Opacus 1CP Research Articles

Removal of Phenol by Rhodococcus opacus 1CP after Dormancy: Insight into Enzymes' Induction, Specificity, and Cells Viability.

Biodegradation of phenol is an effective method for removing this toxicant from contaminated sites. Phenol is a toxic compound for living cells, so many bacteria degrade phenol in relatively low concentrations, up to 0.75 g L-1. The Rhodococcus opacus strain 1CP is an effective destructor of a wide range of pollutants. In the absence of a carbon source in the medium, cells of the R. opacus 1CP strain easily form cyst-like resting cells (CLC). The purpose of this work was to evaluate the viability of cells during long-term storage and the efficiency of the process of phenol destruction by R. opacus 1CP cells germinating after dormancy. Resting cells were obtained by simple cultivation in a rich medium followed by storage under static conditions. This is a simple approach to obtain a large amount of biomass. Decomposition of phenol proceeded via catechol followed by ortho-cleavage of aromatic ring. The induction of three phenol hydroxylases was detected by RT-PCR in cells germinated in a mineral medium with phenol as the carbon source. The stability of the genome of cells germinating after dormancy is shown by box-PCR. Dormant R. opacus 1CP cells, both suspended and immobilized, can be directly used for the decomposition of phenol after 4-12 months storage. In addition to phenol, after 9 months of storage, immobilized germinating cells easily metabolized 4-chlorophenol and 2,4,6-trichlorophenol. The results demonstrate a potential and simple approach toward achieving long-term storage of cells for further use in bioremediation.

The Contribution of Actinobacteria to the Degradation of Chlorinated Compounds: Variations in the Activity of Key Degradation Enzymes

Bacteria make a huge contribution to the purification of the environment from toxic stable pollutants of anthropogenic and natural origin due to the diversity of their enzyme systems. For example, the ability to decompose 3-chlorobenzoate (3CBA) by the four representative genera of Actinobacteria, such as Rhodococcus, Gordonia, Microbacterium, and Arthrobacter, was studied. In most cases, the formation of 4-chlorocatechol as the only key intermediate during the decomposition of 3CBA was observed. However, Rhodococcus opacus strain 1CP was an exception, whose cells decomposed 3CBA via both 3-chloro- and 4-chlorocatechol. The enzyme 3-Chlorobenzoate 1,2-dioxygenase (3CBDO) induced during the growth of these bacteria in the presence of 3CBA differed significantly in substrate specificity from the benzoate dioxygenases induced upon growth in the presence of benzoate. The R. opacus 6a strain was found to contain genes encoding chlorocatechol 1,2-dioxygenase, chloromuconate cycloisomerase, and dienelactone hydrolase, whose nucleotide sequence was 100% consistent with the sequences of the corresponding genes encoding the enzymes of the modified 4-chlorocatechol ortho-cleavage pathway of the strain R. opacus 1CP. However, the gene encoding chloromuconolactone dehalogenase (clcF) was not found in the representatives of the actinomycete genera, including Gordonia and Arthrobacter. A linear mega-plasmid carrying 3-chlorocatechol degradation genes remained stable after maintaining the R. opacus 1CP strain on an agar-rich medium for 25 years. In general, a similar plasmid was absent in actinobacteria of other genera, as well as in closely related species of R. opacus 6a.

Specificity of Rhodococcus opacus 1CP cells' responses to benzoate and 3-chlorobenzoate.

Halogenated aromatic compounds are more resistant to microbial degradation than non-halogenated aromatic compounds. Microbial degradation of sodium benzoate in the presence of sodium 3-chlorobenzoate is of interest. The ability to degrade aromatic compounds is largely determined by the substrate specificity of the first enzyme that initiates degradation, namely, benzoate 1,2-dioxygenase for benzoate degradation, and 3-chlorobenzoate 1,2-dioxygenase for 3-chlorobenzoate degradation. In this study, the perspective of immobilized cells of Rhodococcus opacus 1CP actinobacterium for degradation of benzoate and 3-chlorobenzoate was explored. The biosensor approach (a membrane microbial sensor based on immobilized cells of Rhodococcus opacus 1CP and the Clark-type oxygen electrode as a transducer) was applied to evaluate the actinobacterial cells' responses to benzoate and 3-chlorobenzoate in the absence of both enzymes, benzoate 1,2-dioxygenase and 3-chlorobenzoate 1,2-dioxygenase, or in the presence of one of the said enzymes. Data obtained show that 1CP actinobacterium possessed a constitutive system for the transport of benzoate and 3-chlorobenzoate into culture cells. The affinity of the transport system for benzoate was higher than that for 3-chlorobenzoate. Moreover, adaptation to one substrate did not preclude the use of the second substrate. Probably, porins facilitated the penetration of benzoate and 3-chlorobenzoate into 1CP cells. Analyzing V vs. S dependencies, negative cooperativity was found, when benzoate 1,2-dioxygenase bound substrate (3-chlorobenzoate), while positive cooperativity was determined at benzoate binding. The observed difference could be associated with the presence of at least two systems of 3-chlorobenzoate transport into actinobacterial cells and allosteric interaction of active sites of benzoate 1,2-dioxygenase in the presence of 3-chlorobenzoate. The membrane microbial sensor based on immobilized Rhodococcus opacus 1CP cells could be useful as a perspective tool for comparative evaluation of enzymes of complex structure such as benzoate- and 3-chlorobenzoate 1,2-dioxygenase.

Identification of molecular basis that underlie enzymatic specificity of AzoRo from Rhodococcus opacus 1CP: A potential NADH:quinone oxidoreductase

Azo dyes are important to various industries such as textile industries. However, these dyes are known to comprise toxic, mutagenic, and carcinogenic representatives. Several approaches have already been employed to mitigate the problem such as the use of enzymes. Azoreductases have been well-studied in its capability to reduce azo dyes. AzoRo from Rhodococcus opacus 1CP has been found to be accepting only methyl red as a substrate, surmising that the enzyme may have a narrow active site. To determine the active site configuration of AzoRo at atomic level and identify the key residues involved in substrate binding and enzyme specificity, we have determined the crystal structure of holo-AzoRo and employed a rational design approach to generate AzoRo variants. The results reported here show that AzoRo has a different configuration of the active site when compared with other bacterial NAD(P)H azoreductases, having other key residues playing a role in the substrate binding and restricting the enzyme activity towards different azo dyes. Moreover, it was observed that AzoRo has only about 50% coupling yield to methyl red and p-benzoquinone – giving rise to the possibility that NADH oxidation still occurs even during catalysis. Results also showed that AzoRo is more active and more efficient towards quinones (about four times higher than methyl red).

Characterization of Two Hydrogen Peroxide Resistant Peroxidases from Rhodococcus opacus 1CP

The dye-decolorizing peroxidases (DyP) are a family of heme-dependent enzymes present on a broad spectrum of microorganisms. While the natural function of these enzymes is not fully understood, their capacity to degrade highly contaminant pigments such as azo dyes or anthraquinones make them excellent candidates for applications in bioremediation and organic synthesis. In this work, two novel DyP peroxidases from the organism Rhodococcus opacus 1CP (DypA and DypB) were cloned and expressed in Escherichia coli. The enzymes were purified and biochemically characterized. The activities of the two DyPs via 2,2′-azino-bis [3-ethylbenzthiazoline-6-sulphonic acid] (ABTS) assay and against Reactive Blue 5 were assessed and optimized. Results showed varying trends for DypA and DypB. Remarkably, these enzymes presented a particularly high tolerance towards H2O2, retaining its activities at about 10 mM H2O2 for DypA and about 4.9 mM H2O2 for DypB.

Gentisate 1,2-dioxygenase from the gram-positive bacteria Rhodococcus opacus 1CP: Identical active sites vs. different substrate selectivities

Gentisate 1,2-dioxygenases belong to the class III ring-cleaving dioxygenases catalyzing key reactions of aromatic compounds degradation by aerobic microorganisms. In the present work, the results of complete molecular, structural, and functional investigations of the gentisate 1,2-dioxygenase (rho-GDO) from a gram-positive bacterium Rhodococcus opacus 1CP growing on 3-hydroxybenzoate as a sole source of carbon and energy are presented. The purified enzyme showed a narrow substrate specificity. Among fourteen investigated substrate analogues only gentisate was oxidized by the enzyme, what can be potentially applied in biosensor technologies. The rho-GDO encoding gene was identified in the genomic DNA of the R. opacus 1CP. According to phylogenetic analysis, the rho-GDO belongs to the group of apparently most recently acquired activities in bacterial genera Rhodococcus, Arthrobacter, Corynebacterium, Nocardia, Amycolatopsis, Comamonas, and Streptomyces. Homology modeling the rho-GDO 3D-structure demonstrates the composition identity of the first-sphere residues of the active site of rho-GDO and salicylate 1,2-dioxygenase from Pseudaminobacter salicylatoxidans (RCSB PDB: 2PHD), despite of their different substrate specificities. The phenomenon described for the first time for this family of enzymes supposes a more complicated mechanism of substrate specificity than previously imagined, and makes the rho-GDO a convenient model for a novel direction of structure-function relationship studies.

Evaluation of phenol-degradation activity of Rhodococcus opacus 1CP using immobilized and intact cells

Phenol is among the most distributed pollutants; phenol biodegradation is one of the most efficient and cost-effective pollutants degradation technologies. To estimate phenol-degradation activity of actinobacterium Rhodococcus opacus 1CP, the pollutant-degrading microorganism, evaluation of the activity of phenol hydroxylase and other systems for phenol degradation was performed in this study. For the first time, phenol hydroxylase activity and activity of phenol transporting cellular systems of R. opacus 1CP cells were assessed using biosensor technique based on the immobilized cells of the culture of interest. For phenol-induced cells and cells grown in the enriched medium, the responses to a substrate were compared. Two non-specific systems of phenol transport into 1CP cells were detected. These systems differed in the degree of affinity for phenol. It was shown for phenol-induced 1CP cells that phenol was transported into the cell by simple diffusion at phenol concentrations above 0.1 µM. For R. opacus 1CP phenol hydroxylase, Km app, obtained with immobilized cells, was not greater than 1 µM. For the first time, immobilized cells-based technique (estimation of the responses to a substrate using immobilized and intact cells) was applied to predict the presence of at least two isozymes of phenol hydroxylases, which play metabolic and regulatory roles, and of a few differentially regulated catechol 1,2-dioxygenases in cells of this culture. This study confirmed that biosensor technique is simple, rapid and useful method for investigation of substrate metabolism.

Two Homologous Enzymes of the GalU Family in Rhodococcus opacus 1CP-RoGalU1 and RoGalU2.

Uridine-5’-diphosphate (UDP)-glucose is reported as one of the most versatile building blocks within the metabolism of pro- and eukaryotes. The activated sugar moiety is formed by the enzyme UDP-glucose pyrophosphorylase (GalU). Two homologous enzymes (designated as RoGalU1 and RoGalU2) are encoded by most Rhodococcus strains, known for their capability to degrade numerous compounds, but also to synthesize natural products such as trehalose comprising biosurfactants. To evaluate their functionality respective genes of a trehalose biosurfactant producing model organism—Rhodococcus opacus 1CP—were cloned and expressed, proteins produced (yield up to 47 mg per L broth) and initially biochemically characterized. In the case of RoGalU2, the Vmax was determined to be 177 U mg−1 (uridine-5’-triphosphate (UTP)) and Km to be 0.51 mM (UTP), respectively. Like other GalUs this enzyme seems to be rather specific for the substrates UTP and glucose 1-phosphate, as it accepts only dTTP and galactose 1-phoshate in addition, but both with solely 2% residual activity. In comparison to other bacterial GalU enzymes the RoGalU2 was found to be somewhat higher in activity (factor 1.8) even at elevated temperatures. However, RoGalU1 was not obtained in an active form thus it remains enigmatic if this enzyme participates in metabolism.

Evaluation of 3-Chlorobenzoate 1,2-Dioxygenase Inhibition by 2- and 4-Chlorobenzoate with a Cell-Based Technique.

The electrochemical reactor microbial sensor with the Clark oxygen electrode as the transducer was used for investigation of the competition between 3-chlorobenzoate (3-CBA) and its analogues, 2- and 4-chlorobenzoate (2-CBA and 4-CBA), for 3-chlorobenzoate-1,2-dioxygenase (3-CBDO) of Rhodococcus opacus 1CP cells. The change in respiration of freshly harvested R. opacus 1CP cells in response to 3-CBA served as an indicator of 3-CBDO activity. The results obtained confirmed inducibility of 3-CBDO. Sigmoidal dependency of the rate of the enzymatic reaction on the concentration of 3-CBA was obtained and positive kinetic cooperativity by a substrate was shown for 3-CBDO. The Hill concentration constant, S0.5, and the constant of catalytic activity, Vmax, were determined. Inhibition of the rate of enzymatic reaction by excess substrate, 3-CBA, was observed. Associative (competitive inhibition according to classic classification) and transient types of the 3-CBA-1,2-DO inhibition by 2-CBA and 4-CBA, respectively, were found. The kinetic parameters such as S0.5i and Vmaxi were also estimated for 2-CBA and 4-CBA. The disappearance of the S-shape of the curve of the V versus S dependence for 3-CBDO in the presence of 4-CBA was assumed to imply that 4-chlorobenzoate had no capability to be catalytically transformed by 3-chlorobenzoate-1,2-dioxygenase of Rhodococcus opacus 1CP cells.

Pathways of 3-Chlorobenzoate Degradation by Rhodococcus opacus strains 1CP and 6a

3-Chlorobenzoic acid (3-CBA) is widely used as a precursor/preservative in industry and agriculture and is therefore a known environmental contaminant. The key stages of 3-CBA decomposition by Rhodococcus opacus strains 1CP and 6a were studied. Comparative characterization of the substrate specificity of 3-chlorobenzoate 1,2-dioxygenase (3-CBA 1,2-DO), induced in the strains grown in the presence of 3‑CBA, was carried out. These enzymes were established to have a wider substrate specificity than the benzoate 1,2-dioxygenase (1,2-BDO) of R. opacus strain 1CP, which is induced during growth of R. opacus strain 1CP in the presence of benzoate. Benzoate, 3-CBA, and 3,4-dihydroxybenzoate served as substrates for 3‑CBA 1,2-DO. During the degradation of 3-CBA by R. opacus 1CP cells, both 3-chloro- and 4-chlorocatechol (3-CCat and 4-CCat) were detected. R. opacus 6a efficiently degraded 3-CBA without accumulation of intermediates. The difference in the pathways of 3-CBA degradation by these strains was shown: via the pathway of ortho-cleavage of 3-chlorocatechol in R. opacus 1CP and of 4-chlorocatechol in R. opacus 6a. In the genome of the strain R. opacus 6a, the genes encoding chlorocatechol 1,2-dioxygenase and chloromuconate cycloisomerase were found, which were 98-99% identical to the genes of R. opacus 1CP encoding 4‑chlorocatechol 1,2-dioxygenase (4-CCat 1,2-DO) and 3-chloromuconate cycloisomerase (3-CMCI) of the modified ortho-cleavage pathway for conversion of 4-chlorocatechol (the intermediate of 4-chlorophenol degradation). It was shown for the strains under study that implementation of different pathways for 3-CBA decomposition was predestined not by the metabolic capabilities of bacteria, but by the substrate specificity of 3-CBA 1,2-DO, the enzyme that initiates 3-CBA degradation.

Catalytic Performance of a Class III Old Yellow Enzyme and Its Cysteine Variants.

Class III old yellow enzymes (OYEs) contain a conserved cysteine in their active sites. To address the role of this cysteine in OYE-mediated asymmetric synthesis, we have studied the biocatalytic properties of OYERo2a from Rhodococcus opacus 1CP (WT) as well as its engineered variants C25A, C25S and C25G. OYERo2a in its redox resting state (oxidized form) is irreversibly inactivated by N-methylmaleimide. As anticipated, inactivation does not occur with the Cys variants. Steady-state kinetics with this maleimide substrate revealed that C25S and C25G doubled the turnover frequency (kcat) while showing increased KM values compared to WT, and that C25A performed more similar to WT. Applying the substrate 2-cyclohexen-1-one, the Cys variants were less active and less efficient than WT. OYERo2a and its Cys variants showed different activities with NADPH, the natural reductant. The variants did bind NADPH less well but kcat was significantly increased. The most efficient variant was C25G. Replacement of NADPH with the cost-effective synthetic cofactor 1-benzyl-1,4-dihydronicotinamide (BNAH) drastically changed the catalytic behavior. Again C25G was most active and showed a similar efficiency as WT. Biocatalysis experiments showed that OYERo2a, C25S, and C25G converted N-phenyl-2-methylmaleimide equally well (81–84%) with an enantiomeric excess (ee) of more than 99% for the R-product. With cyclic ketones, the highest conversion (89%) and ee (>99%) was observed for the reaction of WT with R-carvone. A remarkable poor conversion of cyclic ketones occurred with C25G. In summary, we established that the generation of a cysteine-free enzyme and cofactor optimization allows the development of more robust class III OYEs.

Benzoate Concentration and Cooperativity by a Substrate for Benzoate 1,2-dioxygenase from Benzoate-Degrading Rhodococcus Opacus 1CP

Benzoate Concentration and Cooperativity by a Substrate for Benzoate 1,2-dioxygenase from Benzoate-Degrading Rhodococcus Opacus 1CP

N-terminus determines activity and specificity of styrene monooxygenase reductases

Styrene monooxygenases (SMOs) are two-enzyme systems that catalyze the enantioselective epoxidation of styrene to (S)-styrene oxide. The FADH2 co-substrate of the epoxidase component (StyA) is supplied by an NADH-dependent flavin reductase (StyB). The genome of Rhodococcus opacus 1CP encodes two SMO systems. One system, which we define as E1-type, displays homology to the SMO from Pseudomonas taiwanensis VLB120. The other system, originally reported as a fused system (RoStyA2B), is defined as E2-type. Here we found that E1-type RoStyB is inhibited by FMN, while RoStyA2B is known to be active with FMN. To rationalize the observed specificity of RoStyB for FAD, we generated an artificial reductase, designated as RoStyBart, in which the first 22 amino acid residues of RoStyB were joined to the reductase part of RoStyA2B, while the oxygenase part (A2) was removed. RoStyBart mainly purified as apo-protein and mimicked RoStyB in being inhibited by FMN. Pre-incubation with FAD yielded a turnover number at 30°C of 133.9±3.5s−1, one of the highest rates observed for StyB reductases. RoStyBart holo-enzyme switches to a ping-pong mechanism and fluorescence analysis indicated for unproductive binding of FMN to the second (co-substrate) binding site. In summary, it is shown for the first time that optimization of the N-termini of StyB reductases allows the evolution of their activity and specificity.

Heterologous production of different styrene oxide isomerases for the highly efficient synthesis of phenylacetaldehyde

The styrene oxide isomerase (SOI, StyC) represents a key enzyme of the styrene-degrading pathway and has been discussed as promising biocatalyst during recent studies. The enzyme enables the synthesis of pure phenylacetaldehyde from styrene oxide. In this study the native as well as the corresponding codon-optimized genes of three different SOIs from Rhodococcus opacus 1CP (StyC-1CP), Sphingopyxis fribergensis Kp5.2 (StyC-Kp5.2), and Pseudomonas fluorescens ST (StyC-ST) were investigated for the expression in Escherichia coli BL21(DE3)pLysS. Specific enzyme activities of 61.9±7.5Umg−1, 23.2±2.8Umg−1, and 10.9±1.2Umg−1 were achieved after 6–9h for the codon-optimized gene of strain 1CP and the native genes of Kp5.2 and ST, respectively. Afterwards, these enzymes were enriched and applied for biotransformation studies. A complete conversion of 150mM styrene oxide to phenylacetaldehyde was observed for the enzyme StyC-Kp5.2 indicating a significantly improved stability towards product inactivation. Remarkably, more than 300mM product (>36gL−1, yield of about 80%) were finally synthesized from 400mM substrate with 150U of this enzyme within 60-120min. This represents the highest product concentration which has been reached with this type of enzymes, so far.

Morphological, physiological, and biochemical characteristics of a benzoate-degrading strain Rhodococcus opacus 1CP under stress conditions

Ability of actinobacteria Rhodococcus opacus 1CP to survive under unfavorable conditions and retain its biodegradation activity was assessed. The morphological and ultrastructural features of R. opacus 1CP cells degrading benzoate in the presence of oxidants and stress-protecting agents were investigated. The cells of R. opacus 1CP were resistant to oxidative stress caused by up to 100 mM H2O2 or up to 25 μM juglone (5-oxy-1,4-naphthoquinone). After 2 h of stress impact, changes in the fatty acid composition, increased activity of antioxidant enzymes, and changes in cell morphology and ultrastructure were observed. The strain retained its ability to degrade benzoate. Quercetin had a protective effect on benzoate-degrading cells of R. opacus 1CP. The strategy for cells survival under unfavorable conditions was formulated, which included decreased cell size/volume and formation of densely-packed cell conglomerates, in which the cells are embedded into a common matrix. Formation of conglomerates may probably be considered as a means for protecting the cells against aggressive environmental factors. The multicellular conglomerate structure and the matrix material impede the penetration of toxic substances into the conglomerates, promoting survival of the cells located inside.

Kinetics of interaction between substrates/substrate analogs and benzoate 1,2-dioxygenase from benzoate-degrading Rhodococcus opacus 1CP.

Benzoate 1,2-dioxygenase (BDO) of Rhodococcus opacus 1CP, which carried out the initial attack on benzoate, was earlier shown to be the enzyme with a narrow substrate specificity. A kinetics of interaction between benzoate 1,2-dioxygenase and substituted benzoates was assessed taking into account the enlarged list of the type of inhibition and using whole cells grown on benzoate. The type of inhibition was determined and the constants of a reaction of BDO with benzoate in the presence of 2-chlorobenzoate (2CBA), 3,5-dichlorobenzoate (3,5DCBA), and 3-methylbenzoate (3MBA) were calculated. For 2CBA and 3MBA, the types of inhibition were classified as biparametrically disсoordinated inhibition and transient inhibition (from activation towards inhibition), respectively. The process of not widely recognized pseudoinhibition of a BDO reaction with benzoate by 3,5DCBA was assessed by the vector method for the representation of enzymatic reactions. Ki value was determined for 2CBA, 3MBA, and 3,5DCBA as 337.5, 870.3, and 14.7 μM, respectively.

Immobilization of Rhodococcus opacus 1CP azoreductase to obtain azo dye degrading biocatalysts operative at acidic pH

A novel FMN-containing oxygen-insensitive azoreductase designated as AzoRo from strain Rhodococcus opacus 1CP was recently reported to enable higher dye degradation rate between pH 3.8 and 5, but its stability was poor. Attempts to improve it by making cross-linked enzyme aggregates and crystals were not successful. Thus covalent immobilization of AzoRo on modified mesoporous silicas was carried out using two types of mesoporous silica carriers with different pore structure: SBA-15 (ordered mesoporous silica) and meso-cellular foams (MCF). The supports were functionalized with amino and epoxy groups. Immobilized AzoRo (7.35 U mg−1) showed almost the same preference for pH and temperature as free enzyme (16.89 U mg−1) but stability was significantly improved. The immobilized enzyme was active after incubation at pH of 4.0 for 60 h, its storability was also improved and maximum activity was 5.2-fold higher than at standard conditions and even over 2.2 times higher than of free enzyme at pH 6.0. Compared to SBA-15, MCF catalysts showed higher activity probably due to larger pores and more open structure. Overall, AzoRo immobilization on mesoporous silicas appeared to be a successful strategy to obtain biocatalysts degrading azo dyes at lower pH up to 38.24 U mg−1 and over a longer period.

Changing the electron donor improves azoreductase dye degrading activity at neutral pH

The oxygen-insensitive azoreductase AzoRo originating from Rhodococcus opacus 1CP was found to be most active at low pH (ca. 4) and high temperature (ca. 50°C). AzoRo is not an efficient biocatalyst when used at low pH due to stability problems. To overcome this issue, we discovered that AzoRo accepts an alternative electron donor, 1-benzyl-1,4-dihydronicotinamide (BNAH), which allows fast turnover at neutral pH. In order to screen this nicotinamide coenzyme mimic as a source of electrons, AzoRo-catalysed reactions were run under neutral conditions, under which typically slow rates are observed with NADH. For the reduction of 1 azo bond by azoreductases 2mol nicotinamide coenzyme are needed. AzoRo displayed Methyl Red (MR) reduction activities with NADH and NADPH of 5.49±0.14Umg-1 and 4.96±0.25Umg-1, respectively, whereas with BNAH it displayed 17.01±0.74Umg-1 (following BNAH oxidation) and 7.16±0.06Umg-1 (following MR reduction). Binding of BNAH to AzoRo was determined with a Km of 18.75±2.45μM (BNAH oxidation) and 12.45±0.47μM (MR reduction). In order to show applicability of this system an upscaled reaction was performed using 78.6μg of purified AzoRo to convert 2.96μmol of MR (total reaction volume: 40ml) within a 1h reaction.

Dioxygenases of Chlorobiphenyl-Degrading Species Rhodococcus wratislaviensis G10 and Chlorophenol-Degrading Species Rhodococcus opacus 1CP Induced in Benzoate-Grown Cells and Genes Potentially Involved in These Processes.

Dioxygenases induced during benzoate degradation by the actinobacterium Rhodococcus wratislaviensis G10 strain degrading haloaromatic compounds were studied. Rhodococcus wratislaviensis G10 completely degraded 2g/liter benzoate during 30h and 10g/liter during 200h. Washed cells grown on benzoate retained respiration activity for more than 90 days, and a high activity of benzoate dioxygenase was recorded for 10 days. Compared to the enzyme activities with benzoate, the activity of benzoate dioxygenases was 10-30% with 13 of 35 substituted benzoate analogs. Two dioxygenases capable of cleaving the aromatic ring were isolated and characterized: protocatechuate 3,4-dioxygenase and catechol 1,2-dioxygenase. Catechol inhibited the activity of protocatechuate 3,4-dioxygenase. Protocatechuate did not affect the activity of catechol 1,2-dioxygenase. A high degree of identity was shown by MALDI-TOF mass spectrometry for protein peaks of the R. wratislaviensis G10 and Rhodococcus opacus 1CP cells grown on benzoate or LB. DNA from the R. wratislaviensis G10 strain was specifically amplified using specific primers to variable regions of genes coding α- and β-subunits of protocatechuate 3,4-dioxygenase and to two genes of the R. opacus 1CP coding catechol 1,2-dioxygenase. The products were 99% identical with the corresponding regions of the R. opacus 1CP genes. This high identity (99%) between the genes coding degradation of aromatic compounds in the R. wratislaviensis G10 and R. opacus 1CP strains isolated from sites of remote location (1400 km) and at different time (20-year difference) indicates a common origin of biodegradation genes of these strains and a wide distribution of these genes among rhodococci.

Biochemical characterization of an azoreductase from Rhodococcus opacus 1CP possessing methyl red degradation ability

Azo dyes, characterized by one or more R1NNR2 bonds, could be enzymatically metabolized. A flavin-containing oxygen-insensitive azoreductase designated as AzoRo (25KDa) from strain Rhodococcus opacus 1CP was identified and catalyses the initial degradation step of azo dyes. Protein sequence of AzoRo shared best identity of 33% to PaAzo1 from Pseudomonas aeruginosa for which the structure was solved, but clearly forms an own branch in the dendrogram. Thus AzoRo seems to be another subtype of azoreductases. The optimized gene coding for AzoRo of 214 amino acids was heterologously expressed in Escherichia coli BL21 (DE3). NADH served as an electron donor and a typical azo dye 2-(4-dimethylaminophenylazo) benzoic acid (methyl red) served as the substrate. The apparent kinetic values Km and Vmax of NADH are 10.07μM and 51.48U/mgprotein. Effect properties including pH, temperature and metal ions were characterized. Results showed AzoRo performed higher degradation velocity between pH 3.8–5 in acetate buffer. But, it would not be stable in that pH range. The thermal assay revealed the optimal temperature is 53°C. AzoRo remained stable from 10 to 40°C. However, the unfolding temperature is 55°C. RPHPLC analysis verified the products through AzoRo cleavage of methyl red. AzoRo is the first azoreductase obtained from a Rhodococcus strain which has been described in detail after initial biochemical characterization.