Abstract
The gene coding for an aerobic azoreductase was cloned from Xenophilus azovorans KF46F (formerly Pseudomonas sp. strain KF46F), which was previously shown to grow with the carboxylated azo compound 1-(4′-carboxyphenylazo)-2-naphthol (carboxy-Orange II) as the sole source of carbon and energy. The deduced amino acid sequence encoded a protein with a molecular weight of 30,278 and showed no significant homology to amino acid sequences currently deposited at the relevant data bases. A presumed NAD(P)H-binding site was identified in the amino-terminal region of the azoreductase. The enzyme was heterologously expressed in Escherichia coli and the azoreductase activities of resting cells and cell extracts were compared. The results suggested that whole cells of the recombinant E. coli strains were unable to take up sulfonated azo dyes and therefore did not show in vivo azoreductase activity. The turnover of several industrially relevant azo dyes by cell extracts from the recombinant E. coli strain was demonstrated.
Azo dyes are characterized by the presence of one or more azo groups (-N=N-). They are the largest and most versatile class of dyes, and more than half of the annually produced dyes (estimated for 1994 worldwide as about 1 million tons) are azo dyes. Presumably more than 2,000 different azo dyes are currently used for the dyeing of various materials such as textiles, leather, plastics, cosmetics, and food (2, 9, 11, 36, 50).
Azo dyes are generally considered to be xenobiotic compounds which are rather recalcitrant against biodegradative processes in conventional sewage treatment systems (33, 40). Nevertheless, during the last years it has been demonstrated that several microorganisms are able to transform azo dyes to noncolored products or even mineralize them completely under certain environmental conditions. There are numerous reports which describe the reductive cleavage of azo dyes under anaerobic conditions which result in the decolorization of azo dyes. These reactions usually occur with rather low specific activities but are extremely unspecific with regard to the organisms involved and the dyes converted. In these unspecific anaerobic processes very often low-molecular-weight redox mediators (e.g., flavins or quinones) are involved (10, 22, 24, 35, 42).
Some aerobic biotransformations of azo dyes by fungi and bacteria are also known. Thus, various lignolytic fungi were shown to decolorize azo dyes using ligninases, manganese peroxidases, or laccases (8). Only very few aerobic bacteria which can grow with azo compounds have been described. The ability of bacteria to grow with simple carboxylated azo compounds as the sole source of carbon and energy was shown first by Overney (32) who isolated a “Flavobacterium” which was able to grow aerobically with the model compound 4,4′-dicarboxyazobenzene. In subsequent work, it was shown that 4,4′-dicarboxyazobenzene-degrading mixed bacterial cultures could be adapted after prolonged continuous cultivation for several hundreds of generations under nonsterile conditions to the degradation of more-complex azo compounds such as 1-(4′-carboxyphenylazo)-2-naphthol (carboxy-Orange II) or 1-(4′-carboxyphenylazo)-4-naphthol (carboxy-Orange I). From these adaptation processes in continuous cultures strains Xenophilus azovorans KF46 and Pigmentiphaga kullae were obtained (5, 6, 25, 27).
The aerobic reductive metabolism of azo dyes requires specific enzymes (aerobic azoreductases), which catalyze the NAD(P)H-dependent reduction of azo compounds to the corresponding amines. In contrast to the anaerobic reductions described above, these reactions are not inhibited in the presence of molecular oxygen. The aerobic azoreductase from the carboxy-Orange II-degrading strain KF46 was previously purified and characterized (48). The azoreductase was shown to be a monomeric flavin-free enzyme which preferentially used NADPH (and only with significantly higher Km values with NADH) as a cofactor. The purified enzyme reductively cleaved the sulfonated azo dye Orange II [1-(4′-sulfophenylazo)-2-naphthol] to sulfanilate (4-aminobenzenesulfonate) and an unidentified metabolite (presumably 1-amino-2-naphthol) consuming two moles of NAD(P)H. The azoreductase converted not only carboxy-Orange II and Orange II but also several sulfonated structural analogues, which carried a hydroxy group in the 2 position of the naphthol ring (49).
Aerobic azoreductases possess a significant potential for the purely aerobic treatment of wastewaters which are colored by azo dyes. Therefore, we decided to clone and characterize the gene encoding this interesting enzyme activity from X. azovorans KF46 in order to obtain more information about the evolution of this group of enzymes and to enable future genetic modifications.
MATERIALS AND METHODS
Bacterial strains, media, and plasmids.
X. azovorans KF46 was originally isolated from a soil inoculum after a prolonged enrichment with carboxy-Orange II [1-(4′-carboxyphenylazo)-2-naphtol] as sole source of carbon and energy (27). For the present study, strain KF46F DSM 13620 was used, which is a nonmucoid variant of strain KF46, which had been preserved freeze-dried during the last 25 years (T. Leisinger, personal communication). X. azovorans KF46F was routinely cultivated in a mineral medium with 4-hydroxybenzoate and Orange II, supplemented with proline and a trace element solution as described previously by Zimmermann et al. (49).
Escherichia coli DH5α and E. coli BL21(DE3)pLysS were used as host strains for recombinant DNA work. E. coli strains were routinely cultured at 37°C in Luria-Bertani medium which was supplemented with ampicillin (100 μg/ml), if appropriate.
The plasmid pBluescript II KS(+) (1) was used for most cloning experiments, and the plasmid vector pET11a (44) was used for high levels of expression.
Preparation of cell extracts.
The cells were suspended in 100 mM potassium phosphate buffer (pH 7.1) and disrupted by using a French press (Aminco, Silver Spring, Md.) at 80 or 125 MPa. Cell debris were removed by centrifugation at 100,000 × g for 30 min at 4°C. Protein was determined by the method of Bradford (7) using bovine serum albumin as a standard.
Standard assay for the determination of enzyme activities with cell extracts and purified enzyme preparations.
The standard enzyme assays contained in 1 ml 87 μmol of potassium phosphate buffer (pH 7.1), 1 μmol of NADH, 8 nmol of Orange II and different amounts of protein (1 to 600 μg). The reaction was spectrophotometrically assayed at room temperature at 482 nm (ɛ482 = 18.2 mM−1 cm−1). One unit of enzyme activity was defined as the amount of enzyme that catalyzed the decolorization of 1 μmol of substrate per min.
Conversion of different azo dyes by the azoreductase.
The reaction mixtures for the determination of the substrate specificity of the azoreductase contained in 1 ml 87 μmol of potassium phosphate buffer (pH 7.1), 1 μmol of NADH, and 25 nmol of the respective azo compounds and cell extracts (0.15 mg/ml) from E. coli BL21(DE3)pLysSpET-OII-Ex9, which expressed the azoreductase from X. azovorans KF46F. The relevant wavelengths and extinction coefficients for these dyes are summarized in Table 1.
TABLE 1.
Color index registration numbers, absorption maxima, purity, and calculated molar extinction coefficients of sulfonated azo dyes used in this studya
| Azo dye | CI number | Dye content (%) | Absorp- tion max (nm) | Extinction coefficient (mM−1 cm−1) |
|---|---|---|---|---|
| Acid Orange 7 (Orange II) | 15510 | 95 | 482 | 18.2 |
| Mordant Violet 5 (Violet N) | 15670 | NSb | 529 | 10.7 |
| Acid Orange 8 | 15575 | 65 | 486 | 27.4 |
| Acid Orange 12 (CroceinOrange G) | 15970 | 70 | 482 | 24.7 |
| Acid Red 66 (Ponceau BS) | 26905 | NS | 502 | 22.9 |
| Acid Red 88 | 15620 | 75 | 500 | 7.8 |
| Food Yellow 3 (Sunset Yellow FD6) | 15985 | NS | 480 | 19.8 |
| Solvent Yellow 14 (Sudan I) | 12055 | NS | 557 | 8.7 |
| Solvent Orange 7 (Sudan II) | 12140 | 90 | 559 | 4.3 |
| Solvent Red 23 (Sudan III) | 26100 | NS | 512 | 2.3 |
| Solvent Red 24 (Sudan IV) | 26105 | NS | 515 | 5.7 |
| Acid Orange 10 (Orange G) | 16230 | NS | 477 | 20.7 |
| Acid Red 18 (Neucoccin) | 16255 | NS | 507 | 19.9 |
| Acid Red 27 (Amaranth) | 16185 | 90 | 520 | 22.6 |
| Acid Black 52 (Palatine Fast Black WAN) | 15711 | 25 | 565 | 63.2 |
| Acid Red 151 | 26900 | 40 | 486 | 6.9 |
| 1-(2-Pyridylazo)-2-naphthol | NS | 445 | 7.7 | |
| Calconcarboxylic acid | NS | 555 | 3.2 | |
| Calmagite | NS | 539 | 9.9 |
The dyes were purchased from Fluka, Aldrich, or Sigma and not further purified. The absorption maxima were determined in NaK phosphate buffer (pH 7.4, 54 mM). The molar extinction coefficients were calculated using the dye purities indicated. If the dye purity was not indicated by the supplier, it was assumed that the preparations consisted of pure dye.
NS, dye purity not specified by the supplier.
Enzyme purification.
Protein was purified at room temperature by use of a fast-performance liquid chromatography system consisting of an LCC 500 controller, pump P-500, UV-1 monitor, conductivity monitor, REC-482 recorder, and FRAC autosampler from Amersham Pharmacia Biotech (Uppsala, Sweden).
X. azovorans KF46F was grown in a 10-liter fermentation vessel on a medium with 4-hydroxybenzoate (15 mM) and Orange II (0.2 mM) at 30°C as described above. The culture medium was intensively stirred (450 rpm). The optical density at 546 nm and the concentration of the azo dye (λmax = 482 nm) were determined spectrophotometrically. The cells were harvested by centrifugation during the exponential growth phase when the optical density reached an optical density at 546 nm of about 2 and a significant decolorization of Orange II was noticed. A crude extract was prepared using a French press, and 402 mg of protein was applied in two portions to a Red Sepharose CL-6B column (column volume, 32 ml; Amersham Pharmacia Biotech). Proteins that were not bound to the column were eluted with 0.1 M K-phosphate buffer (pH 8.5). The proteins bound to the column were subsequently eluted with 90 ml of a linear gradient of 0.1 M K-phosphate buffer into 0.1 M K-phosphate buffer plus 60 mM NADH at a flow rate of 1 to 2 ml/min. Fractions (4 ml each) were collected, and azo reductase activity was determined spectrophotometrically. The azoreductase was eluted as a single peak at a concentration of about 50 to 55 mM NADH. The active fractions were pooled (11 mg of protein, 12.2 U of azo reductase activity), and 0.5 M (NH4)2SO4 was added. The solution was incubated for 15 min on ice and finally filtered (Minisart NML [0.2-μm pore size]; Sartorius, Göttingen, Germany). This filtrate was transferred to an octyl-Sepharose column (column volume, 9 ml; Amersham Pharmacia Biotech). Protein was eluted with 120 ml of a linear gradient of K-phosphate buffer (0.1 M, pH 8.5) plus 0.5 M (NH4)2SO4 into K-phosphate buffer (0.1 M, pH 8.5) plus 50% (vol/vol) ethylene glycol at a flow rate of 0.1 to 0.3 ml/min. The active fractions (5 ml each) eluted at about 45 to 50% (vol/vol) ethylene glycol (0.72 mg of protein, 3.3 U of azoreductase activity). The fractions containing azoreductase activity were concentrated by ultrafiltration (Centricon 30; Amicon, Danvers, Mass.). The concentrated sample (about 1 ml) was applied to a Superdex 75 prep grade column (Amersham Pharmacia Biotech) and eluted with 90 ml of K-phosphate buffer (0.1 M, pH 7.1) at a flow rate of 1.5 ml/min. Fractions (0.5 ml each) with azoreductase activity were pooled.
Polyacrylamide gel electrophoresis.
Sodium dodecyl sulfate-polyacrylamide gel electrophoresis was performed by the method of Laemmli (28). Gels were silver stained by the method of Merril et al. (31) using the Amersham Pharmacia Biotech silver stain kit.
Determination of molecular weight.
The relative molecular mass of the native enzyme was determined by gel filtration using a Superdex 75 prep-grade column (Amersham Pharmacia Biotech) and appropriate standard proteins.
Protein cleavage, isolation of peptides, and sequencing of peptides and N termini.
The digestion of the azoreductase by trypsin (Sigma, Deisenhofen, Germany) and the subsequent separation of tryptic digests by reversed-phase high-pressure liquid chromatography (HPLC) were performed as described previously (43). The digestion of the enzyme with endoproteinase Glu-C (Sigma) was performed in Na-phosphate buffer (pH 7.8) in order to ensure a proteolytic cleavage of the enzyme on the carboxyl-side of glutamate or aspartate residues. For the digestions, 38 or 23 μg, respectively, of the purified azoreductase was incubated with 1.5 μg or 1 μg of trypsin or endoproteinase C, respectively. The digests were incubated for 24 h at 37°C, and the individual peptides were purified by reverse-phase HPLC. The amino acid sequences were determined by automated Edman degradation using an Applied Biosystems model 491 sequencer.
DNA manipulation techniques.
The genomic DNA was prepared as described by Ausubel et al. (3). Plasmid DNA from E. coli DH5α was isolated with the Flexi-Prep kit (Amersham Pharmacia Biotech) or the Qiaprep Spin Miniprep kit (Qiagen, Hilden, Germany). Digestion of DNA with restriction endonucleases (Gibco BRL, New England Biolabs, Frankfurt, Germany), electrophoresis, purification, and ligation with T4 DNA ligase (Gibco BRL) were performed according to the standard procedures (39). Transformation of E. coli was done by the method of Inoue et al. (20). For cloning of PCR products a T vector was prepared as described by Marchuk et al. (30).
PCR.
Oligonucleotides were custom synthesized according to the known or deduced sequences of the amino-terminal amino acid sequence and various internal peptides. PCR mixtures (50 μl) for the amplification of genomic DNA contained 50 pmol of each primer, 0.1 μg of genomic template DNA, a 0.1 mM concentration of each deoxynucleoside triphosphate, 0 to 7.5% (vol/vol) dimethyl sulfoxide, 1.5 mM MgCl2, 0.7 U of Taq DNA polymerase, and the corresponding reaction buffer (Gibco BRL).
For the amplification reaction with the primers deduced from the amino terminus and the internal peptides, the following PCR program was used: an initial denaturation (95°C, 3 min; addition of the Taq polymerase after 2 min) was followed by 29 cycles consisting of an annealing temperature of 50°C (1.5 min), a polymerization step (72°C, 2 min), and denaturation (95°C, 40 s). The last polymerization step was extended to 10 min.
The PCR products were initially cloned into the T-tailed EcoRV-site of pBluescript II KS(+) (30).
Hybridization procedures.
A digoxygenin DNA labeling and detection kit was used according to the instructions of the supplier (Boehringer Mannheim). The hybridization temperature was set to 68°C.
DNA sequencing and nucleotide sequence analysis.
The DNA sequence was determined by dideoxy chain termination with double-stranded DNA of clones and overlapping subclones in an automated DNA sequencing system (ALFexpress-Sequencer; Amersham Pharmacia Biotech) with fluorescently labeled primers or nucleotides.
Sequence analysis, database searches, and comparisons were done with the PCGene software package, release 6.85, and the BLAST search at the National Center for Biotechnology Information (NCBI). The alignment of the azoreductases was obtained with the program CLUSTAL using the default parameters.
Expression of the azoreductase in E. coli.
For expression in E. coli, azoB was inserted into pET11a (44) under the control of the phage T7 promoter. The DNA segment encompassing azoB was amplified by PCR with simultaneous introduction of an NdeI site upstream and a BamHI site downstream of azoB. The following oligonucleotide primers were used for the amplification: 5′-ATG ACA TAT GAT TCT GGT CGT CGG AGG AAC-3′ and 5′-GCG CGG ATC CGA CGG CAT CGA GAG CAT C. The amplified products were cleaved with NdeI and BamHI and ligated into pET11a. E. coli DH5α was transformed with the resulting plasmids. The plasmids were subsequently isolated and introduced into E. coli BL21(DE3)pLysS by transformation.
Chemicals.
The azo dyes and all other chemicals were obtained from Aldrich (Steinheim, Germany), Fluka (Buchs, Switzerland), Merck (Darmstadt, Germany), Sigma, and Gerbu Biotech (Gaiberg, Germany). The azo dyes Mordant Yellow 3 and 1-(4′-hydroxyphenylazo)-2-naphthol-6-sulfonate were kindly provided by Bayer AG (Leverkusen, Germany) and K. Bredereck (University of Stuttgart), respectively. The oligonucleotides were synthesized by MWG Biotech (Ebersberg, Germany).
Nucleotide sequence accession number.
The nucleotide sequence of the 5,782-bp SstI fragment was deposited in GenBank under accession number AF466104.
RESULTS
Purification of the aerobic azoreductase.
Xenophilus azovorans KF46F was grown in liquid culture on a mineral medium with 4-hydroxybenzoate (15 mM) and Orange II (0.2 mM) in order to achieve an optimal expression of the azoreductase. The azoreductase was purified from cell extracts by affinity chromatography using a Red Sepharose CL-6B column, a hydrophobic interaction chromatography and gel filtration as described in Materials and Methods. In this way the enzyme was purified about 400-fold, giving a specific activity of 10.8 U/mg of protein (Table 2). The purified enzyme gave a single band by sodium dodecyl sulfate-polyacrylamide gel electrophoresis with a molecular weight of approximately 30,000. This estimation was confirmed by the amino acid sequence of the protein deduced from the nucleotide sequence (see below). Surprisingly, the gel filtration indicated a molecular weight of the holoenzyme of less than 20,000. Therefore it can be assumed that the enzyme is a monomer which somehow behaved extraordinary during gel filtration. The results obtained agreed sufficiently with the results obtained previously by Zimmermann et al. (49) after a different purification procedure using the original strain KF46, who described the enzyme as a monomer with a molecular weight of 30,000.
TABLE 2.
Purification of aerobic azoreductase from X. azovorans KF46F
| Purification step | Total protein (mg) | Sp act (U/mg) | Total activity (U) | Recovery (%) | Purifi- cation (fold) |
|---|---|---|---|---|---|
| Crude extract | 402 | 0.027 | 10.9 | 100 | 1 |
| Red Sepharose CL-6B | 11 | 1.10 | 12.2 | 111 | 41 |
| Octyl-Sepharose + ultrafiltration | 0.7 | 4.5 | 3.3 | 30 | 165 |
| Gel filtration | 0.09 | 10.8 | 1.0 | 9 | 400 |
Determination of the NH2-terminal and some internal amino acid sequences.
The NH2-terminal amino acid sequence of the purified enzyme was determined by automated Edman degradation (Table 3). To obtain more sequence information, the purified protein was digested with trypsin and the fragments were separated by HPLC. Thus, the sequences of two fragments were determined (Table 4), which obviously overlapped each other and thus allowed us to deduce a peptide consisting of 26 amino acids. The azoreductase was also digested with endoproteinase Glu-C, which resulted in two additional amino acid sequences (Table 4).
TABLE 3.
Sequences of the amino terminus, tryptic peptides, and deduced primers
| Protein or peptide | Amino acid sequencea | Deduced primer sequence |
|---|---|---|
| Amino terminus | MILVVGGTGTI | |
| A (trypsin digest) | EEVDKVFVVTPLVPDQVQMR | 5′-GA(T/C)-AA(A/G)-GTI-TT(T/C)-GTN-GT-3′ |
| F (trypsin digest) A + F | TLPAALEEVDKVFVVTLPAALEEVDKV FVVTPLVPDQVQMR | |
| B (endoproteinase Glu-C digest) | SGMAWTFVQPGFFM | 5′-CA(A/G)-CCN-GGN-TT(T/C)-TT(T/C)-ATG-3′ or 3′-GT(T/C)-GGN-CCN-AA(A/G)-AA(A/G)-TAC-5′ |
| C (endoproteinase Glu-C digest) | LYALAPPGYLAGVLDTVPKVTGRPA |
Segments used for the design of oligonucleotides for PCR are underlined.
TABLE 4.
Regions of sequence similarity between deduced peptides from the sequenced DNA fragment from X. azovorans KF46F and sequences previously deposited at NCBIb
| Deduced peptide | Position in clone sequence | Size (aa) | Probable function of product | Source | % Identitya (aa) | Reference for homologous proteins |
|---|---|---|---|---|---|---|
| 1 | 4530-3949 | 194 | 3-Oxoacyl (acyl-carrier protein) reductase | Bacillus subtilis | 45 (79-246) | P51831 |
| 2 | 3890-2109 | 593 | Hypothetical protein | Methanococcus jannaschii | 37 (14-617) | Q58010 |
Percentage of amino acids that are identical when sequences were aligned with sequences listed in the GenBank database of the NCBI facilities.
aa, amino acids.
Cloning of the azoreductase gene.
The amino acid sequences of two peptides served for the design of oligonucleotide primers (Table 4). Using these primers and genomic DNA of strain KF46F as a template, an approximately 0.2-kb DNA fragment was amplified. This PCR product was cloned into a pBluescript II KS(+) T vector and sequenced. In the deduced amino acid sequence the amino acid sequence of a part of fragment A (Table 4) was found which had not been used for the design of the oligonucleotide primers. It was therefore deduced that indeed a fragment of the azoreductase gene from strain KF46F had been amplified. The PCR fragment was labeled using digoxigenin-labeled dUTP residues and used as a probe to identify by Southern hybridization the complete azoreductase gene. Thus, hybridization signals were found with an approximately 6-kb SstI fragment, a 3-kb EcoRI fragment, and a 2-kb PstI fragment from the total DNA of strain KF46F. Finally, the probe was used to identify the complete gene in a size-selected gene bank obtained by SstI digestion of the genomic DNA of strain KF46F. This plasmid carrying an approximately 6-kb SstI fragment cloned into plasmid pBluescript II SK(+) was designated pBlue-OII-S3-59.
Determination of the nucleotide sequence of the azoreductase gene and the surrounding DNA fragments.
The DNA sequence of the insert in plasmid pBlue-OII-S3-59 was determined and a continuous DNA fragment of 5,782 bp sequenced. The gene for the azoreductase (azoB) was unequivocally identified on the cloned fragment by the presence of the amino-terminal region and the internal peptides determined by Edman degradation (Fig. 1). The gene encoded a protein consisting of 281 amino acids, which corresponded to a molecular mass of 30,278 Da. An NAD(P)H binding site could be clearly identified near the amino terminus of the deduced protein sequence. The presence of an arginine residue as the 10th conserved amino acid sequence in this NAD(P)H-binding site indicated that the azoreductase binds in vivo preferentially NADPH (34). This corresponds with the biochemical data of Zimmermann et al. (49), who determined Km values of the azoreductase for NADPH and NADH of 5 and 180 μM, respectively. A BLAST search using the deduced amino acid sequence of azoB did not identify proteins with significantly similar sequences. The highest degrees of sequence identities (24.2 to 16.4%) were found with a hypothetical protein (P39315) in E. coli, a hypothetical protein from the chloroplast of Guillardia theta (O78472), a hypothetical protein from the cyanelle of Cyanophora paradoxa (P48279), a regulatory protein (P23762) from the nitrogen metabolism of Neurospora crassa, and a homologous protein of the isoflavone reductase from Arabidopsis thaliana (P52577). In all these cases the major regions of sequence identity were within the highly conserved NAD(P)H-binding region. No significant sequence similarity was detected with the recently described aerobic azoreductase from Bacillus sp. OY1-2 (AB032601 [46]).
FIG. 1.
DNA sequence and amino acid sequence of the azoreductase from X. azovorans KF46F. The N-terminal and two internal amino acid sequences, which were determined by chemical Edman degradation, are underlined. The stop codon is indicated by a dash. The amino acids putatively involved in NAD(P)H binding are boxed.
Because these sequence comparisons did not give any indications about the putative evolutionary origin of the azoreductase, also the DNA sequences upstream and downstream of azoB were analyzed. Two putative regions of homology with sequences deposited at the NCBI were found downstream of the azoreductase gene, but these sequences demonstrated sequence similarities only for parts of the reference sequences deposited at the NCBI and are probably also not parts of open reading frames in the DNA from strain KF46F (Table 4).
Expression of the azoreductase in E. coli.
The azoreductase gene was amplified by PCR from the genomic DNA of strain KF46F using a set of primers which created new NdeI and BamHI restriction sites and was functionally expressed in E. coli using a phage T7-promoter system. Cell extracts were prepared from cultures of E. coli BL21(DE3)pLysS carrying the expression plasmid, which had been induced by the addition of IPTG (isopropyl-β-d-thiogalactopyranoside). After 6 h of induction an azoreductase activity of 1.3 U/mg of protein was obtained, which was almost 50 times higher than the activity observed in cell extracts of X. azovorans KF46F.
Comparison of the in vivo- and in vitro-reduction rates for azo dyes by the recombinant E. coli strain.
It has been repeatedly suggested that the metabolism of sulfonated azo dyes would be restricted by the limited permeability of bacterial cell membranes for the highly polar sulfonated azo dyes (13, 17, 37, 47). Because a recombinant azoreductase is now available, it was attempted to experimentally verify this proposal. The recombinant strain E. coli BL21(DE3)pLysSpET-OII-Ex9 was grown in Luria-Bertani medium, and the azoreductase gene was induced by the addition of IPTG. Then the culture was split into two parts, and from one part of the cells a cell extract was prepared. Finally, the azoreductase activities of the resting cells and a cell extract prepared from the same cells were compared. Thus, it was observed that the cell extract demonstrated an azoreductase activity of about 0.8 U/mg of protein. In contrast, for the resting cell suspension no detectable azoreductase activity was found. When resting cells were stirred on a vortex mixer with toluene (25 μl per ml of cell suspension) for 3 min prior to the assay, a low but clearly measurable decolorization activity was detected (0.0012 U/mg of protein), which was increased approximately 10 times by the addition of NADPH (1 mM) to the whole-cell assay. These experiments suggested that for the recombinant E. coli strain the missing transport of the sulfonated dye into the cells was indeed a limiting factor which prevented the metabolism of the sulfonated azo dye by whole cells. Furthermore, it is apparent that under the test conditions using resting cells also the NADPH supply may become limiting for the reduction of azo dyes.
Substrate specificity of the azoreductase.
The previous biochemical characterization of the azoreductase from strain KF46 demonstrated that the enzyme converted a wide range of specifically synthesized model compounds, which contained a hydroxy group in ortho position towards the azo group (49). Because azo dyes with this basic structure are rather widely used as industrial dyestuff, it was tested in the present study if the recombinantly expressed azoreductase would also convert industrially relevant dyes (Table 5). These experiments demonstrated that the azoreductase decolorized several azo dyes carrying a hydroxy group in the 2 position of the naphthol ring and confirmed previous suggestions (49) that electron-withdrawing groups on the phenyl ring accelerated the reactions, while a charged functional group in proximity to the azo group or the presence of a second polar group interfered with the reaction. This was especially evident when those (few) dyes were analyzed which fulfilled the basic structural requirement of the enzyme (a hydroxy group in ortho position to the azo group) but which were not converted. In almost all of these substrates two sulfonic acid groups were attached to the naphthalene ring system (Table 5).
TABLE 5.
Relative activities of the azoreductase from X. azovorans KF46F with different azo dyesa

The tests contained in 1 ml 87 μmol of potassium phosphate buffer (pH 7.1), 1 μmol NADH, 25 nmol of the respective azo compounds, and cell extracts (0.15 mg/ml) from E. coli BL21(DE3)pLysSpET-OII-Ex9. The enzyme activities were determined at the absorption maxima of the respective dyes indicated in Table 1. The dyes were added from aqueous or ethanolic (*) stock solutions. The reaction rates are expressed as percentages of that for Orange II (100%). The activities with the dyes added from aqueous stock solutions were related to the activity of the enzyme with Orange II in a purely aqueous system (0.57 U/mg of protein), and those with the dyes from the ethanolic stock solutions with activity for Orange II in the presence of 1% (vol/vol) ethanol (0.14 U/mg of protein) were taken, respectively, as 100% enzyme activity.
DISCUSSION
This paper is the second example of the analysis of an aerobic azoreductase on the genetic level. Recently, Suzuki et al. (46) cloned an aerobic azoreductase from a Bacillus strain (OY1-2). This strain was originally isolated for its ability to decolorize low concentrations (0.02%) of the azo dye Acid Red 88 [C.I. 15620, 2′-hydroxy-(1,1′)-azonaphthalene-4-sulfonate] while growing on agar plates on a nutrient medium (45). Both azoreductases from Bacillus sp. strain OY1-2 and X. azovorans KF46F were able to decolorize Acid Red 88 and Acid Orange 7, but unfortunately only very limited conclusions can be drawn about the substrate specificity of the azoreductase from Bacillus sp. strain OY1-2 because with this enzyme mainly proprietary reactive dyes of unpublished structure have been tested (45). Similarly to the azoreductase studied in the present paper, also the azoreductase from Bacillus sp. OY1-2 was found to be a rather small monomeric protein with a molecular mass of approximately 20 kDa (compared to about 30 kDa for the enzyme from strain KF46F) (46). Surprisingly, no other similarities were observed among both aerobic azoreductases. Thus, a sequence alignment of both azoreductases did not show any noticeable homology between the deduced amino acid sequences. Furthermore, it was suggested that the azoreductase from Bacillus sp. strain OY1-2 contains an NAD(P)H-binding motif (GXGXXG) at positions 106 to 111 of the protein and not at the amino terminus as found in the present study for the enzyme from X. azovorans KF46F.
The existence of two nonhomologous aerobic azoreductases is somehow surprising, because of the great problems that have been observed when trying to isolate microorganisms with the ability to grow aerobically with sulfonated azo dyes (4, 25, 26, 27). On the other hand, it had been shown that it is easy to isolate bacteria with rather simple azo compounds such as 4,4′-dicarboxyazobenzene (19, 32), which form aromatic amines after the reductive cleavage that can be mineralized aerobically by many bacteria. Thus, it may be possible that the major problem in the isolation of aerobic bacteria with the ability to degrade the commercially important sulfonated azo dyes is either the limited transport of the dyes into the cells or the high reactivity of many of the ortho-aminohydroxyaromatics which are formed after the reductive cleavage of the azo dyes. These cleavage products can escape a productive degradation because of their spontaneous auto-oxidation reactions and can also harm the cells by futile redox cycles or the formation of addition products between the quinoneimines or quinones and various cell constituents (18, 23).
A rather astonishing observation from the enzymatic and molecular studies about aerobic azoreductases is that the enzyme from strain KF46F [and also the aerobic azoreductases from P. kullae (formerly Pseudomonas sp.) K22 and Bacillus strain OY1-2)] are rather simple polypeptides which do not contain any metal ions or enzyme bound cofactors (46, 48, 49). This is surprising because the complete reduction of the azo compounds to the respective amines requires 2 mol of NAD(P)H and thus a rather complex coordinated four-electron reduction, which may occur either by a simultaneous reduction process or by two subsequent coordinated two-electron transfers. This may indicate that the azoreductases mainly catalyze the reduction of the azo dyes to the corresponding hydrazo compounds. These may then be reduced spontaneously in the presence of NAD(P)H to the corresponding amines or undergo a spontaneous disproportionation to an iminoquinone and an aminoaromatic compound, as previously suggested for the chemical or anaerobic reduction of azo compounds (13, 16). This mechanism would require a rapid spontaneous reduction of the iminoquinones (or the naphthoquinones formed from the hydrolysis of the iminoquinones) to the aminohydroxy (or dihydroxy) compounds, because the enzyme demonstrates a rather fixed ratio of 2 mol of NAD(P)H consumed per mol of azo compound cleaved (49).
The experiments with the recombinant E. coli strain gave some further indications that the metabolism of sulfonated azo dyes is apparently often limited by the transport of the highly charged dyes into the microbial cells. This has already previously been suggested for the intracellular reduction of sulfonated azo dyes under anaerobic conditions (13, 17, 37, 38, 47) and has now been substantiated also for the aerobic metabolism of this class of compounds. This suggests that microbial strains with the ability to decolorize sulfonated azo dyes intracellularly will require not only the presence of azoreductases but also a transport system(s) which allows the uptake of the sulfonated dyes into the cells. Currently there is no information available about transport systems for sulfonated azo dyes, but there are some reports about specific transport systems which are involved in the transport of other kinds of sulfonated substrates into bacterial cells (e.g., p-toluenesulfonate, taurine or alkanesulfonates) (14, 21, 29). Functionally similar transport systems are expected to exist also in bacteria (e.g., Hydrogenophaga intermedia S1 or Sphingomonas xenophaga BN6), which are able to grow aerobically on aminobenzene- or aminonaphthalenesulfonates, which are structural elements of many sulfonated azo dyes (12, 15, 41). Furthermore, it is clear that whole cells of strain KF46 are able to take up Orange II and to reduce this sulfonated dye in vivo (27). In order to construct recombinant organisms with the ability to decolorize sulfonated azo dyes in vivo, it therefore may be necessary to transfer the gene for the aerobic azo reductase into bacterial strains which are able to grow with sulfonated aromatics.
Acknowledgments
We thank S. Bürger, J. Altenbuchner, and E. Dabbs for practical, theoretical, and linguistic help during the final completion of the manuscript.
REFERENCES
- 1.Alting-Mees, M. A., J. A. Sorge, and J. M. Short. 1992. pBluescriptII: multifunctional cloning and mapping vectors. Methods Enzymol. 216:483-495. [DOI] [PubMed] [Google Scholar]
- 2.Anliker, R. 1979. Ecotoxicology of dyestuffs: a joint effort by industry. Ecotox. Environ. Safety 3:59-74. [DOI] [PubMed] [Google Scholar]
- 3.Ausubel, F. M., R. Brent, R. E. Kingston, D. D. Moore, J. G. Seidman, J. A. Smith, and K. Struhl (ed.). 1987. Current protocols in molecular biology, vol. 1. John Wiley & Sons, Inc., New York, N.Y.
- 4.Blümel, S., M. Contzen, M. Lutz, A. Stolz, and H.-J. Knackmuss. 1998. Isolation of a bacterial strain with the ability to utilize the sulfonated azo compound 4-carboxy-4′-sulfoazobenzene as sole source of carbon and energy. Appl. Environ. Microbiol. 64:2315-2317. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Blümel, S., H.-J. Busse, A. Stolz, and P. Kämpfer. 2001. Xenophilus azovorans gen. nov., sp. nov., a soil bacterium able to degrade azo dyes of the Orange II type. Int. J. Syst. E vol. Bacteriol. 51:1831-1837. [DOI] [PubMed] [Google Scholar]
- 6.Blümel, S., B. Mark, H.-J. Busse, P. Kämpfer, and A. Stolz. 2001. Pigmentiphaga kullae gen. nov., sp. nov., a new member of the family Alcaligenaceae with the ability to decolorize aerobically azo dyes. Int. J. Syst. E vol. Bacteriol. 51:1867-1871. [DOI] [PubMed] [Google Scholar]
- 7.Bradford, M. M. 1976. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Anal. Biochem. 72:248-254. [DOI] [PubMed] [Google Scholar]
- 8.Bumpus, J. A. 1995. Microbial degradation of azo dyes, p. 157-167. In V. P. Singh (ed.), Microbial degradation of health risk compounds. Elsevier, Amsterdam, The Netherlands.
- 9.Chudgar, R. J. 1985. Azo dyes, p. 821-875. In J. I. Kroschwitz (ed.), Kirk-Othmer encyclopedia of chemical technology, 4th ed., vol. 3. John Wiley, New York, N.Y. [Google Scholar]
- 10.Chung, K.-T., S. E. Stevens, and C. E. Cerniglia. 1992. The reduction of azo dyes by the intestinal microflora. Crit. Rev. Microbiol. 18:175-190. [DOI] [PubMed] [Google Scholar]
- 11.Clarke, A., and R. Anliker. 1980. Organic dyes and pigments, p. 181-215. In O. Hutzinger (ed.), The handbook of environmental chemistry, vol. 3, part A. Anthropogenic compounds. Springer-Verlag, New York, N.Y.
- 12.Contzen, M., E. R. B. Moore, S. Blümel, A. Stolz, P. Kämpfer. 2000. Hydrogenophaga intermedia sp. nov., a 4-aminobenzenesulfonate degrading organism. Syst. Appl. Microbiol. 23:487-493. [DOI] [PubMed] [Google Scholar]
- 13.Dubin, P., and K. L. Wright. 1975. Reduction of azo food dyes in cultures of Proteus vulgaris. Xenobiotica 5:563-571. [DOI] [PubMed] [Google Scholar]
- 14.Eichhorn, E., J. R. VanderPloeg, and T. Leisinger. 2000. Deletion analysis of the Escherichia coli taurine and alkanesulfonate transport systems. J. Bacteriol. 182:2687-2695. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Feigel, B. J., and H.-J. Knackmuss. 1993. Syntrophic interactions during degradation of 4-aminobenzenesulfonic acid by a two species bacterial culture. Arch. Microbiol. 159:124-130. [DOI] [PubMed] [Google Scholar]
- 16.Florence, T. M. 1965. Polarography of aromatic azo compounds. II. Kinetic study of the disproportionation of 4-aminohydrazobenzene-4′-sulphonic acid. Aust. J. Chem. 18:619-626. [Google Scholar]
- 17.Gingell, R., and R. Walker. 1971. Mechanism of azo reduction by Streptococcus faecalis. II. The role of soluble flavins. Xenobiotica 1:231-239. [DOI] [PubMed] [Google Scholar]
- 18.Grundmann, C. 1979. Ortho-Chinone, p. 144. In C. Grundmann (ed.), Methoden der organischen Chemie (Houben-Weyl), 4th ed., vol. 7/3b, part II. Chinone. Georg Thieme Verlag, Stuttgart, Germany. [Google Scholar]
- 19.Hausser, A. 1995. Abbau von 4,4′-Dicarboxyazobenzol durch einen neu isolierten Bakterienstamm. Studienarbeit. Universität Stuttgart, Stuttgart, Germany.
- 20.Inoue, H., H. Nojima, and H. Okayama. 1990. High efficiency transformation of Escherichia coli with plasmids. Gene 96:23-28. [DOI] [PubMed] [Google Scholar]
- 21.Kahnert, A., P. Vermeij, C. Wietek, P. James, T. Leisinger, and M. A. Kertesz. 2000. The ssu locus plays a key role in organosulfur metabolism in Pseudomonas putida S-313. J. Bacteriol. 182:2869-2878. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Keck, A., J. Klein, M. Kudlich, A. Stolz, H.-J. Knackmuss, and R. Mattes. 1997. Reduction of azo dyes by mediators originating in the naphthalenesulfonic acid degradation pathway of Sphingomonas sp. strain BN6. Appl. Environ. Microbiol. 63:3684-3690. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Kudlich, M., M. J. Hetheridge, H.-J. Knackmuss, and A. Stolz. 1999. Autoxidation reactions of different aromatic ortho-aminohydroxynaphthalenes which are formed during the anaerobic reduction of sulfonated azo dyes. Environ. Sci. Technol. 33:896-901. [Google Scholar]
- 24.Kudlich, M., A. Keck, J. Klein, and A. Stolz. 1997. Localization of the enzyme system involved in the anaerobic reduction of azo dyes by Sphingomonas sp. strain BN6 and effect of artificial redox mediators on the rate of azo dye reduction. Appl. Environ. Microbiol. 63:3691-3694. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Kulla, H. G. 1981. Aerobic bacterial degradation of azo dyes, p. 387-399. In T. Leisinger, A. M. Cook, J. Nüesch, and R. Hütter (ed.), Microbial degradation of xenobiotics and recalcitrant compounds. Academic Press, London, United Kingdom.
- 26.Kulla, H. G., F. Klausener, U. Meyer, B. Lüdeke, and T. Leisinger. 1983. Interference of aromatic sulfo groups in the microbial degradation of the azo dyes Orange I and Orange II. Arch. Microbiol. 135:1-7. [Google Scholar]
- 27.Kulla, H. G., R. Krieg, T. Zimmermann, and T. Leisinger. 1984. Experimental evolution of azo dye-degrading bacteria, p. 663-667. In M. J. Klug and C. A. Reddy (ed.), Current perspectives in microbial ecology. American Society for Microbiology, Washington, D.C.
- 28.Laemmli, U. K. 1970. Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature (London) 227:680-685. [DOI] [PubMed] [Google Scholar]
- 29.Locher, H. H., B. Poolman, A. M. Cook, and W. N. Konings. 1993. Uptake of 4-toluene sulfonate by Comamonas testosteroni T-2. J. Bacteriol. 175:1075-1080. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Marchuk, D., M. Drumm, A. Saulino, and F. S. Collins. 1991. Construction of T-vectors, a rapid and general system for direct cloning of unmodified PCR products. Nucleic Acids Res. 19:1154. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Merril, C. R., D. Goldman, S. A. Sedman, and M. H. Ebert. 1981. Ultrasensitive stain for proteins in polyacrylamide gels shows regional variations in cerebrospinal fluid proteins. Science 211:1437-1438. [DOI] [PubMed] [Google Scholar]
- 32.Overney, G. 1979. Ueber den aeroben Abbau von Dicarboxyazobenzol durch ein Flavobacterium sp. Ph.D. thesis ETH 6421. ETH Zürich, Zürich, Switzerland.
- 33.Pagga, U., and D. Brown. 1986. The degradation of dyestuffs: part II-behaviour of dyestuffs in aerobic biodegradation tests. Chemosphere 15:479-491. [Google Scholar]
- 34.Quandt, K. S., and D. E. Hultquist. 1994. Flavin reductase. Sequence of cDNA from bovine liver and tissue distribution. Proc. Natl. Acad. Sci. USA 91:9322-9326. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Rau, J., H.-J. Knackmuss, and A. Stolz. 2002. Effects of different quinoid redox mediators on the anaerobic reduction of azo dyes by bacteria. Environ. Sci. Technol. 36:1497-1504. [DOI] [PubMed] [Google Scholar]
- 36.Reisch, M. S. 1996. Asian textile dye makers are a growing power in changing market. Chem. Eng. News 15:10-12. [Google Scholar]
- 37.Roxon, J. J., A. J. Ryan, and S. E. Wright. 1967. Enzymatic reduction of tartrazine by Proteus vulgaris from rats. Fd. Cosmet. Toxicol. 5:645-656. [DOI] [PubMed] [Google Scholar]
- 38.Russ, R., J. Rau, and A. Stolz. 2000. The function of cytoplasmatic flavin reductases in the reduction of azo dyes by bacteria. Appl. Environ. Microbiol. 66:1429-1434. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Sambrook, J., E. F. Fritsch, and T. Maniatis. 1989. Molecular cloning: a laboratory manual, 2nd ed. Cold Spring Harbor Press, Cold Spring Harbor, N.Y.
- 40.Shaul, G. M., T. J. Holdsworth, C. R. Dempsey, and K. A. Dostal. 1991. Fate of water soluble azo dyes in the activated sludge process. Chemosphere 22:107-119. [Google Scholar]
- 41.Stolz, A. 1999. Degradation of substituted naphthalenesulfonic acids by Sphingomonas xenophaga BN6. J. Ind. Microbiol. Biotechnol. 23:391-399. [DOI] [PubMed] [Google Scholar]
- 42.Stolz, A. 2001. Basic and applied aspects in the microbial degradation of azo dyes. Appl. Microbiol. Biotechnol. 56:69-80. [DOI] [PubMed] [Google Scholar]
- 43.Stone, K. L., M. B. LoPresti, J. M. Crawford, R. DeAngelis, and K. R. Williams. 1989. Enzymatic digestion of proteins and HPLC peptide isolation, p. 31-47. In P. T. Matsudaira (ed.), A practical guide to protein and peptide purification for microsequencing. Academic Press, Inc. San Diego, Calif.
- 44.Studier, F. W., and B. A. Moffatt. 1986. Use of bacteriophage T7 RNA polymerase to direct selective high-level expression of cloned genes. J. Mol. Biol. 189:113-130. [DOI] [PubMed] [Google Scholar]
- 45.Sugiura, W., T. Miyashita, T. Yokoyama, and M. Arai. 1999. Isolation of azo-dye degrading microorganisms and their application to white discharge printing of fabric. J. Biosci. Bioeng. 88:577-581. [DOI] [PubMed] [Google Scholar]
- 46.Suzuki, Y., T. Yoda, A. Ruhul, and W. Sugiura. 2001. Molecular cloning and characterization of the gene coding for azoreductase from Bacillus sp. OY1-2 isolated from soil. J. Biol. Chem. 276:9059-9065. [DOI] [PubMed] [Google Scholar]
- 47.Wuhrmann, K., K. Mechsner, and T. Kappeler. 1980. Investigation on rate-determining factors in the microbial reduction of azo dyes. Eur. J. Appl. Microbiol. 9:325-338. [Google Scholar]
- 48.Zimmermann, T., F. Gasser, H. G. Kulla, and T. Leisinger. 1984. Comparison of two azoreductases acquired during adaptation to growth on azo dyes. Arch. Microbiol. 138:37-43. [DOI] [PubMed] [Google Scholar]
- 49.Zimmermann, T., H. G. Kulla, and T. Leisinger. 1982. Properties of purified Orange II azoreductase, the enzyme initiating azo dye degradation by Pseudomonas KF46. Eur. J. Biochem. 129:197-203. [DOI] [PubMed] [Google Scholar]
- 50.Zollinger, H. 1991. Color chemistry, 2nd ed. VCH, Weinheim, Germany.

