complete oxidation of organic compounds to the reduction of iron and other metals. Arch Microbiol. 1993, 159: 336-344. 10.1007/BF00290916.PubMedView ArticleGoogle Scholar
- Hosoda A, Kasai Y, Hamamura N, Takahata Y, Watanabe K: Development of a PCR method for the detection and quantification of benzoyl-CoA reductase genes and its application to monitored natural attenuation. Biodegradation. 2005, 16: 591-601. 10.1007/s10532-005-0826-5.PubMedView ArticleGoogle Scholar
- Wischgoll S, Heintz D, Peters F, Erxleben A, Sarnighausen E, Reski R, Van Dorsselaer A, Boll M: Gene clusters involved in anaerobic benzoate degradation of Geobacter metallireducens. Molecular Microbiology. 2005, 58: 1238-1252.PubMedView ArticleGoogle Scholar
- Copeland A, Lucas S, Lapidus A, Barry K, Detter JC, Glavina T, Hammon N, Israni S, Pitluck S, Di Bartolo G, Chain P, Schmutz J, Larimer F, Land M, Kyrpides N, Ivanova N, Richardson P: Complete sequence of Geobacter metallireducens GS-15. unpublished. 2005Google Scholar
- Schuhle K, Fuchs G: Phenylphosphate carboxylase: a new C-C lyase involved in anaerobic phenol metabolism in Thauera aromatica. J Bacteriol. 2004, 186: 4556-4567. 10.1128/JB.186.14.4556-4567.2004.PubMed CentralPubMedView ArticleGoogle Scholar
- Schmeling S, Narmandakh A, Schmitt O, Gad'on N, Schuhle K, Fuchs G: Phenylphosphate synthase: a new phosphotransferase catalyzing the first step in anaerobic phenol metabolism in Thauera aromatica. J Bacteriol. 2004, 186: 8044-8057. 10.1128/JB.186.23.8044-8057.2004.PubMed CentralPubMedView ArticleGoogle Scholar
- Breinig S, Schiltz E, Fuchs G: Genes involved in anaerobic metabolism of phenol in the bacterium Thauera aromatica. J Bacteriol. 2000, 182: 5849-5863. 10.1128/JB.182.20.5849-5863.2000.PubMed CentralPubMedView ArticleGoogle Scholar
- Cronin CN, Kim J, Fuller JH, Zhang X, McIntire WS: Organization and sequences of p-hydroxybenzaldehyde dehydrogenase and other plasmid-encoded genes for early enzymes of the p-cresol degradative pathway in Pseudomonas putida NCIMB 9866 and 9869. DNA Seq. 1999, 10: 7-17.PubMedGoogle Scholar
- Rabus R, Kube M, Heider J, Beck A, Heitmann K, Widdel F, Reinhardt R: The genome sequence of an anaerobic aromatic-degrading denitrifying bacterium, strain EbN1. Arch Microbiol. 2005, 183: 27-36. 10.1007/s00203-004-0742-9.PubMedView ArticleGoogle Scholar
- Breese K, Fuchs G: 4-Hydroxybenzoyl-CoA reductase (dehydroxylating) from the denitrifying bacterium Thauera aromatica--prosthetic groups, electron donor, and genes of a member of the molybdenum-flavin-iron-sulfur proteins. Eur J Biochem. 1998, 251: 916-923. 10.1046/j.1432-1327.1998.2510916.x.PubMedView ArticleGoogle Scholar
- Greated A, Lambertsen L, Williams PA, Thomas CM: Complete sequence of the IncP-9 TOL plasmid pWW0 from Pseudomonas putida. Environ Microbiol. 2002, 4: 856-871. 10.1046/j.1462-2920.2002.00305.x.PubMedView ArticleGoogle Scholar
- Kim J, Hetzel M, Boiangiu CD, Buckel W: Dehydration of (R)-2-hydroxyacyl-CoA to enoyl-CoA in the fermentation of alpha-amino acids by anaerobic bacteria. FEMS Microbiol Rev. 2004, 28: 455-468.PubMedView ArticleGoogle Scholar
- Hans M, Sievers J, Muller U, Bill E, Vorholt JA, Linder D, Buckel W: 2-hydroxyglutaryl-CoA dehydratase from Clostridium symbiosum. Eur J Biochem. 1999, 265: 404-414. 10.1046/j.1432-1327.1999.00748.x.PubMedView ArticleGoogle Scholar
- Locher KP, Hans M, Yeh AP, Schmid B, Buckel W, Rees DC: Crystal structure of the Acidaminococcus fermentans 2-hydroxyglutaryl-CoA dehydratase component A. J Mol Biol. 2001, 307: 297-308. 10.1006/jmbi.2000.4496.PubMedView ArticleGoogle Scholar
- Breese K, Boll M, Alt-Morbe J, Schagger H, Fuchs G: Genes coding for the benzoyl-CoA pathway of anaerobic aromatic metabolism in the bacterium Thauera aromatica. Eur J Biochem. 1998, 256: 148-154. 10.1046/j.1432-1327.1998.2560148.x.PubMedView ArticleGoogle Scholar
- Hu Y, Faham S, Roy R, Adams MW, Rees DC: Formaldehyde ferredoxin oxidoreductase from Pyrococcus furiosus: the 1.85 A resolution crystal structure and its mechanistic implications. J Mol Biol. 1999, 286: 899-914. 10.1006/jmbi.1998.2488.PubMedView ArticleGoogle Scholar
- Chan MK, Mukund S, Kletzin A, Adams MW, Rees DC: Structure of a hyperthermophilic tungstopterin enzyme, aldehyde ferredoxin oxidoreductase. Science. 1995, 267: 1463-1469. 10.1126/science.7878465.PubMedView ArticleGoogle Scholar
- Elshahed MS, McInerney MJ: Benzoate fermentation by the anaerobic bacterium Syntrophus aciditrophicus in the absence of hydrogen-using microorganisms. Appl Environ Microbiol. 2001, 67: 5520-5525. 10.1128/AEM.67.12.5520-5525.2001.PubMed CentralPubMedView ArticleGoogle Scholar
- Lopez Barragan MJ, Carmona M, Zamarro MT, Thiele B, Boll M, Fuchs G, Garcia JL, Diaz E: The bzd gene cluster, coding for anaerobic benzoate catabolism, in Azoarcus sp. strain CIB. J Bacteriol. 2004, 186: 5762-5774. 10.1128/JB.186.17.5762-5774.2004.PubMedView ArticleGoogle Scholar
- Lopez Barragan MJ, Diaz E, Garcia JL, Carmona M: Genetic clues on the evolution of anaerobic catabolism of aromatic compounds. Microbiology. 2004, 150: 2018-2021. 10.1099/mic.0.27186-0.PubMedView ArticleGoogle Scholar
- Rabus R: Functional genomics of an anaerobic aromatic-degrading denitrifying bacterium, strain EbN1. Appl Microbiol Biotechnol. 2005, 68: 580-587. 10.1007/s00253-005-0030-x.PubMedView ArticleGoogle Scholar
- Tan HM: Bacterial catabolic transposons. Appl Microbiol Biotechnol. 1999, 51: 1-12. 10.1007/s002530051356.PubMedView ArticleGoogle Scholar
- Ochman H, Lawrence JG, Groisman EA: Lateral gene transfer and the nature of bacterial innovation. Nature. 2000, 405: 299-304. 10.1038/35012500.PubMedView ArticleGoogle Scholar
- Karlin S, Campbell AM, Mrazek J: Comparative DNA analysis across diverse genomes. Annu Rev Genet. 1998, 32: 185-225. 10.1146/annurev.genet.32.1.185.PubMedView ArticleGoogle Scholar
- Siguier P, Perochon J, Lestrade L, Mahillon J, Chandler M: ISfinder: the reference centre for bacterial insertion sequences. Nucleic Acids Res. 2006, 34: D32-6. 10.1093/nar/gkj014.PubMed CentralPubMedView ArticleGoogle Scholar
- Mahillon J, Chandler M: Insertion sequences. Microbiol Mol Biol Rev. 1998, 62: 725-774.PubMed CentralPubMedGoogle Scholar
- Dobrindt U, Hochhut B, Hentschel U, Hacker J: Genomic islands in pathogenic and environmental microorganisms. Nat Rev Microbiol. 2004, 2: 414-424. 10.1038/nrmicro884.PubMedView ArticleGoogle Scholar
- Hacker J, Blum-Oehler G, Muhldorfer I, Tschape H: Pathogenicity islands of virulent bacteria: structure, function and impact on microbial evolution. Mol Microbiol. 1997, 23: 1089-1097. 10.1046/j.1365-2958.1997.3101672.x.PubMedView ArticleGoogle Scholar
- Lawrence JG, Ochman H: Amelioration of bacterial genomes: rates of change and exchange. J Mol Evol. 1997, 44: 383-397. 10.1007/PL00006158.PubMedView ArticleGoogle Scholar
- Champine JE, Goodwin S: Acetate catabolism in the dissimilatory iron-reducing isolate GS-15. J Bacteriol. 1991, 173: 2704-2706.PubMed CentralPubMedGoogle Scholar
- Galushko AS, Schink B: Oxidation of acetate through reactions of the citric acid cycle by Geobacter sulfurreducens in pure culture and in syntrophic coculture. Arch Microbiol. 2000, 174: 314-321. 10.1007/s002030000208.PubMedView ArticleGoogle Scholar
- Cortay JC, Negre D, Galinier A, Duclos B, Perriere G, Cozzone AJ: Regulation of the acetate operon in Escherichia coli: purification and functional characterization of the IclR repressor. Embo J. 1991, 10: 675-679.PubMed CentralPubMedGoogle Scholar
- Petrie L, North NN, Dollhopf SL, Balkwill DL, Kostka JE: Enumeration and characterization of iron(III)-reducing microbial communities from acidic subsurface sediments contaminated with uranium(VI). Appl Environ Microbiol. 2003, 69: 7467-7479. 10.1128/AEM.69.12.7467-7479.2003.PubMed CentralPubMedView ArticleGoogle Scholar
- North NN, Dollhopf SL, Petrie L, Istok JD, Balkwill DL, Kostka JE: Change in bacterial community structure during in situ biostimulation of subsurface sediment cocontaminated with uranium and nitrate. Appl Environ Microbiol. 2004, 70: 4911-4920. 10.1128/AEM.70.8.4911-4920.2004.PubMed CentralPubMedView ArticleGoogle Scholar
- van der Meer JR, Sentchilo V: Genomic islands and the evolution of catabolic pathways in bacteria. Curr Opin Biotechnol. 2003, 14: 248-254. 10.1016/S0958-1669(03)00058-2.PubMedView ArticleGoogle Scholar
- Muller TA, Werlen C, Spain J, Van Der Meer JR: Evolution of a chlorobenzene degradative pathway among bacteria in a contaminated groundwater mediated by a genomic island in Ralstonia. Environ Microbiol. 2003, 5: 163-173. 10.1046/j.1462-2920.2003.00400.x.PubMedView ArticleGoogle Scholar
- Lovley DR: Cleaning up with genomics: applying molecular biology to bioremediation. Nat Rev Microbiol. 2003, 1: 35-44. 10.1038/nrmicro731.PubMedView ArticleGoogle Scholar
- Holmes DE, Nevin KP, O'Neil RA, Ward JE, Adams LA, Woodard TL, Vrionis HA, Lovley DR: Potential for quantifying expression of the Geobacteraceae citrate synthase gene to assess the activity of Geobacteraceae in the subsurface and on current-harvesting electrodes. Appl Environ Microbiol. 2005, 71: 6870-6877. 10.1128/AEM.71.11.6870-6877.2005.PubMed CentralPubMedView ArticleGoogle Scholar
- Holmes DE, Nevin KP, Lovley DR: In situ expression of nifD in Geobacteraceae in subsurface sediments. Appl Environ Microbiol. 2004, 70: 7251-7259. 10.1128/AEM.70.12.7251-7259.2004.PubMed CentralPubMedView ArticleGoogle Scholar
- Altschul SF, Madden TL, Schaffer AA, Zhang J, Zhang Z, Miller W, Lipman DJ: Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Res. 1997, 25: 3389-3402. 10.1093/nar/25.17.3389.PubMed CentralPubMedView ArticleGoogle Scholar
- Benson DA, Karsch-Mizrachi I, Lipman DJ, Ostell J, Wheeler DL: GenBank. Nucleic Acids Res. 2005, 33: D34-8. 10.1093/nar/gki063.PubMed CentralPubMedView ArticleGoogle Scholar
- Bairoch A, Apweiler R, Wu CH, Barker WC, Boeckmann B, Ferro S, Gasteiger E, Huang H, Lopez R, Magrane M, Martin MJ, Natale DA, O'Donovan C, Redaschi N, Yeh LS: The Universal Protein Resource (UniProt). Nucleic Acids Res. 2005, 33: D154-9. 10.1093/nar/gki070.PubMed CentralPubMedView ArticleGoogle Scholar
- Mulder NJ, Apweiler R, Attwood TK, Bairoch A, Bateman A, Binns D, Bradley P, Bork P, Bucher P, Cerutti L, Copley R, Courcelle E, Das U, Durbin R, Fleischmann W, Gough J, Haft D, Harte N, Hulo N, Kahn D, Kanapin A, Krestyaninova M, Lonsdale D, Lopez R, Letunic I, Madera M, Maslen J, McDowall J, Mitchell A, Nikolskaya AN, Orchard S, Pagni M, Ponting CP, Quevillon E, Selengut J, Sigrist CJ, Silventoinen V, Studholme DJ, Vaughan R, Wu CH: InterPro, progress and status in 2005. Nucleic Acids Res. 2005, 33: D201-5. 10.1093/nar/gki106.PubMed CentralPubMedView ArticleGoogle Scholar
- Gardy JL, Laird MR, Chen F, Rey S, Walsh CJ, Ester M, Brinkman FS: PSORTb v.2.0: expanded prediction of bacterial protein subcellular localization and insights gained from comparative proteome analysis. Bioinformatics. 2005, 21: 617-623. 10.1093/bioinformatics/bti057.PubMedView ArticleGoogle Scholar
- Thompson JD, Gibson TJ, Plewniak F, Jeanmougin F, Higgins DG: The CLUSTAL_X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res. 1997, 25: 4876-4882. 10.1093/nar/25.24.4876.PubMed CentralPubMedView ArticleGoogle Scholar
- Saitou N, Nei M: The neighbor-joining method: a new method for reconstructing phylogenetic trees. Mol Biol Evol. 1987, 4: 406-425.PubMedGoogle Scholar
- Kumar S, Tamura K, Nei M: MEGA3: Integrated software for Molecular Evolutionary Genetics Analysis and sequence alignment. Brief Bioinform. 2004, 5: 150-163. 10.1093/bib/5.2.150.PubMedView ArticleGoogle Scholar
- Tatusov RL, Koonin EV, Lipman DJ: A genomic perspective on protein families. Science. 1997, 278: 631-637. 10.1126/science.278.5338.631.PubMedView ArticleGoogle Scholar
- Rubin GM, Yandell MD, Wortman JR, Gabor Miklos GL, Nelson CR, Hariharan IK, Fortini ME, Li PW, Apweiler R, Fleischmann W, Cherry JM, Henikoff S, Skupski MP, Misra S, Ashburner M, Birney E, Boguski MS, Brody T, Brokstein P, Celniker SE, Chervitz SA, Coates D, Cravchik A, Gabrielian A, Galle RF, Gelbart WM, George RA, Goldstein LS, Gong F, Guan P, Harris NL, Hay BA, Hoskins RA, Li J, Li Z, Hynes RO, Jones SJ, Kuehl PM, Lemaitre B, Littleton JT, Morrison DK, Mungall C, O'Farrell PH, Pickeral OK, Shue C, Vosshall LB, Zhang J, Zhao Q, Zheng XH, Lewis S: Comparative genomics of the eukaryotes. Science. 2000, 287: 2204-2215. 10.1126/science.287.5461.2204.PubMed CentralPubMedView ArticleGoogle Scholar
- Rice P, Longden I, Bleasby A: EMBOSS: the European Molecular Biology Open Software Suite. Trends Genet. 2000, 16: 276-277. 10.1016/S0168-9525(00)02024-2.PubMedView ArticleGoogle Scholar
- van Passel MW, Luyf AC, van Kampen AH, Bart A, van der Ende A: Deltarho-web, an online tool to assess composition similarity of individual nucleic acid sequences. Bioinformatics. 2005, 21: 3053-3055. 10.1093/bioinformatics/bti460.PubMedView ArticleGoogle Scholar
- Esteve-Nunez A, Rothermich M, Sharma M, Lovley D: Growth of Geobacter sulfurreducens under nutrient-limiting conditions in continuous culture. Environ Microbiol. 2005, 7: 641-648. 10.1111/j.1462-2920.2005.00731.x.PubMedView ArticleGoogle Scholar
- He Q, Huang KH, He Z, Alm EJ, Fields MW, Hazen TC, Arkin AP, Wall JD, Zhou J: Energetic consequences of nitrite stress in Desulfovibrio vulgaris Hildenborough inferred from global transcriptional analysis. Appl Environ Microbiol. 2006, 72 (6): 4370-4381. 10.1128/AEM.02609-05.PubMed CentralPubMedView ArticleGoogle Scholar
- Thompson DK, Beliaev AS, Giometti CS, Tollaksen SL, Khare T, Lies DP, Nealson KH, Lim H, Yates J, Brandt CC, Tiedje JM, Zhou J: Transcriptional and proteomic analysis of a ferric uptake regulator (fur) mutant of Shewanella oneidensis: possible involvement of fur in energy metabolism, transcriptional regulation, and oxidative stress. Appl Environ Microbiol. 2002, 68: 881-892. 10.1128/AEM.68.2.881-892.2002.PubMed CentralPubMedView ArticleGoogle Scholar
- He Z, Wu L, Li X, Fields MW, Zhou J: Empirical establishment of oligonucleotide probe design criteria. Appl Environ Microbiol. 2005, 71: 3753-3760. 10.1128/AEM.71.7.3753-3760.2005.PubMed CentralPubMedView ArticleGoogle Scholar
- Gao H, Wang Y, Liu X, Yan T, Wu L, Alm E, Arkin A, Thompson DK, Zhou J: Global transcriptome analysis of the heat shock response of Shewanella oneidensis. J Bacteriol. 2004, 186: 7796-7803. 10.1128/JB.186.22.7796-7803.2004.PubMed CentralPubMedView ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.