Biodegradation of para-Nitrophenol (PNP) proceeds via two distinct pathways, having 1,2,3-benzenetriol (BT) and hydroquinone (HQ) as their respective terminal aromatic intermediates. Genes involved in these pathways have already been studied in different PNP degrading bacteria. Burkholderia sp. strain SJ98 degrades PNP via both the pathways. Earlier, we have sequenced and analyzed a ~41 kb fragment from the genomic library of strain SJ98. This DNA fragment was found to harbor all the lower pathway genes; however, genes responsible for the initial transformation of PNP could not be identified within this fragment. Now, we have sequenced and annotated the whole genome of strain SJ98 and found two ORFs (viz., pnpA and pnpB) showing maximum identity at amino acid level with p-nitrophenol 4-monooxygenase (PnpM) and p-benzoquinone reductase (BqR). Unlike the other PNP gene clusters reported earlier in different bacteria, these two ORFs in SJ98 genome are physically separated from the other genes of PNP degradation pathway. In order to ascertain the identity of ORFs pnpA and pnpB, we have performed in-vitro assays using recombinant proteins heterologously expressed and purified to homogeneity. Purified PnpA was found to be a functional PnpM and transformed PNP into benzoquinone (BQ), while PnpB was found to be a functional BqR which catalyzed the transformation of BQ into hydroquinone (HQ). Noticeably, PnpM from strain SJ98 could also transform a number of PNP analogues. Based on the above observations, we propose that the genes for PNP degradation in strain SJ98 are arranged differentially in form of non-contiguous gene clusters. This is the first report for such arrangement for gene clusters involved in PNP degradation. Therefore, we propose that PNP degradation in strain SJ98 could be an important model system for further studies on differential evolution of PNP degradation functions.
Citation: Vikram S, Pandey J, Kumar S, Raghava GPS (2013) Genes Involved in Degradation of para-Nitrophenol Are Differentially Arranged in Form of Non-Contiguous Gene Clusters in Burkholderia sp. strain SJ98. PLoS ONE 8(12): e84766. doi:10.1371/journal.pone.0084766
Editor: Asad U Khan, Aligarh Muslim University, India
Received: July 17, 2013; Accepted: November 18, 2013; Published: December 23, 2013
Copyright: © 2013 Vikram et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This study was partly supported by Council for Scientific and Industrial Research (CSIR), India and Department of Biotechnology (DBT), India. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: One of the co-authors, Gajendra Raghava, is a PLOS ONE Editorial Board member. This does not alter the authors’ adherence to all the PLOS ONE policies on sharing data and materials.
para-Nitrophenol (PNP) is a toxic and bio-refractory organic pollutant which releases into the environment via industrial waste and agricultural application of parathion and methyl parathion derived pesticides [1-4]. It has been categorized as a priority environmental pollutant and is reported to be hazardous to humans, and a number of animal models [5-7]. Several bacterial strains have been isolated and characterized for their ability to metabolize PNP as the sole source of carbon, nitrogen and energy [8-15]. Furthermore, two mutually independent oxidative pathways for microbial aerobic degradation of PNP have also been well elucidated in number of PNP degrading bacteria. The 1,2,4-benzenetriol (BT) pathway, commonly reported in Gram-positive bacteria, proceeds via transformation of PNP to BT [13,16]. On the other hand, hydroquinone (HQ) pathway, preferentially found in Gram-negative bacteria involves conversion of PNP to hydroquinone (HQ) via p-benzoquinone (BQ) . A few studies have reported for cloning and characterization of gene(s) and/or gene cluster(s) involved in PNP degradation via BT pathway and HQ pathway [16,18-21]. Interestingly, only a very few studies have reported deviation from the above generalization with regards to distribution of PNP degradation pathways amongst Gram positive and Gram negative bacterial isolates. Recently, Zhang et al., (2012) have shown involvement of both 4-Nitrocatechol (NC)/BT and HQ pathways for degradation of PNP in Pseudomonas sp. 1-7 . In a concurrent report, we have also shown the involvement of both BT and HQ pathways in the degradation of PNP by Burkholderia sp. strain SJ98 . The biochemical analysis of samples collected during growth and resting cell studies with strain SJ98 on PNP showed the presence of characteristic intermediates of BT and HQ pathways. Additionally, annotation and genetic characterization of ~41 kb DNA fragment of a cosmid clone screened from the genomic library of strain SJ98 for harboring the open reading frame (ORF) pnpC which encodes for benzenetriol dioxygenase (BtD) has shown the presence of 5 ORFs (i.e., pnpE2, pnpE1, pnpF, pnpD and pnpC). These ORFs were later identified for encoding small subunit of Hydroquinone dioxygenase (HqD-SS), large subunit of Hydroquinone dioxygenase (HqD-LS), 4-Hydroxymuconic semialdehyde dehydrogenase (4-HMSD), BtD and Maleylacetate reductase (MaR) respectively [21,23]. The first three enzymes are well established for catalyzing reactions involved in the degradation of PNP via HQ pathway [17,24-26], while the latter two are known to be involved in BT pathway [13,16,20]. Noticeably, this ~41 kb DNA fragment did not show the presence of any gene(s) corresponding to the initial reaction(s) of either of the above two pathways .
In the present study, we have identified two ORFs (pnpA and pnpB) after the whole genome sequencing and annotation of strain SJ98 . These ORFs share maximum sequence identity at amino acid level with previously characterized p-nitrophenol 4-monooxygenase (PnpM) and p-benzoquinone reductase (BqR) respectively. Surprisingly, ORFs pnpA and pnpB in strain SJ98 are found to be physically separated and positioned very far from all other genes involved in PNP degradation (identified earlier to be located on ~41 kb genomic fragment). Biochemical characterization of purified PnpA ascertained its identity as PnpM with NADH/FAD dependent oxidoreductase activity. In in-vitro activity assays, it catalyzed monooxygenation of PNP. Purified PnpB transformed BQ to HQ in the presence of NAD(P)H/FMN and therefore, its identity was ascertained as a BqR. This is the first report for such type of genetic arrangement of PNP degrading genes in any bacteria. In this report, we also presented a comparison of PNP degradation gene cluster identified and characterized from strain SJ98 with PNP degradation gene clusters of other bacteria. It is proposed that this study will enhance the understanding of ‘genetic and functional diversity’ of PNP degradation in microorganisms. Further, based on these observation it can be proposed that this strain could be used as a model system for studying the ‘phylogenetic evolution’ of the genes involved in microbial degradation of PNP and potentially other related nitroaromatic compounds, e.g. chloro-nitrophenols.
Materials and Methods
Bacterial strains, plasmids, primers, media and culture conditions
Bacterial strains and plasmids used in the present study are listed in table S1 while primers are listed in table S2. Cultures of strain SJ98 were grown in minimal salt medium (MSM) supplemented with appropriate concentrations (100–300 µM) of nitroaromatic compounds/degradation intermediates. MSM was prepared according to the composition as described earlier by Pandey et al., (2012) . Wild type strain SJ98 was maintained on nutrient rich media (nutrient agar, nutrient broth) prepared according to the manufacturer’s suggestion. E. coli BL21 AI, E. coli Top10 and recombinant E. coli strains were grown in Luria-Bertani medium. Filter sterilized antibiotic viz., ampicillin or kanamycin was added at a final concentration of 100 μg ml-1 or 50 μg ml-1 respectively, wherever required. Cultures of strain SJ98 were grown at 30°C with aeration (180-200 rpm) while E. coli strains were grown at different incubation temperatures (25°C, 30°C and 37°C) with aeration (200 rpm) as required.
The standards of p-nitrophenol (PNP), m-nitrophenol (MNP), o-nitrophenol (ONP), 4-nitrocatechol (4-NC), Benzoquinone (BQ), Hydroquinone (HQ), chlorohydroquninone (CHQ), 3-methyl-4-nitrophenol (3M4NP), 2-chloro-4-nitrophenol (2C4NP), 4-chloro-3-nitrophenol (4C3NP), 4-chloro-2-nitrophenol (4C2NP), 2,6-dichlorophenol (2,4-DCP) 2,4-dinitrophenol (2,4DNP) and 2,5-dinitrophenol (2,5-DNP), and all expected metabolites were obtained from Sigma Aldrich, (St, Louis, MO, USA). All other chemicals used in the study were of the purest grade available.
Sequencing and analysis of strain SJ98 genome
Whole genome of Burkholderia sp. strain SJ98 was sequenced on Roche’s 454 and Illumina GAIIX platform; annotated by RNAmmer  and PGAAP pipeline. Annotated genome sequence is now available at National Center for Biotechnology Information (NCBI) GenBank database .
Identification of pnpA and pnpB
The annotated genome sequence of strain SJ98 was searched and analyzed for the presence of ORFs with the putative function of PnpM and BqR. ORFs were identified using the ORF Finder program on the NCBI website (http://www.ncbi.nlm.nih.gov/projects/gorf). The deduced proteins were examined for sequence similarity with other proteins in the NCBI, GenBank database using BLASTN and BLASTP modules available from NCBI . These analyses showed the presence of two physically associated ORFs (pnpA and pnpB) with maximum amino acid identity and putative functions of PnpM and BqR respectively. These ORFs were selected for further validation and characterization with heterologous expression, purification and biochemical studies.
Comparison of PNP degrading gene clusters
Nucleotide sequences of previously characterized PNP degradation gene clusters were obtained from the GenBank (NCBI), and these sequences were saved into FASTA format. Analysis of ORFs orientation and comparison were done by Vector NTI v11.5.1 software (Invitrogen, life technologies, USA).
Cloning and expression of pnpA and pnpB
DNA fragments corresponding to ORFs pnpA and pnpB were amplified from SJ98 genome using Hot-Star™ High-Fidelity Taq DNA Polymerase (Qiagen, GmBH, Germany) and primer pairs as listed in table S2. These primers were designed to incorporate attB sites corresponding to recombination site of the GatewayTM entry vector (Invitrogen Inc. CA, USA) according to the manufacturer’s recommendations. The thermocycler program for amplifications was as follows: initial denaturation of genomic DNA at 95°C for 10 min followed by 29 cycles of denaturation at 95°C for 1 min, primer annealing at 55°C for 30 seconds and extension at 72°C for 2 min. Final extension was carried out at 72°C for 10 min. Resulting amplicons were analyzed with 1.0% agarose gel electrophoresis. Single amplicons with expected size for pnpA and pnpB were cloned in GatewayTM entry vector pDONR221 using BP clonase enzyme (Invitrogen Inc. CA, USA) according to manufacturer’s recommendations. Sequences of the cloned amplicons were verified to ensure that no mutation has been introduced during PCR reaction. Sequencing of the amplicon was carried out with ABI-3130xl Genetic analyzer capillary sequencer (Applied Biosystems- Life Technologies, USA) using vector specific primers as shown in table S2. Subsequently, Gateway LR reactions were carried out to sub-clone pnpA and pnpB into the GatewayTM N-terminal His-Tag expression vector viz., pDEST17. Recombinant plasmids obtained from the sub-cloning reactions were transformed into E. coli BL21-AITM (Invitrogen Inc. CA, USA) cell for protein expression according to the manufacturer’s instruction. Resulting transformants were designated as pDEST17-pnpA and pDEST17-pnpB and grown in Luria-Bertani broth at 37°C to an optical density (OD600) of ~0.5-0.6 and then induced for 12 hrs by adding L-Arabinose (0.2% w/v) at 25°C for expression of the target proteins.
Preparation of cell extract and protein purification
The cell pellets of induced recombinants were harvested from 250 ml culture by centrifugation, re-suspended into 8 ml of 50 mM potassium phosphate buffer, pH 8.0 containing imidazole (10 mM), NaCl (300 mM) and glycerol (10%) at pH 8.0 and lysed by ultrasonication. Over-expression of cloned genes was determined with SDS-PAGE analysis of lysed samples. Subsequently, cell free lysate with over-expressed PnpA and PnpB from 250 ml cultures were centrifuged at 13,000 x g for 20 min at 4°C to remove membrane fractions. Cell free lysate was further purified with affinity chromatography using 2 ml of Nickel-Nitrilotriacetic Acid (Ni2+ -NTA) Super-flow Cartridge (Qiagen, GmbH, Germany) according to supplier’s instructions. His-tagged PnpA and PnpB were separately allowed to bind to the resin equilibrated with 50 mM potassium phosphate buffer, pH 8.0, imidazole (10 mM), NaCl (300 mM) and glycerol (10%); washed twice with 10-15 ml of wash buffer containing 50 mM potassium phosphate buffer, pH 8.0 imidazole (30 mM), NaCl (300 mM) and glycerol (10%). His-tagged PnpA and PnpB were eluted in the buffer same as the binding buffer except that the final concentration of imidazole was 250 mM. Purified proteins were dialyzed twice in 50 mM potassium phosphate buffer, pH 8.0 containing NaCl (300 mM) and Glycerol (10%) at 4°C for 12-16 hrs. Protein concentrations were determined by Bradford reagent (Sigma, USA) using the standard concentration plot generated with known concentrations of Bovine Serum Albumin. Purification of the target protein was also scrutinized by SDS-PAGE analysis. Size exclusion chromatography of purified PnpA and PnpB was carried out using Shodex KW803 protein column on Agilent-1260 infinity series. Molecular mass and stoichiometry of the purified recombinant proteins was determined using linear standard curve generated with proteins of known molecular masses. Purified proteins were stored in storage buffer containing 50 mM potassium phosphate pH 8.0, NaCl (300 mM), Glycerol (10% v/v) at 4°C or -20°C. Aliquots of purified PnpA and PnpB proteins were frozen rapidly by plunging the sample vial in liquid nitrogen and then stored in -20°C. Later, PnpA and PnpB aliquots were thawed by incubating the sample vial under running tap water.
Enzyme activity of purified PnpA
The catalytic activity of purified PnpA was monitored with spectrophotometric enzyme assay specific for PnpM and performed according to the method described earlier by Spain et al., (1979) . Briefly, the reaction mixtures consisted of 0.2 mM NADH, 0.02 mM flavin adenine dinucleotide (FAD), 10 µg of purified protein (PnpA), 100 µM substrate (PNP) in 50 mM phosphate buffer (pH 7.4) at a final reaction volume of 1.0 ml. The rationale for using a buffer with pH 7.4 for enzyme activity analysis of PnpA is explained later. Reaction was initiated with the addition of PNP at different concentrations ranging from 12.5- 250 µM. Reference cuvette contained all of the above components except the reaction substrate. The molar extinction coefficients of NADH and PNP were found to be maximum at 340 nm and 405 nm respectively. Therefore, positive activity of PnpA was determined by measuring the change (decrease) in spectral absorbance at above wavelengths corresponding to the consumption of NADH and PNP at regular interval. Kinetic properties of PnpA were determined by assays performed at different concentrations of PNP and NADH. Spectrophotometric analyses were performed on UV-visible spectrophotometer UV-1800 (Shimadzu Instrumentation, MD USA). Effects of temperature, pH and inhibitory metal ions on PnpA activity were studied with standard activity assay.
Alternatively, monooxygenase activity of PnpA was also studied with analytical chemistry approach, wherein 100 µg of purified His-6-PnpA was mixed with 100 µM of substrate (PNP) and 300 µM NADH, 50 µM FAD in 20 mM phosphate buffer (pH 7.4) in a total reaction volume of 10 ml and incubated at 25°C. Samples were collected and analysed for the quantitation of transformation of PNP into BQ by HPLC analysis according to the method described earlier by Ghosh et al., (2010) . A brief description of the HPLC method used is described below. A positive PnpM activity was also measured by estimation of concentration of nitrite ion released in the reaction medium as determined by colorimetric methods described earlier [25,32]. Concentration of nitrite ion was estimated with reference of linear calibration curve generated with known concentrations (0.5 to 250 μM) of NaNO2. At least three time points from the linear parts of the nitrite release curves were used for the calculation of specific initial rates.
Substrate specificity of purified PnpA of strain SJ98
In order to evaluate the substrate specificity of PnpA, purified His-6-PnpA was subjected to HPLC analyses for NADH/FAD dependent monooxygenase activity using chemical analogues of PNP (viz., 4-NC, 2C4NP, 4-CP, 3,4-DCP, 4C3NP, 4C2NP, 2,4-DCP and 4-CC) as the reaction substrates. 100 µM of different substrates with 150 µM NADH and 50 µM FAD in 50 mM potassium phosphate buffer, pH 7.4 were incubated in a total reaction volume of 1 ml. Samples were analysed for the transformation of substrates and quantified using HPLC by comparing with known concentrations of authentic standards.
Enzyme activity of purified PnpB
For functional characterization of purified PnpB, spectrophotometric enzyme assay corresponding to BqR activities was performed according to the method described earlier [25,31]. Briefly, the reaction mixture for enzyme activity of His-6-PnpB contained 50 mM phosphate buffer, pH 7.2, 100 µM NADPH, 50 µM FMN and 15 µg of His-6-PnpB. The rationale for using a buffer with pH 7.2 is explained later. Positive BqR activity was determined by monitoring the transformation of BQ (molar extinction coefficient at 238.9 nm is 24,300 cm-1.M-1) to HQ according to the method described earlier [25,31,33]. The reaction was initiated by the addition of BQ to the reaction mixture. Reference cuvette contained each of the reaction components except the purified His-6-PnpB. Spectral analyses were carried out using Shimadzu UV-Visible spectrophotometer Model UV-1800 (Shimadzu Instrumentation, MD USA). Kinetic properties of PnpB were determined with enzyme assays performed at different concentrations of BQ and NAD(P)H. Activity assays were performed in triplicates, and arithmetic means were considered for estimation of the kinetic properties.
HPLC analyses of the samples collected from enzyme activity for PnpA on PNP and its chemical analogues were performed according to the method described earlier . Briefly, samples were analyzed with a Waters 600 model equipped with Waters 996 photodiode array detector and C18 reversed-phase column (5 µm; 4.6 x 250 mm) (Waters Inc. MD, USA) operating at a column temperature of 25°C. Reaction substrate and product were separated with mobile phase consisting of 1% glacial acetic acid in methanol:1% glacial acetic acid in water with a gradient from 35:65 to 68:32 over 10 min at a flow rate of 1 ml.min-1.
Phylogenetic analysis of PnpA and PnpB from different PNP degrading microorganisms
Phylogenetic analysis of PnpA and PnpB was carried out with amino acid sequences of PnpM and BqR previously characterized from different PNP degrading microorganisms. Amino- acid sequences were obtained from NCBI, GenBank database and subjected to multiple and pair-wise alignment using CLUSTALW module on the MEGA version 5 . Phylogenetic and molecular evolutionary analyses were conducted using MEGA version 5. Phylogenetic trees were constructed with ‘Test Neighbor Joining’ approach using bootstrap values of 1000. Additionally, multiple sequence alignment of PnpB from Burkholderia sp. SJ98 (EKS70312.1) was performed with corresponding genes encoding BqR sequenced and reported from Pseudomonas sp. WBC-3 (ABU50909.1), Pseudomonas putida (ACN43576.1), Pseudomonas sp. 1-7 (ADB81393.1) and Pseudomonas sp. NyZ402 (ACZ51379.1) using ClustalX version 2.1 . Further neighbor joining tree of this alignment was generated by using Jalview 2.8 .
Nucleotide sequence accession number
This Whole Genome Shotgun project has been deposited at DDBJ/EMBL/GenBank under the accession AJHK00000000. The version described in this paper is the second version, AJHK02000000.2. Nucleotide sequences for ORFs pnpA and pnpB isolated and characterized from strain SJ98 have been deposited at GenBank under accession numbers BURK_019605 and BURK_019600 respectively.
Results and Discussion
Identification of ORFs pnpA and pnpB
Genetic characterization of BT transforming gene cluster from strain SJ98 showed the presence of genes encoding cognate subunits of Hydroquinone dioxygenase (HqD) and 4-HMSD, BtD and MaR . Noticeably, annotation of BT and HQ transforming gene cluster from strain SJ98 did not show the presence of either PnpM that would catalyze initial removal of nitro group as nitrite and formation of HQ or PNP-hydroxylase that would catalyze transformation of PNP into 4-NC and BT [21,23]. Furthermore, putative gene(s) with the above function could not be identified within a genomic DNA fragment extending ~41 Kb from the BtD gene .
Genome annotation of strain SJ98 showed the presence of an ORF (designated as pnpA) having conserved FAD and NADH binding motif- ‘GXXXLXGDAAH’ (where ‘X’ is any amino acid) as reported earlier  and maximum sequence similarity (78% identity at amino acid level for the ORF product) with PnpM of Pseudomonas sp. WBC-3 (accession no. ABU50908.1). Another ORF (designated as pnpB) has shown maximum sequence similarity (88% identity at amino acid level) with BqR of Pseudomonas sp. WBC-3 (accession no. ABU50909.1). Noticeably, the above ORFs were found to be physically separated from the other lower pathway genes of PNP degradation earlier identified from strain SJ98. Based on the sequence similarities, at this point of the study, we propose that the ORFs pnpA and pnpB could be potentially involved in PNP degradation by strain SJ98. The proposed position for proteins encoded by ORFs pnpA and pnpB on the degradation pathway of PNP is shown in Figure 1.
Comparison of PNP gene cluster of strain SJ98 with those reported from other bacteria
It was observed from the whole genome sequence of strain SJ98 that the gene cluster pnpAB was present on contig 12 whereas gene cluster pnpE1E2FCD which harbored the lower pathway genes of PNP degradation was present on contig 11. Further attempts were made to find out the distance between these gene clusters in SJ98 genome. There are two possibilities for relative positions of contig 11 and 12: if both the contigs are joined back to back in the order of contig no. 11 followed by contig no. 12, then calculated distance between these gene clusters (pnpAB and pnpE1E2FCD) would be >1.6 Mb (Figure 2A), whereas if both the contigs are joined in the reverse order, then the distance between these two cluster would be >0.4 Mb (Figure 2B). Either way, this observation is different from the earlier reports pertaining to the organization of PNP degradation gene clusters from different PNP degrading organisms which showed the occurrence of all of the PNP degradation genes clustered together in only one gene cluster/operon [22,24,25,37] (Figure 2).
(A) schematic representation of distance between Contig 11 (NZ_AJHK02000011.1) and contigs 12 (NZ_AJHK02000012.1) (B) if contigs 12 and then contigs 11 placed in series together then distance between the gene clusters and (C) PNP degradation gene clusters found in the other PNP degrading bacteria Pseudomonas sp. NyZ402 (GU123925.1), Pseudomonas putida DLLE-4 (FJ376608), Pseudomonas sp. 1-7 (FJ821777) and Pseudomonas sp. WBC-3 (EF577044).
Similar genes have been assigned by the same colors.
Complete PNP gene clusters (which include the genes encoding the enzymes PnpM, BqR, HqD, 4-HMSD, BtD and MaR) previously reported from other microorganisms have been found to be present within DNA fragments ranging from ~9 to 15 kb [22,24,25,37]. Interestingly, the physical organization of the lower pathway genes (PNP degradation) in strain SJ98, Nyz402, DLL-E4, 1-7 and WBC3 is almost identical (Figure 2A, 2B and 2C). On the contrary, in strain SJ98, the PNP degradation genes are separated into two non-contiguous gene clusters viz., pnpAB and pnpE1E2FCD that are physically separated from one another (Figure 2).
G+C content analysis of pnpA and pnpB genes found to be almost similar to the G+C content for the whole genome of strain SJ98 suggesting that these genes may not have been inherited by the horizontal gene transfer mechanism. Also at this point of our understanding, it would be premature to predict or comment upon the mechanism for such divergence. However, we propose that it would be very interesting to work out the molecular details of this observation. Similar separation of the metabolic operons has been reported in a number of earlier reports [38–40]. Zaslaver et al., (2006) have reported that the partitioning of given set of genes is not same in every organism . Gene re-arrangement can take place in any organisms due to mutational event such as gene duplication, which forms new operons or genome rearrangement that can split the existing operon or lateral gene transfer from other organisms [38,39]. However, to the best of authors’ knowledge, a similar partitioning of gene clusters has not been reported with regards to the degradation of PNP.
Cloning, expression of ORFs pnpA, pnpB and purification of PnpA and PnpB
ORF pnpA was cloned, expressed and subsequently His-6-PnpA was purified to homogeneity with a yield of ~5 mg of PnpA from 1 liter of culture. In SDS PAGE analysis, purified His-6-PnpA protein (>90%) was found to have an estimated molecular weight of ~46 kDa (Figure 3A). Gel filtration chromatography of functionally active His-6-PnpA indicated it to be a monomer. This observation is in agreement with the earlier report that has shown PnpM to be a monomer .
(A) His-6-PnpA purification by Ni-NTA chromatography, Lane M) Marker, Lane 1) uninduced, 2) induced whole cell lysate, 3) Induced supernatant, 4) pellet, 5) & 6) flow through, 7) wash and lane 8) Elution of His-6-PnpA is showing with a red arrow.(B) His-6-PnpB purification by Ni-NTA chromatography, Lane M) Marker, Lane1) uninduced , 2) induced whole cell lysate, 3) Induced supernatant, 4) pellet, 5) & 6) flow through, 7) wash and lane 8) Elution of His-6-PnpB is showing with a red arrow.
Similarly ORF pnpB was cloned, expressed and His-6-PnpB protein purified with an identical procedure as used for purification of His-6-PnpA protein to obtain a yield of ~12 mg of PnpB protein from 1 liter of culture. In SDS PAGE analysis, purified His-6-PnpB showed a single band of >90% purity at an apparent molecular mass of ~21 kDa (Figure 3B). Gel filtration chromatography of functionally active His-6-PnpB showed it to be a monomer (Figure S1A). The corresponding size exclusion standard curve generated with proteins of known molecular masses is shown in Figure S1B. Characteristically, majority of the earlier reports have shown functional BqR to be a NAD(P)H and FMN dependent dimer(s) and/or tetramers [25,41,42]. Result obtained during the present study with regards to the oligomeric state BqR of strain SJ98 represented one of the very few examples showing occurrence of a functional BqR as a monomeric protein. Lee et al., (2007) reported isolation and characterization of monomeric quinone reductase involved in the degradation of aromatic compound including lignin by white rot fungi viz., Trametes versicolor . Subsequent biochemical characterization clearly established that despite being functional monomer, the BqR from strain SJ98 exhibited somewhat similar biochemical characteristics to those reported with the other BqRs.
Biochemical and kinetic properties of PnpA
In in-vitro activity assays, a cell extract prepared from recombinant E. coli harboring pDEST17-pnpA was found positive for the stoichiometric release of NO2- ion along with concomitant PNP consumption. Transformation of PNP with stoichiometric NO2- ion release was also observed with purified PnpA in the presence of both NADH and NAD(P)H. Effective concentration of NADH required for PnpA was achieved by performing the enzyme activity at different concentrations of NADH (Table 1). In spectrophotometric analyses for monooxygenation, PnpA catalyzed rapid degradation of PNP along with consumption of NADH as indicated by time dependent decrease in the absorbance at 405 nm and 340 nm respectively (Figure 4A). Reference cuvette containing all components of the reaction except purified PnpA did not show any decrease at either 405 nm or 340 nm (Figure 4B). These assays ascertained the identity of PnpA as PnpM. The stoichiometry of PNP consumption in time-course assay was found to be nearly equivalent to the total accumulation of BQ. HPLC analysis of the samples collected from monooxygenation reaction performed with purified PnpA identified BQ as major reaction product by comparison with the authentic standards (Figure 4C). A small amount of HQ was also detected with HPLC analyses (Figure 4C) and this observation could be justified on the basis of abiotic auto-reduction of BQ into HQ in the presence of NADH. Similar non-enzymatic transformation of BQ into HQ has also been reported by Zhang et al., (2009) . Figure 5 shows the time course of PnpA catalyzed transformation of PNP into BQ along with the slight accumulation of hydroquinone in the reaction mixture.
|Enzyme||Substrate||Vmax (µmole.min-1 .nmole-1 of protein)||Km (µM)|
|PnpA||p-nitrophenol||3.133 ±0.0992||35.37 ± 5.950|
|NADH||5.658 ±0.1426||95.99 ± 7.743|
|PnpB||p-benzoquinone||1.717 ±0.0464||14.90 ± 2.275|
|NAD(P)H||2.952 ±0.0897||118.4 ± 10.96|
(A) Spectrophotometric analysis PnpM activity as shown by decrease in spectral absorption at 420 and 340 nm corresponding to depletion of p-nitrophenol (PNP) and NADH in a time dependent manner. (B) Lack of PnpM activity in negative control sample (C) Enzymatic transformation of PNP to BQ was confirmed by HPLC analysis.
The samples were collected at different time points and analyzed for the formation of BQ and HQ by HPLC analysis. Standard deviation values were calculated by taking the mean of triplicate experiments.
Kinetic properties of PnpA were determined from Michaelis-Menten curve obtained from spectrophotometric analysis of monooxygenation reaction at different concentrations of PNP with a fixed concentration of NADH and another one obtained with varying concentrations of NADH and fixed concentration of PNP. The Vmax and Km values of His-6-PnpA for PNP and NADH were calculated and listed in table 1. Difference in the Km values of PnpA with reference to PNP and NADH has also been observed with PnpA of Pseudomonas sp. WBC-3 (Table S3) . The other noticeable observation was that the purified PnpM of strain SJ98 showed significant differences in Km and Vmax values when compared to PnpM of strain WBC-3. Specific activity of PnpM from strain SJ98 is significantly different from those reported for the corresponding purified enzyme from strain WBC-3 (Table S3).
Purified His-6-PnpA showed a broad temperature optima ranging from 15-30°C with maximum activity at 30°C (Figure S2A). PnpA was found to be functional over the pH range of 6.8- 8.0 with its optimum being the maximum at pH 7.4 (Figure S2B). Since it was observed during the initial screening that the pH optimum for PnpA is at 7.4, therefore, all subsequent biochemical assays carried out for determining the kinetic characteristics were conducted using a buffer with pH of 7.4. In the presence of 10% glycerol, purified His-6-PnpA was stable up-to 7 days at both -20°C and 4°C. The monooxygenase activity of His-6-PnpA was completely abolished in the presence of 100 µM of Cu2+, Hg2+, and Mo5+ salts whereas similar concentrations of Fe2+ and Mn2+ salts showed no inhibitory effect.
PnpA was found to catalyze the monooxygenation of different phenolic substrates viz., MNP, ONP, 3M4NP, 4-NC, 2C4NP, 4C3NP, 4C2NP, 2,6DCP, 2,4DNP and 2,5DNP. Of the selected substrates, purified PnpA of strain SJ98 showed the strongest activity with 2C4NP, 4-NC, 2,4-DNP and 3M4NP whereas relatively weaker activity was observed with 2,6-DNP, ONP and PCP (Table 2). A few earlier reports have also suggested for relaxed monooxygenation activity, which resulted in the removal of substituent groups and formation of corresponding quinones from nitro/chloro substituted phenolic compounds in a broad substrate specific manner [25,44].
|Substrate||Relative activity (%)|
|p-Nitrophenol||100 ± 3|
|o-Nitrophenol||15 ± 2|
|3-Methyl 4-nitrophenol||66 ± 3|
|4-Nitrocatechol||41 ± 2|
|2-Chloro 4-nitrophenol||25 ± 4|
|2,6-Dichlorophenol||18 ± 2|
|2,6-Dinitrophenol||15 ± 4|
|2-Amino 4-nitrophenol||38 ± 3|
|Pentachlorophenol||12 ± 4|
Biochemical and kinetic properties of purified PnpB
The positive BqR activity of purified PnpB was monitored by analyzing the formation of HQ (increased absorbance at 281 nm) and concurrent depletion of BQ (decreased absorbance at 241 nm) in time dependent wavelength scan mode during spectrophotometric analysis (Figure 6A). Similar transformation was not observed in the control reaction mixture lacking His-6-PnpB (Figure 6B). Kinetic properties of PnpB were determined with Michaelis- Menten curves generated with varying concentrations of BQ and NAD(P)H. The Vmax and Km of PnpB for BQ and NAD(P)H were calculated and listed in the table 1. It is noticeable that PnpB of strain SJ98 is a single component monomeric protein, whereas the other characterized benzoquinone reductase from strain WBC-3 (as heterologously expressed and purified recombinant protein) is known to exist as dimeric proteins in the functional state [25,41]. At this point, it would be premature and inconclusive to suggest that the difference in the state of oligomerization would also entail to variation in the activity and chemistry of this protein (PnpB). However, it is noteworthy that the difference in the oligomeric state of this protein shows the difference in the kinetic properties of PnpB from strain SJ98 compared to those reported with a dimeric PnpB characterized from Pseudomonas sp. WBC-3 . Dendrogram obtained on the basis of multiple sequence alignment of amino-acid sequence of PnpB from strain SJ98 compared to the amino acid sequences of BqR reported from other bacterial strains suggested that PnpB of strain SJ98 constitutes an entirely different clade (Figure S3A & S3B). Further studies of determining the structure-function relation of PnpB would be required to elaborate on its functional evolution.
Purified His-6-PnpB also showed broad temperature optima ranging from 20 to 40°C (Figure S4A). However, it is active over a relatively narrow range of pH (7.0 to 7.8) with an optimum pH 7.2 (Figure S4B). Therefore, further biochemical characterization of purified PnpB was carried out using a buffer of pH of 7.2. To conclude, the results obtained from the biochemical characterization of the purified PnpA and PnpB ascertained their identity as PnpM and BqR.
Phylogenetic analysis of PnpA and PnpB
Phylogenetic analysis of PnpA and PnpB of strain SJ98 further substantiated the observation for the presence of pnpAB as physically separated gene cluster. In Neighbor Joining phylogenetic tree, PnpA and PnpB from strain SJ98 displayed separate clade from the other PnpMs and BqRs respectively. As shown in Figure 7A, PnpM from strain SJ98 and Pseudomonas sp. 1-7 are very different from the PnpMs of other bacterial strains (Figure 7A). Furthermore, PnpB from strain SJ98 also appeared in a different clade (Figure 7B).
Neighbor joining method was applied at the bootstrap value of 1000. Accession number of the proteins is written in parentheses.
During the recent past, a number of studies have shown identification and characterization of PNP degradation gene clusters from different PNP degrading microorganisms. Identification and characterization of previously unknown gene clusters have helped significantly with the advancements in the field of genome sequencing and annotation. Several studies have reported identification of previously unknown degradation reactions and/or in identification of molecular components (genes, gene clusters) with the important role in previously characterized degradative potentials [45,46]. Furthermore, comparative genomic studies of degradative microorganisms may also help in developing a better understanding about their evolutionary relationships and optimization of bioremediation processes. Significance of the genomic studies is further highlighted in the case of organisms for which genetic tools, e.g. ‘selective gene knockouts’ and ‘complementation studies’ are relatively less well established. Present study conclusively demonstrates the identification of important genes involved in PNP degradation by Burkholderia sp. strain SJ98 that had remained elusive with conventional microbial genetic approaches.
In the present study, we have identified and characterized two ORFs pnpA and pnpB from the genome sequence of strain SJ98. His-6-PnpA transforms PNP to BQ and has broad substrate specificity while His-6-PnpB transforms BQ to HQ. These genes are physically separated from the other genes (lower pathway genes) involved in the degradation of PNP by strain SJ98. Thus we conclude that genes involved in the degradation of the PNP by strain SJ98 are present in the form of two separate/non-contiguous clusters. This is the first report for identification of such arrangement of PNP degradation gene cluster. We propose that this study would provide valuable insights about underlying molecular mechanism of microbial degradation of PNP and that the strain SJ98 could be used as an important model system for the microbial degradation of PNP.
Determination of molecular weight of PnpB (A) Size exclusion chromatography profile of purified functional His-6-PnpB (Rt 11.22 min corresponding to MW ~ 21 kDa). (B) Linear standard curve for the known molecular weight proteins i.e., Feritine (450 kDa), 8.6033 min; Conalbumine, (76.6 kDa) 9.9284 min; Ovalbumine (45 kDa), 10.2454 min; Chymotrypsinogen (25 kDa), 11.1305 min; Ribonuclease A (13.7 kDa) 11.3263 min; Insuline (5.8 kDa) 11.6974 min.
Relative percent activity of PnpA at different (A) Temperatures and (B) different pH.
Multiple sequence alignment (MSA) of (A) PnpB and (B) Dendrogram on the basis of MSA, from Burkholderia sp. SJ98 (EKS70312.1), Pseudomonas sp. WBC-3 (ABU50909.1), Pseudomonas putida (ACN43576.1), Pseudomonas sp. 1-7 (ADB81393.1) and Pseudomonas sp. NyZ402 (ACZ51379.1).
Relative percent activity of PnpB at different (A) Temperatures and (B) different pH.
Bacterial strains and plasmids used in this study.
List of primers used in this study.
Comparison of kinetic properties of p-nitrophenol 4-monooxygenase from strain SJ98 with strain WBC-3.
We are thankful to Late Dr. R.K. Jain for initiating this project, who conceived this project. Authors are thankful to Ms. Bhawana Pant and Mr. Anil Gupta for their excellent technical help during this work. Authors acknowledge Dr. Ankur Gautam for proofreading of the manuscript. SV and SK duly acknowledge research fellowship awarded by CSIR, India. This is the IMTECH communication number 1/2013.
Performed the experiments: SV SK. Analyzed the data: SV JP SK GPSR. Contributed reagents/materials/analysis tools: GPSR. Wrote the manuscript: SV JP SK GPSR.
- 1. Wissiack R, Rosenberg E (2002) Universal screening method for the determination of US Environmental Protection Agency phenols at the lower ng l(-1) level in water samples by on-line solid-phase extraction-high-performance liquid chromatography-atmospheric pressure chemical ionization mass spectrometry within a single run. J Chromatogr A 963: 149-157. doi:10.1016/S0021-9673(02)00546-0. PubMed: 12187965.
- 2. Rubin C, Esteban E, Hill RH Jr, Pearce K (2002) Introduction--the methyl parathion story: a chronicle of misuse and preventable human exposure. Environ Health Perspect 110 (Suppl 6): 1037-1040. doi:10.1289/ehp.02110s61037. PubMed: 12634136.
- 3. Imtiaz R, Haugh G (2002) Analysis of environmental and biologic methyl parathion data to improve future data collection. Environ Health Perspect 110 (Suppl 6): 1071-1074. doi:10.1289/ehp.02110s61071. PubMed: 12634142.
- 4. Munnecke DM, Hsieh DP (1976) Pathways of microbial metabolism of parathion. Appl Environ Microbiol 31: 63-69. PubMed: 8005.
- 5. Smith LW, Hall GT, Kennedy GL (1988) Acute and repeated dose inhalation toxicity of para-nitrophenol sodium salt in rats. Drug Chem Toxicol 11: 319-327. doi:10.3109/01480548809017886. PubMed: 3181044.
- 6. Esteban E, Rubin C, Hill R, Olson D, Pearce K (1996) Association between indoor residential contamination with methyl parathion and urinary para-nitrophenol. J Expo Anal Environ Epidemiol 6: 375-387. PubMed: 8889955.
- 7. Guizzetti M, Pathak S, Giordano G, Costa LG (2005) Effect of organophosphorus insecticides and their metabolites on astroglial cell proliferation. Toxicology 215: 182-190. doi:10.1016/j.tox.2005.07.004. PubMed: 16102884.
- 8. Bhushan B, Chauhan A, Samanta SK, Jain RK (2000) Kinetics of biodegradation of p-nitrophenol by different bacteria. Biochem Biophys Res Commun 274: 626-630. doi:10.1006/bbrc.2000.3193. PubMed: 10924328.
- 9. Sahoo NK, Pakshirajan K, Ghosh PK (2011) Batch biodegradation of para-nitrophenol using Arthrobacter chlorophenolicus A6. Appl Biochem Biotechnol 165: 1587-1596. doi:10.1007/s12010-011-9379-8. PubMed: 21927857.
- 10. Nielsen MB, Ingvorsen K (2013) Biodegradation of para-nitrophenol by Citricoccus nitrophenolicus strain PNP1T at high pH. Biodegradation 24: 79-87. doi:10.1007/s10532-012-9559-4. PubMed: 22678128.
- 11. Yi S, Zhuang WQ, Wu B, Tay ST, Tay JH (2006) Biodegradation of p-nitrophenol by aerobic granules in a sequencing batch reactor. Environ Sci Technol 40: 2396-2401. doi:10.1021/es0517771. PubMed: 16646480.
- 12. Zhang J, Sun Z, Li Y, Peng X, Li W et al. (2009) Biodegradation of p-nitrophenol by Rhodococcus sp. CN6 with high cell surface hydrophobicity. J Hazard Mater 163: 723-728. doi:10.1016/j.jhazmat.2008.07.018. PubMed: 18718714.
- 13. Jain RK, Dreisbach JH, Spain JC (1994) Biodegradation of p-nitrophenol via 1,2,4-benzenetriol by an Arthrobacter sp. Appl Environ Microbiol 60: 3030-3032. PubMed: 8085840.
- 14. Nielsen MB, Kjeldsen KU, Ingvorsen K (2011) Description of Citricoccus nitrophenolicus sp. nov., a para-nitrophenol degrading actinobacterium isolated from a wastewater treatment plant and emended description of the genus Citricoccus Altenburger et al. 2002. Antonie Van Leeuwenhoek 99: 489-499.
- 15. Chauhan A, Chakraborti AK, Jain RK (2000) Plasmid-encoded degradation of p-nitrophenol and 4-nitrocatechol by Arthrobacter protophormiae. Biochem Biophys Res Commun 270: 733-740. doi:10.1006/bbrc.2000.2500. PubMed: 10772893.
- 16. Kadiyala V, Spain JC (1998) A two-component monooxygenase catalyzes both the hydroxylation of p-nitrophenol and the oxidative release of nitrite from 4-nitrocatechol in Bacillus sphaericus JS905. Appl Environ Microbiol 64: 2479-2484. PubMed: 9647818.
- 17. Spain JC, Gibson DT (1991) Pathway for Biodegradation of p-Nitrophenol in a Moraxella sp. Appl Environ Microbiol 57: 812-819. PubMed: 16348446.
- 18. Takeo M, Murakami M, Niihara S, Yamamoto K, Nishimura M et al. (2008) Mechanism of 4-nitrophenol oxidation in Rhodococcus sp. Strain PN1: characterization of the two-component 4-nitrophenol hydroxylase and regulation of its expression. J Bacteriol 190: 7367-7374. doi:10.1128/JB.00742-08. PubMed: 18805976.
- 19. Takeo M, Yasukawa T, Abe Y, Niihara S, Maeda Y et al. (2003) Cloning and characterization of a 4-nitrophenol hydroxylase gene cluster from Rhodococcus sp. PN1. J Biosci Bioeng 95: 139-145. doi:10.1016/S1389-1723(03)80119-6. PubMed: 16233382.
- 20. Perry LL, Zylstra GJ (2007) Cloning of a gene cluster involved in the catabolism of p-nitrophenol by Arthrobacter sp. strain JS443 and characterization of the p-nitrophenol monooxygenase. J Bacteriol 189: 7563-7572. doi:10.1128/JB.01849-06. PubMed: 17720792.
- 21. Chauhan A, Pandey G, Sharma NK, Paul D, Pandey J et al. (2010) p-Nitrophenol degradation via 4-nitrocatechol in Burkholderia sp. SJ98 and cloning of some of the lower pathway genes. Environ Sci Technol 44: 3435-3441. doi:10.1021/es9024172. PubMed: 20359211.
- 22. Zhang S, Sun W, Xu L, Zheng X, Chu X et al. (2012) Identification of the para-nitrophenol catabolic pathway, and characterization of three enzymes involved in the hydroquinone pathway, in Peudomonas sp. 1-7. BMC Microbiol 12: 27. doi:10.1186/1471-2180-12-27. PubMed: 22380602.
- 23. Vikram S, Pandey J, Bhalla N, Pandey G, Ghosh A et al. (2012) Branching of the p-nitrophenol (PNP) degradation pathway in Burkholderia sp. Strain SJ98: Evidences from genetic characterization of PNP gene cluster. AMB Express 2: 30. doi:10.1186/2191-0855-2-30. PubMed: 22681853.
- 24. Shen W, Liu W, Zhang J, Tao J, Deng H et al. (2010) Cloning and characterization of a gene cluster involved in the catabolism of p-nitrophenol from Pseudomonas putida DLL-E4. Bioresour Technol 101: 7516-7522. doi:10.1016/j.biortech.2010.04.052. PubMed: 20466541.
- 25. Zhang JJ, Liu H, Xiao Y, Zhang XE, Zhou NY (2009) Identification and characterization of catabolic para-nitrophenol 4-monooxygenase and para-benzoquinone reductase from Pseudomonas sp. strain WBC-3. J Bacteriol 191: 2703-2710. doi:10.1128/JB.01566-08. PubMed: 19218392.
- 26. Yamamoto K, Nishimura M, Kato D, Takeo M, Negoro S (2011) Identification and characterization of another 4-nitrophenol degradation gene cluster, nps, in Rhodococcus sp. strain PN1. J Biosci Bioeng 111: 687-694. doi:10.1016/j.jbiosc.2011.01.016. PubMed: 21396889.
- 27. Kumar S, Vikram S, Raghava GP (2013) Genome annotation of Burkholderia sp. SJ98 with special focus on chemotaxis genes. PLOS ONE 8: e70624. doi:10.1371/journal.pone.0070624. PubMed: 23940608.
- 28. Pandey J, Heipieper HJ, Chauhan A, Arora PK, Prakash D et al. (2011) Reductive dehalogenation mediated initiation of aerobic degradation of 2-chloro-4-nitrophenol (2C4NP) by Burkholderia sp. strain SJ98. Appl Microbiol Biotechnol 92: 597-607. doi:10.1007/s00253-011-3254-y. PubMed: 21626025.
- 29. Lagesen K, Hallin P, Rødland EA, Staerfeldt HH, Rognes T et al. (2007) RNAmmer: consistent and rapid annotation of ribosomal RNA genes. Nucleic Acids Res 35: 3100-3108. doi:10.1093/nar/gkm160. PubMed: 17452365.
- 30. Altschul SF, Gish W, Miller W, Myers EW, Lipman DJ (1990) Basic local alignment search tool. J Mol Biol 215: 403-410. doi:10.1016/S0022-2836(05)80360-2. PubMed: 2231712.
- 31. Spain JC, Wyss O, Gibson DT (1979) Enzymatic oxidation of p-nitrophenol. Biochem Biophys Res Commun 88: 634-641. doi:10.1016/0006-291X(79)92095-3. PubMed: 37837.
- 32. Ghosh A, Khurana M, Chauhan A, Takeo M, Chakraborti AK et al. (2010) Degradation of 4-nitrophenol, 2-chloro-4-nitrophenol, and 2,4-dinitrophenol by Rhodococcus imtechensis strain RKJ300. Environ Sci Technol 44: 1069-1077. doi:10.1021/es9034123. PubMed: 20050667.
- 33. Braude EA (1945) Studies in light absorption. Part I. p-Benzoquinones. J Chem Soc: 490-497.
- 34. Tamura K, Peterson D, Peterson N, Stecher G, Nei M et al. (2011) MEGA5: Molecular Evolutionary Genetics Analysis using Maximum Likelihood, Evolutionary Distance, and Maximum Parsimony Methods. Mol Biol Evol 28: 2731–2739. doi:10.1093/molbev/msr121. PubMed: 21546353.
- 35. Larkin MA, Blackshields G, Brown NP, Chenna R, McGettigan PA et al. (2007) Clustal W and Clustal X version 2.0. Bioinformatics 23: 2947–2948. doi:10.1093/bioinformatics/btm404. PubMed: 17846036.
- 36. Waterhouse AM, Procter JB, Martin DM, Clamp M, Barton GJ (2009) Jalview Version 2--a multiple sequence alignment editor and analysis workbench. Bioinformatics 25 (9):1189-1191. doi:10.1093/bioinformatics/btp033.
- 37. Wei Q, Liu H, Zhang JJ, Wang SH, Xiao Y et al. (2010) Characterization of a para-nitrophenol catabolic cluster in Pseudomonas sp. strain NyZ402 and construction of an engineered strain capable of simultaneously mineralizing both para- and ortho-nitrophenols. Biodegradation 21: 575-584. doi:10.1007/s10532-009-9325-4. PubMed: 20049512.
- 38. Zaslaver A, Mayo A, Ronen M, Alon U (2006) Optimal gene partition into operons correlates with gene functional order. Phys Biol 3: 183-189. doi:10.1088/1478-3975/3/3/003. PubMed: 17021382.
- 39. Omelchenko MV, Makarova KS, Wolf YI, Rogozin IB, Koonin EV (2003) Evolution of mosaic operons by horizontal gene transfer and gene displacement in situ. Genome Biol 4: R55. doi:10.1186/gb-2003-4-9-r55. PubMed: 12952534.
- 40. Riveros-Rosas H, Julian-Sanchez A, Villalobos-Molina R, Pardo JP, Pina E (2003) Diversity, taxonomy and evolution of medium-chain dehydrogenase/reductase superfamily. European journal of biochemistry / FEBS 270 (16): 3309-3334.
- 41. Brock BJ, Rieble S, Gold MH (1995) Purification and Characterization of a 1,4-Benzoquinone Reductase from the Basidiomycete Phanerochaete chrysosporium. Appl Environ Microbiol 61: 3076-3081. PubMed: 16535104.
- 42. Binter A, Staunig N, Jelesarov I, Lohner K, Palfey BA et al. (2009) A single intersubunit salt bridge affects oligomerization and catalytic activity in a bacterial quinone reductase. FEBS J 276: 5263-5274. doi:10.1111/j.1742-4658.2009.07222.x. PubMed: 19682074.
- 43. Lee SS, Moon DS, Choi HT, Song HG (2007) Purification and characterization of an intracellular NADH: quinone reductase from Trametes versicolor. J Microbiol 45: 333-338. PubMed: 17846587.
- 44. Haigler BE, Nishino SF, Spain JC (1994) Biodegradation of 4-methyl-5-nitrocatechol by Pseudomonas sp. strain DNT. J Bacteriol 176: 3433-3437. PubMed: 8195105.
- 45. Parales RE, Haddock JD (2004) Biocatalytic degradation of pollutants. Curr Opin Biotechnol 15: 374-379. doi:10.1016/j.copbio.2004.06.003. PubMed: 15296933.
- 46. Lovley DR (2003) Cleaning up with genomics: applying molecular biology to bioremediation. Nat Rev Microbiol 1: 35-44. doi:10.1038/nrmicro731. PubMed: 15040178.