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. 2006 Dec 1;73(4):1367–1369. doi: 10.1128/AEM.01904-06

Identification and Expression of Benzylsuccinate Synthase Genes in a Toluene-Degrading Methanogenic Consortium

Cheryl E Washer 1, Elizabeth A Edwards 1,*
PMCID: PMC1828654  PMID: 17142355

Abstract

Benzylsuccinate synthase (BSS) initiates anaerobic toluene biodegradation, and BSS genes have been found in several nitrate- and iron-reducing organisms. Here, two new putative bssA genes were identified in a methanogenic toluene-degrading culture. Transcription was upregulated with toluene but not with benzoate, consistent with the proposed function. These are the first bss sequences from a methanogenic culture.


Anaerobic toluene biodegradation can be initiated by benzylsuccinate synthase (BSS) (3, 4, 6, 7, 13, 15, 16, 21), and the genes encoding BSS and related enzymes (bssDCABE) have to date been sequenced from six denitrifying bacteria (1, 9, 12, 14, 15, 19) and one iron-reducing microorganism (13). No BSS gene sequences from any sulfate-reducing or methanogenic cultures have yet been published. This goal of this study was to identify BSS gene sequences in a highly enriched toluene-degrading methanogenic consortium. We have previously shown that benzylsuccinate is produced by this culture (4) but were unable to amplify BSS genes by the use of published primers (5).

Identification of putative bssA sequences.

The toluene-degrading methanogenic enrichment culture used in this study (4, 10, 11) has been maintained for almost 15 years with toluene as the sole carbon source and electron donor. Genomic DNA was extracted from the culture by use of an UltraClean soil DNA extraction kit (Mo Bio Laboratories Inc., Solana Beach, CA), and PCR amplification of putative bssA sequences was performed using a variety of primer sets designed from alignments of known sequences and incorporating degeneracies (Table 1). A partial transcriptional map of the bss operon and of the target regions labeled TR1 to TR5, flanked by different forward and reverse primer sets, is shown in Fig. 1. PCR amplifications were performed using RediTaq (New England BioLabs, Mississauga, ON), and conditions were as follows: initial denaturation at 94°C for 5 min followed by 30 cycles of denaturation at 94°C for 1 min, primer annealing for 1 min (for annealing temperatures, see Table 1), and chain extension for 1.5 min (1 min for primer set 5) at 72°C followed by a final extension step at 72°C for 10 min. All PCRs were carried out in a PTC-200 DNA Engine thermocycler (MJ Research Inc., Waltham, MA). For each primer set, three PCRs were carried out in parallel, and the products were pooled and run on a 1% agarose gel stained with ethidium bromide. Where only one band of the expected length was observed, the PCR products were purified using a QIAquick PCR cleanup kit (QIAGEN, Valencia, CA). Where more than one band was observed, the band of the expected length was excised from the gel and purified using a QIAGEN gel purification kit (QIAGEN, Valencia, CA). Amplicons were cloned using a TOPO TA cloning kit (Invitrogen, Carlsbad, CA), according to the manufacturer's instructions, and DNA from 10 to 15 clones was sequenced using vector primers T7f and M13r. To obtain complete sequences of putative bssA or bssABE clones, internal primers designed with Primer3 software (17) were used. Partial sequences of putative bssA or bssABE amplicons were aligned and assembled using ChromasPro 1.15 (Technelysium Pty Ltd., Australia), and GeneMark (8) was used to predict start and/or stop codons of the putative bssA, bssB, and bssE sequences identified.

TABLE 1.

Degenerate PCR primers designed to amplify putative bssA or bssABE sequences in the methanogenic toluene-degrading culture

Primer set(s) (target region[s]) Primera Sequence (5′-3′)b Annealing temp (°C)
1, 3 BssA327f CGAATTCATCNTCGGCTACC 54
1 BssA2004r GTCGTCRTTGCCCCAYTTNGG 54
2 MBssA1516fc AGACCCAGAAGACCAGGTC 54
3 MBssA2446rc ATGCTTTTCAGGCTCCCTCT 54
2, 5 BssA2524r ATGATSGTGTTYTGSCCRTAGGT 54, 46d
4, 5 BssA1985f CNAARTGGGGCAAYGACGA 49, 46d
4 BssE347r TGYTCNGGNCGRTTGATCTCYTC 49
a

Sequence positions indicated for primers refer to the nucleotide position numbers in the Azoarcus sp. strain T bssA and bssE sequences.

b

Y = C/T, N = A/C/T/G, R = A/G, S = C/G.

c

Specific primers designed based on an initial cloning study of the methanogenic consortium.

d

The annealing temperature used for primer set 5 was 46°C. An annealing temperature of 52°C also amplified DNA of the expected length.

FIG. 1.

FIG. 1.

Partial transcriptional map of the bss operon. The target regions (TRs) for PCR amplification and sequencing are shown under the map. The primers used to amplify TR5 were 1985f and 2524r. The two dotted vertical lines shown in the bssA box illustrate the approximate positions of nucleotides coding for conserved cysteine (positions 1464 to 1467 in the Thauera aromatica K172 bssA sequence) and glycine (positions 2472 to 2475 in T. aromatica K172) residues in this gene.

One putative sequence was assembled from amplicons obtained with all of the primer sets listed in Table 1. This contiguous sequence (GenBank: EF134966) includes a putative bssA (referred to as bssA-1, encoding a protein with 747 amino acids), a putative bssB (85 amino acids) and a putative partial bssE sequence (113 amino acids). A second putative bssA sequence, referred to as bssA-2, was only found using primers for TR1 and could not be assembled with any other sequences. BLAST queries of translated bssA-1 and bssA-2 sequences against the NCBI non-redundant translated database using default parameters (2) revealed 78-84% similarity to the seven previously known BssA sequences, and the expectation value for each hit was 0.0. The translated sequences of bssA-1 and bssA-2 were 83% similar to each other. As with the previously known BssA sequences, the C-terminal region of BssA-1 was highly conserved, and a conserved glycine residue was present at a position corresponding to residue 825 in the Thauera aromatica strain K172 BssA sequence. The conserved glycine residue is characteristic of all glycyl radical enzymes (GREs) (13), and is a part of the glycyl radical fingerprint motif RVxG(FWY)x6-8(FL)x4Qx2(IV)x2R that is found in most GREs (18) and in all BssA sequences known to date. In addition to the conserved glycine motif in BssA-1, both BssA-1 and BssA-2 contained a conserved cysteine residue at the position corresponding residue 489 of the T. aromatica K172 BssA sequence. This conserved residue is also characteristic of GREs (18).

Differential transcription of bssA.

For this part of the study, 60-ml portions of the methanogenic culture were transferred anaerobically into each of six 125-ml glass bottles sealed with Mininert (VICI Precision Sampling, Baton Rouge, LA) caps. Three bottles were amended with toluene (42 μmol/bottle), while the other three were amended with benzoate (49 μmol/bottle), a downstream metabolite in anaerobic toluene degradation. Toluene and methane concentrations were analyzed as described previously (11). RNA was extracted from all bottles when 50% of the toluene or benzoate was degraded, and all bottles contained approximately the same concentration of methane. Total RNA was extracted and purified from 45 ml of culture as previously described (20) except that culture samples were centrifuged at 15,000 × g and 4°C for 30 min. Reverse transcription was performed using random hexamers and Superscript III reverse transcriptase (RT) (Invitrogen, Carlsbad, CA). Each reaction mixture (25 μl total volume) contained 5 μl of 5× First Strand buffer, 250 ng random hexamers (Invitrogen), 50 nmol of deoxynucleoside triphosphates, 2 μmol of dithiothreitol, and approximately 2 μg of RNA. RT reactions were carried out in RNase-free PCR tubes, using a PTC-200 DNA Engine thermocycler (MJ Research). The program was as follows: incubation at 65°C for 5 min and then 25°C for 5 min followed by addition of 1 μl of RT to each sample, annealing at 25°C for 10 min, reverse transcription at 50°C for 2 h, and finally inactivation of the RT at 70°C for 15 min. A no-RT control was run for each RNA sample to ensure that no DNA contamination was present.

PCRs were carried out on all reverse transcription products, including those from the no-RT control reactions. For these PCR experiments, primers with no degenerate bases were designed to specifically target each of the bssA sequences found in this study (Table 2). A primer set was also designed to target the 16S rRNA gene for a specific microorganism referred to as Eub-1—likely a Desulfotomaculum sp.—found previously to be active in the culture (11). Primer specificity was confirmed by amplifying culture DNA and checking amplicon sequences. Positive or negative amplification of the putative genes was assessed by running PCR products on a 1% agarose gel stained with ethidium bromide and looking for bands of the expected length.

TABLE 2.

PCR primers used for amplifying specific genes in the toluene-degrading consortium

Primera Sequence (5′-3′) Target gene
Eub1-621f TGAAACCATTGAGCTTGAGG Eub-1 (16S rRNA gene)
Eub1-912r CCCGTCAATTCCTTTGAGTT Eub-1 (16S rRNA gene)
bssA1-416f CAGAACACAAAGTATGCCC bssA-1
bssA1-749r TGGAGTTCCAGAGGTCGATT bssA-1
bssA2-413f TACCTGCAGAGCAAGTACGC bssA-2
bssA2-713r ACTTCAGCTTATCGGCGTTC bssA-2
a

The annealing temperature for all primer sets was 59°C. Estimated sequence positions are listed in primer names.

RT-PCRs conducted with RNA from toluene-degrading cultures resulted in the amplification of bssA-2, while no amplification was observed in benzoate-degrading cultures (Fig. 2A). Thus, bssA-2 transcription was upregulated in the presence of toluene relative to benzoate, consistent with involvement of this gene product in the conversion of toluene to benzoate. Surprisingly, although the bssA-1 sequence was readily amplified from culture DNA, transcription of bssA-1 in the presence of either toluene or benzoate was not observed (data not shown). To ensure that all RNA extractions and RT reactions were comparable between treatments, cDNA was amplified with 16S rRNA primers for Eub-1. In all cases, bands corresponding to amplicons of expected sizes and of similar intensities were observed by gel electrophoresis (Fig. 2B). No amplification was observed in any of the no-RT control reactions.

FIG. 2.

FIG. 2.

Agarose gels showing amplicons from RT-PCRs performed using cultures amended with toluene (T) or benzoate (B). Amplification was carried out using specific bssA-2 primers (panel A) and Eub-1 (16S rRNA gene) primers (panel B) listed in Table 2. Expected amplicon lengths were ∼300 bp for all reactions. Control reactions shown: “T-RT” and “B-RT,” controls without reverse transcriptase; +, culture DNA; −, no sample.

The differential transcription of bssA-2, combined with the bioinformatic analysis of the sequence, provides strong evidence that bssA-2 encodes an enzyme that shares the same catalytic function as those encoded by BssA sequences from the nitrate- and iron-reducing microorganisms discovered to date. Although the transcription of bssA-1 was not demonstrated in this study, the strong similarity of BssA-1 sequence to other known BssA sequences and the presence of putative bssB and bssE sequences on the same operon as bssA-1 support the proposed function of this gene. Further studies examining transcription of this gene at very high or low toluene concentrations or in the presence of other alkylbenzenes may help to determine the nature of the role of bssA-1 in the culture.

The identification of new bssA sequences from the methanogenic culture, combined with the existing sequence data obtained from nitrate-reducing and iron-reducing microorganisms, expands our knowledge of the diversity of bssA, bssB, and bssE genes in the environment. As more bssA sequences are discovered, particularly from strict anaerobes such as those found in this study, more comprehensive primers and probes can be designed to track the growth and activity of alkylbenzene-degrading organisms in the environment and confirm biodegradation of toluene and other alkylbenzenes in contaminated soil and groundwater.

Nucleotide sequence accession numbers.

The putative bssA and bssABE sequences have been deposited in GenBank under accession numbers EF134965 and EF134966.

Acknowledgments

We thank Monika Ficker for her previous work enriching the methanogenic toluene-degrading culture and Charles Whang for developing the RNA extraction procedure used.

The research was supported by the Natural Science and Engineering Research Council of Canada through a discovery grant awarded to E.A.E. and a postgraduate scholarship awarded to C.E.W.

Footnotes

Published ahead of print on 1 December 2006.

REFERENCES

  • 1.Achong, G. R., A. M. Rodriguez, and A. M. Spormann. 2001. Benzylsuccinate synthase of Azoarcus sp. strain T: cloning, sequencing, transcriptional organization, and its role in anaerobic toluene and m-xylene mineralization. J. Bacteriol. 183:6763-6770. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Altschul, S. F., T. L. Madden, A. A. Schaffer, J. Zhang, Z. Zhang, W. Miller, and D. J. Lipman. 1997. Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Res. 25:3389-3402. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Beller, H. R., and A. M. Spormann. 1997. Benzylsuccinate formation as a means of anaerobic toluene activation by sulfate-reducing strain PRTOL1. Appl. Environ. Microbiol. 63:3729-3731. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Beller, H. R., and E. A. Edwards. 2000. Anaerobic toluene activation by benzylsuccinate synthase in a highly enriched methanogenic culture. Appl. Environ. Microbiol. 66:5503-5505. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 5.Beller, H. R., S. R. Kane, T. C. Legler, and P. J. J. Alvarez. 2002. A real-time polymerase chain reaction method for monitoring anaerobic, hydrocarbon-degrading bacteria based on a catabolic gene. Environ. Sci. Technol. 36:3977-3984. [DOI] [PubMed] [Google Scholar]
  • 6.Beller, H. R., and A. M. Spormann. 1997. Anaerobic activation of toluene and o-xylene by addition to fumarate in denitrifying strain T. J. Bacteriol. 179:670-676. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Biegert, T., G. Fuchs, and F. Heider. 1996. Evidence that anaerobic oxidation of toluene in the denitrifying bacterium Thauera aromatica is initiated by formation of benzylsuccinate from toluene and fumarate. Eur. J. Biochem. 238:661-668. [DOI] [PubMed] [Google Scholar]
  • 8.Borodovsky, M., and J. McIninch. 1993. GenMark: parallel gene recognition for both DNA strands. Comput. Chem. 17:123-133. [Google Scholar]
  • 9.Coschigano, P. W., T. S. Wehrman, and L. Y. Young. 1998. Identification and analysis of genes involved in anaerobic toluene metabolism by strain T1: putative role of a glycine free radical. Appl. Environ. Microbiol. 64:1650-1656. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Edwards, E. A., and D. Grbic-Galic. 1994. Anaerobic degradation of toluene and o-xylene by a methanogenic consortium. Appl. Environ. Microbiol. 60:313-322. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Ficker, M., K. Krastel, S. Orlicky, and E. Edwards. 1999. Molecular characterization of a toluene-degrading methanogenic consortium. Appl. Environ. Microbiol. 65:5576-5585. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Hermuth, K., B. Leuthner, and J. Heider. 2002. Operon structure and expression of the genes for benzylsuccinate synthase in Thauera aromatica strain K172. Arch. Microbiol. 77:132-138. [DOI] [PubMed] [Google Scholar]
  • 13.Kane, S. R., H. R. Beller, T. C. Legler, and R. T. Anderson. 2002. Biochemical and genetic evidence of benzylsuccinate synthase in toluene-degrading, ferric iron-reducing Geobacter metallireducens. Biodegradation 13:149-154. [DOI] [PubMed] [Google Scholar]
  • 14.Kube, M., J. Heider, J. Amann, P. Hufnagel, S. Kuhner, A. Beck, R. Reinhardt, and R. Rabus. 2004. Genes involved in the anaerobic degradation of toluene in a denitrifying bacterium, strain EbN1. Arch. Microbiol. 181:182-194. [DOI] [PubMed] [Google Scholar]
  • 15.Leuthner, B., C. Leutwein, H. Schulz, P. Horth, W. Haehnel, E. Schiltz, H. Schagger, and J. Heider. 1998. Biochemical and genetic characterization of benzylsuccinate synthase from Thauera aromatica: a new glycyl radical enzyme catalyzing the first step in anaerobic toluene metabolism. Mol. Microbiol. 28:615-628. [DOI] [PubMed] [Google Scholar]
  • 16.Rabus, R., and J. Heider. 1998. Initial reaction of anaerobic metabolism of alkylbenzenes in denitrifying and sulfate-reducing bacteria. Arch. Microbiol. 170:377-384. [Google Scholar]
  • 17.Rozen, S., and H. J. Skaletsky. 2000. Primer3 on the WWW for general users and for biologist programmers. Humana Press, Totowa, NJ. [DOI] [PubMed]
  • 18.Selmer, T., A. Pierik, and J. Heider. 2005. New glycyl radical enzymes catalysing key metabolic steps in anaerobic bacteria. Biol. Chem. 386:981-988. [DOI] [PubMed] [Google Scholar]
  • 19.Shinoda, Y., J. Akagi, Y. Uchihashi, A. Hiraishi, H. Yukawa, H. Yurimoto, Y. Sakai, and N. Kato. 2005. Anaerobic degradation of aromatic compounds by Magnetospirillum strains: isolation and degradation genes. Biosci. Biotechnol. Biochem. 69:1483-1491. [DOI] [PubMed] [Google Scholar]
  • 20.Waller, A. S., R. Krajmalnik-Brown, F. E. Löffler, and E. A. Edwards. 2005. Multiple reductive-dehalogenase-homologous genes are simultaneously transcribed during dechlorination by Dehalococcoides-containing cultures. Appl. Environ. Microbiol. 71:8257-8264. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Zengler, K., J. Heider, R. Rossello-Mora, and F. Widdel. 1999. Phototrophic utilization of toluene under anoxic conditions by a new strain of Blastochloris sulfoviridis. Arch. Microbiol. 172:204-212. [DOI] [PubMed] [Google Scholar]

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