The Scientific World Journal

Volume 2014 (2014), Article ID 598518, 9 pages

http://dx.doi.org/10.1155/2014/598518

Research Article

Activity of a Carboxyl-Terminal Truncated Form of Catechol 2,3-Dioxygenase from Planococcus sp. S5

Katarzyna Hupert-Kocurek, Danuta Wojcieszyńska, and Urszula Guzik

Department of Biochemistry, Faculty of Biology and Environment Protection, University of Silesia in Katowice, Jagiellonska 28, 40-032 Katowice, Poland

Received 15 November 2013; Accepted 26 December 2013; Published 13 February 2014

Academic Editors: M. Y. Arica, A. A. Guevara-Garcia, and A. Scozzafava

Copyright © 2014 Katarzyna Hupert-Kocurek et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

Catechol 2,3-dioxygenases (C23Os, E.C.1.13.12.2) are two domain enzymes that catalyze degradation of monoaromatic hydrocarbons. The catalytically active C-domain of all known C23Os comprises ferrous ion ligands as well as residues forming active site pocket. The aim of this work was to examine and discuss the effect of nonsense mutation at position 289 on the activity of catechol 2,3-dioxygenase from Planococcus strain. Although the mutant C23O showed the same optimal temperature for activity as the wild-type protein (35°C), it exhibited activity slightly more tolerant to alkaline pH. Mutant enzyme exhibited also higher affinity to catechol as a substrate. Its K m (66.17 µM) was approximately 30% lower than that of wild-type enzyme. Interestingly, removal of the C-terminal residues resulted in 1.5- to 1.8-fold increase in the activity of C23OB61 against 4-methylcatechol and 4-chlorocatechol, respectively, while towards catechol the activity of the protein dropped to about 80% of that of the wild-type enzyme. The results obtained may facilitate the engineering of the C23O for application in the bioremediation of polluted areas.

1. Introduction

Aromatic compounds enter the environment either through natural processes (degradation of plant and animal residues) or as the result of anthropogenic activities [1]. They are common constituents of wastes originating from chemical, pharmaceutical, explosive, dyes, and agrochemicals industry [2]. Due to their potential toxicity to living organisms, including humans, as well as their mutagenicity and carcinogenicity aromatic compounds are pollutants of great environmental concern [2, 3]. Although aromatic molecules are considered to be among the most difficult to remove most of them are used by bacterial species as growth substrates [4–6]. The ability of microorganisms to grow in the presence of such compounds enables their potential applications for bioremediation strategies.

The strategy for degradation of aromatic structure by aerobic bacteria comprises hydroxylation and cleavage of the aromatic ring of catechol and its derivatives with the usage of oxygenases [7, 8]. One of the major mechanisms for aromatic ring degradation is its meta-fission catalyzed by extradiol dioxygenases in a position adjacent to the hydroxyl substituents, in a reaction involving incorporation of two atoms of oxygen [7, 9–11]. The catalytic mechanism of extradiol catechol dioxygenases is carried through several enzyme-bound intermediates. The reaction starts with bidentate binding of the substrate as catecholate monoanion to the active-site metal with simultaneous displacing of two water molecules [12, 13]. Binding of the substrate increases the affinity of the metal center for O₂ binding. The oxygen binds to the ferrous form of the enzyme resulting in delocalization of electron density onto the bound O₂ and semiquinone-FeII-superoxide intermediate formation. Subsequent Criegee rearrangement and O–O bond cleavage give a lactone intermediate and an FeII-bound hydroxide ion. Hydrolysis of the lactone and release of the reaction product (2-hydroxymuconate semialdehyde) complete the reaction cycle [7, 13].

Extradiol dioxygenases are versatile enzymes reacting with a wide range of substrates. They can be divided into two separate clades: those showing preference for monoaromatic compounds and those showing preference for polycyclic substrates [14]. Catechol 2,3-dioxygenases (C23Os) belonging to the extradiol dioxygenases family are involved in monoaromatic compounds degradation. These two domain enzymes are mainly oligomers and utilize a nonheme ferrous ion, and rarely manganese (II) or magnesium (II), to cleave the aromatic ring [7, 15, 16]. The catalytic metal in the active site is located at the end of a long funnel of the C-terminal domain. It is coordinated by three well-conserved residues, two histidines and one glutamate forming 2-His-1-carboxylate facial triad motif [12, 13]. Because of their importance in degradation of aromatic ring, C23Os have received in last decades a lot of attention. Knowledge of the molecular determinants relevant for their function and substrate specificity is essential to widen the ability of the microorganisms to transform aromatic compounds [17, 18].

C23O is catechol 2,3-dioxygenase that catalyzes ring cleavage of the catecholic compounds in Gram-positive Planococcus sp. strain S5, which is able to utilize benzoate, hydroxybenzoate, dihydroxybenzoate, phenol, and salicylate as growth substrates [19–21]. The structural gene for this enzyme (GenBank ID: HQ223337.2) was found in the plasmid and the nucleotide sequencing, and homology search revealed that it shares the greatest homology with isoenzymes from Gram-negative Pseudomonas strains [20]. Additionally, the product analysis and its sequence alignment with other dioxygenases suggest that C23O from strain S5 belongs to the type I superfamily of extradiol dioxygenases [22].

In our previous work, c23o gene from Planococcus sp. S5 was cloned and randomly mutated using error-prone PCR. From a random library of mutants 8 clones carrying at least one nonsilent mutation were obtained. In one of those mutant form of catechol 2,3-dioxygenase TGC codon for cysteine at position 103 had been changed to a CGC codon for arginine and the AAG codon at position 289 for lysine had been changed to a UAG stop codon [22]. While Cys103Arg amino acid substitution is localized within inactive N-terminal domain, Lys289stop substitution resulting in shortened protein is localized within C-domain of the enzyme [22]. As the C-terminal domain of all known C23Os is catalytically active [17, 23] the aim of the present study was to determine the effect of removal of terminal amino acid residues on catechol 2,3-dioxygenase structure and activity. The wild-type enzyme (C23Owt) and its carboxyl-terminal truncated form (C23OB61) were functionally expressed in E. coli and their activity and substrate specificity were characterized. Additionally, a putative three-dimensional (3D) structure of wild-type and mutant enzyme was determined. The significance of this study is to discuss the variation in activity of the wild-type and mutated catechol 2,3-dioxygenase towards methylcatechol- and 4-chlorocatechol based on the differences in structural properties of examined proteins. This knowledge gives clues to the design of enzymes with higher activity and altering substrate specificity.

2. Materials and Methods

2.1. Bacterial Strains and Growth Conditions

The bacterial strains and plasmids used in this study are listed in Table 1. Cells of Escherichia coli BL21 were grown in LB medium at 37°C and agitated at 125 rpm. All other strains harboring plasmids bearing the c23o gene were cultivated in LB medium supplemented with 100 μg/mL ampicillin at 37°C at 125 rpm. For overexpression of the wild-type and mutant C23O 1 mM isopropyl-β-D-thiogalactopyranoside (IPTG) was added to the medium.

Table 1: Strains and plasmids.

Strain or plasmid
Genotype and/or properties (reference); source

DH5C23OB61
E. coli [ endA1 glnV44 thi-1 recA1 relA1 gyrA96 deoR nupG 80dlacZΔM15 Δ(lacZYA-argF)U169, hsdR17( ), –] harboring c23oB61 gene [22]; laboratory stock

E. coli BL21
[fhuA2 [lon] ompT gal [dcm] ΔhsdS]; New England Biolabs

BL21C23Owt
E. coli BL21 harboring c23owt gene [22]; laboratory stock

BL21C23OB61
E. coli BL21 harboring c23oB61 gene (this work)

pUC19 c23oB61
Ampr, pUC19 derivative, c23oB61 encoding mutant form of catechol 2,3-dioxygenase (C103R, K289Stop) [22]

pET-22(b)
Ampr; Novagen

pc23oB61
Ampr, pET-22(b) derivative, c23oB61 encoding mutant form of catechol 2,3-dioxygenase (C103R, K289Stop) (this work)

2.2. Subcloning of c23oB61 Gene

The recombinant pUC19c23oB61 plasmid carrying mutated c23o gene was isolated from DH5C23OB61 clone with Plasmid Mini Kit (A&A Biotechnology, Poland) and digested with EcoRI and HindIII endonucleases (Fermentas) by standard procedures [24]. After gel purification, the DNA carrying the mutagenized gene was ligated into the EcoRI and HindIII endonuclease sites of pET-22(b) with T4 DNA ligase (Fermentas). The ligation mixture was then transformed into competent E. coli BL21 cells and plated on LB medium supplemented with ampicillin (100 μg/mL). Transformation of E.coli with plasmid DNA was performed by the RbCl procedure [25]. From transformants plasmids were isolated and those containing the correct insert were identified by restriction enzyme analysis. The presence of mutations in c23oB61 gene was then confirmed by DNA sequencing.

2.3. DNA Sequencing and Analysis

DNA sequencing was performed at the Department of Molecular Biology, Institute of Oncology DNA Sequencing Facility by using Big Dye_Terminator Cycle Sequencing Kit (Applied Biosystem) and AbiPrism_3100 Genetic Analyzer. Assembly and analysis of DNA sequences were performed with Chromas LITE software (Technelysium Pty, Tewantin, Australia).

2.4. Molecular Modeling of Mutant and the Wild-Type Catechol 2,3-Dioxygenase

Amino acid sequence of mutated form and the wild-type catechol 2,3-dioxygenase was deduced using the CLC Free Workbench 4.0.1 software. The deduced structure of the enzymes was modeled using the interactive mode of the 3D-JIGSAW protein comparative modeling server (http://bmm.cancerresearchuk.org/~3djigsaw/). Structure models as x.pdb data files were analyzed using RasMol 2.6 software package.

2.5. Overexpression of C23O in E. coli and Preparation of Cell-Free Extract

For overexpression of C23O, bacterial strains BL21C23Owt and BL21C23OB61 harboring c23owt and c23oB61m, respectively, were cultivated in 50 mL of LB medium supplemented with ampicillin (100 μg/mL) overnight at 37°C, and 5 mL of cells was then subcultured into 250 mL of the same medium and cultured under the same conditions. After the cell OD600 reached 0.4–0.6, IPTG was added to the final concentration of 1 mM. After further incubation for 4 h, cells were centrifuged at 4500 ×g for 15 min at 4°C. Next, the cells were washed with 50 mM phosphate buffer, pH 7.5, resuspended in the same buffer at concentration equivalent to an OD600 of 1.0, and ruptured by pulsed sonication (Vibra Cell TM) 6 times for 15 s. The disrupted cells suspensions were centrifuged at 9000 ×g for 30 min at 4°C to remove cell debris. The clear supernatant was used as crude extract for enzyme assays.

2.6. Enzyme Assay

In order to determine catechol 2,3-dioxygenase activity, the formation of 2-hydroxymuconic semialdehyde (2-HMS) was measured at 375 nm ( cm) in a reaction mixture containing 20 μL of catechol (50 mM), 960 μL of phosphate buffer pH 7.5 (50 mM), and 20 μL of crude extract in a total volume of 1 mL [26]. Control reactions (without crude extract) were performed for each assay. Protein concentrations of the crude extract from cultured bacteria were determined by the Bradford method [27]. One unit of C23O activity was defined as the enzyme amount required generating 1 μmol of product per minute. The specific activity is defined in mU per milligram of protein.

2.7. The Effect of pH and Temperature on C23O

The effect of pH on the enzymatic activity of mutant and the wild-type catechol 2,3-dioxygenase was determined by measuring the activity at 35°C, over the pH range of 2.2–10.7 using the following: 0.05 M glycine buffer (pH 2.2), 0.05 M phosphate-citrate buffer (pH 3.0 to 5.0), 0.05 M Sörensen-phosphate buffer (pH 6.0 to 8.0), 0.05 M borate buffer (pH 9.0), and carbonate buffer (pH 9.2 to 10.7).

The effect of temperature on the enzymatic activity of mutant and the wild-type enzyme was determined by measuring the activity using the reaction system described above with temperatures ranging between 4 and 50°C. All experiments were performed in 50 mM Tris-HCl buffer (pH 7.0). The enzyme and substrate solutions were preincubated and mixed and the enzymatic reaction was then carried out at the same temperature.

2.8. Determination of Kinetic Constants of C23O

The catalytic parameters (Michaelis-Menten constant, , and maximum velocity, ) were calculated for the wild-type and mutated form of C23O by measuring initial linear rates of the enzymatic reaction after the addition of different concentrations of the catechol ranging from 0 to 150 μM at 35°C. At least four independent measurements were carried out for each substrate concentration. and were calculated from the Hill equation using nonlinear regression analysis using the SigmaPlot software (SigmaPlot, version 12.0).

2.9. Substrate Specificity of C23O

The substrate specificity of mutated and wild-type catechol 2,3-dioxygenase was examined with 3-methylcatechol, 4-methylcatechol, and 4-chlorocatechol. The aromatic ring cleavage was determined by measuring the increase in the absorbance at the corresponding wavelength of each meta-cleavage product formed. Activity of C23O was assayed under the reaction conditions described above, using tested aromatic compounds instead of catechol as a substrate. The molar extinction coefficient used for the product from 3-methylcatechol was 13,800/M cm (at 388 nm), from 4-methylcatechol was 28,100/M cm (at 382 nm) [28], and from 4-chlorocatechol 40,000/M cm (at 379 nm) [29].

2.10. Statistical Analysis

All experiments were performed in four replicates. The obtained data were analyzed by one-way ANOVA and the statistical significance of differences in measured data was assessed by a post hoc comparison of the means using the least significant differences (LSD) test. Statistical analysis was performed using STATISTICA 10.0 PL software package.

3. Results and Discussion

3.1. Structural Properties of the Wild-Type and Mutant Catechol 2,3-Dioxygenase

Amino acid sequence in the polypeptide chain defines protein structure and properties. In order to determine the effect of mutations (C103R, K289Stop) on the structure and activity of catechol 2,3-dioxygenase from Planococcus strain, the 918-bp insert encoding carboxyl-terminal truncated form of C23O in the clone DH5C23OB61 [22] was subcloned into pET-22(b) vector to express the mutated enzyme in E. coli BL21. Localization of mutations was then confirmed by sequence analysis and amino acid sequence of the mutant enzyme was deduced. Based on the deduced amino acid sequence by using the interactive mode of the 3D-JIGSAW protein comparative modeling server the 3D structure of the wild-type and mutant form of catechol 2,3-dioxygenase from Planococcus strain was predicted.

Molecular studies on three-dimensional structure of catechol 2,3-dioxygenase (MPC) from Pseudomonas putida mt-2 have shown that the active site of the enzyme is located in the cavity within the C-terminal domain. The cavity is arranged as a funnel that is open to the molecular surface from one site and to an intersubunit interface from the other end. C-terminal end region of the C-terminal domain consists of 27 amino acid residues (Val280-Thr307) that cover and narrow the open region of the funnel [30]. In our studies structure of P. putida mt-2 catechol 2,3-dioxygenase (PDB accession code: 1mpy [30]) served as template for homology modeling of the wild-type and mutant C23O. Our data (Figures 1(a) and 1(b)) suggests the presence of externally located α-helices and internally located β-sheets, structures typical for many extradiol dioxygenases [16, 31, 32]. Additionally, the amino acids involved in metal binding in C23O from Planococcus strain (H153, H214 and E265) (Figures 1(c) and 1(d)) are the same as those of XylE and other extradiol dioxygenases [30–32]. The model of C23Owt (Figure 1(a)) shows 6 α-helices (α1–α6) analogous to the XylE model [30], while in the mutant form of protein (Figure 1(b)), as a result of nonsense mutation at position 289, α6 is removed and α5 is inclined that results in wider entrance to the active site.

(a)

(b)

(c)

(d)

Figure 1: The deduced 3D structure of the wild-type and mutated C23O from Planococcus sp. S5. Top row localization of the molecular domains of wild-type (a) and mutant (b) protein. Bottom row predicted structure of the active sites of the wild-type (c) and mutant (d) protein. Fe atoms are shown as light green spheres; the three residues involved in ferrous ions coordination are shown in red and amino acid residues involved in substrate binding are shown in green. Amino acid residues forming the entrance to the active site pocket are shown in yellow.

3.2. Effect of pH on the Mutant Catechol 2,3-Dioxygenase

To verify if introduced mutations influenced C23O activity, the effect of pH on the mutated and wild-type enzyme activity was determined. The wild-type C23O showed the highest activity at pH 7.0, while C23OB61 mutant exhibited activity slightly more tolerant to alkaline pH (Figure 2(a)) and was still 60% active at pH 9.2. pH between 7.0 and 7.5 was optimal for the wild-type C23Os from thermoacidophilic Sulfolobus solfataricus strain 98/2 [33], Bacillus thermoleovorans A2 [34], and rubber degrading bacterium Gordonia polyisoprenivorans [35]. Optimum pH at 8.0 showed catechol 2,3-dioxgenase from Stenotrophomonas maltophilia KB2 [36], while C23O from Pseudomonas putida GJ31 was the most active at pH 9.6. C23Os isolated from Bacillus strains [6] showed the highest activity at pH 10.0–11.0. Wild-type ThnC, an extradiol dioxygenase of a I.3 family involved in tetralin biodegradation, showed a strong dependence on pH with an optimum at pH 6.8–7 and just 35–40 % of the activity at pH 5.5. Some mutants of this enzyme (N213H, G206 M, A282R, and A282G) exhibited activity significantly more tolerant to acidic pH, although their pH optima were the same as that of wild-type ThnC, while for mutant optimal pH was displaced from 7.0 to 5.5 [9]. Substitution of arginine at position 296 with glutamine shifted an optimum pH of catechol 2,3-dioxygenase from Planococcus strain from 7.0 to 5.0. Activity of this mutant protein at pH 5.0 and pH 4.0 relative to its activity at pH 7.0 was 144.7% and 124%, respectively [22]. In contrast, mutated C23O from Pseudomonas strain became more alkalescency stable compared with the wild-type enzyme and retained 75% of the maximal enzyme activity even under pH 9.5 [37].

(a)

(b)

Figure 2: Effects of pH (a) and temperature (b) on the activity of wild-type (C23Owt) and the mutant (C23OB61) dioxygenases. The data shown in this figure represent the mean ± SD of four experimental replicates.

3.3. Effect of Temperature on the Mutant Catechol 2,3-Dioxygenase

Most of the examined C23Os show maximal activity at 30–40°C [35, 37–39]. The temperature optimum of the reaction rate of catechol 2,3-dioxygenase from Pseudomonas putida GJ31 was estimated to be 50°C. However, denaturation of the enzyme was significant at this temperature [40]. C23O isolated from thermophilic Bacillus thermoleovorans A2 [34] as well as four other Bacillus isolates [6] showed the highest activity at 70°C. However, the half-life of the enzyme from strain A2 was only 1.5 min at this temperature [34]. It has been shown that introduced mutations may affect thermostability of enzymes. For example, replacement of Ala229 and His294 in catechol-2,3-dioxygenase from Pseudomonas sp. CGMCC2953 by cysteine resulting in formation of additional disulfide bond widened the optimum temperature of such mutated enzyme from 40°C to 40–50°C [37]. The proline rule for thermostabilizing proteins has been proposed by Suzuki et al. [41]. For different enzymes, including extradiol dioxygenases, the percentage of Pro residues was found to be higher in thermostable compared to mesophilic ones [42, 43]. In molecular stabilization of protein introduction of prolines was effective for α-glucosidase from Thermoanaerobacter tengcongensis MB4 or methyl parathion hydrolase from Ochrobactrum sp. M231 [44, 45]. Determination of the effect of temperature on the mutated and wild-type catechol 2,3-dioxygenase activity indicated that introduced mutations did not change optimal temperature for the enzyme activity. Either C23Owt or C23OB61 showed the highest activity at 35°C (Figure 2(b)). Analysis of amino acid sequences of C23OB61 mutant has shown that introduced mutations did not increase the percentage of cysteine and proline residues. We may speculate that for this reason temperature profiles of the mutant and wild-type enzyme activity were similar.

3.4. Catalytic Parameters of the Mutant Protein

In order to investigate the effect of introduced mutations on the C23O activity for catechol, the specific activities of wild-type and mutant enzyme for this substrate were measured using recombinant E. coli extracts (Table 2). Using various concentrations of catechol as the substrate and of wild-type C23O and its mutant were determined (Table 3). Although C23OB61 showed lower activity towards catechol than the wild-type enzyme (Table 2), it exhibited higher affinity to this substrate (Table 3). Its (66.17 ± 9.44 μM) was approximately 30% lower than that of wild-type enzyme (97.74 ± 10.91 μM) (Figure 3). Based on the predicted structures (Figure 1), we can hypothesize that obtained mutations, especially removal of residues involved in formation of the lid over the substrate-binding pocket, provide an easier access of the substrate to the active site and for positioning the catechol molecule bound to iron. According to Riegert et al. [46], a reduced accessibility of the active center to the substrate reduced substrate affinity of the mutant form of 2,3-dihydroxybiphenyl 1,2-dioxygenase from Sphingomonas xenophaga BN6.

Table 2: Specific and relative activity of wild-type (wt) and mutant C23O dioxygenases using different catechols as the substrate.

Substrate
C23Owt
C23OB61

Specific activity

(mU/mg)a
Relative

activityb %
Relative

activityc %
Specific activity

(mU/mg)a
Relative

activityb %
Relative

activityc %

Catechol

100
100

78.70
100

3-Methylcatechol

100
6.12

182.03
14.16

4-Methylcatechol

100
101.91

145.45
188.32

4-Chlorocatechol

100
44.88

178.57
101.82

. One unit of C23O activity was defined as the enzyme amount required generating 1 µmol of product per minute. The specific activity is defined in mU per milligram of protein.

bExpressed as a percentage of the C23Owt-specific activity which is set as 100%.

cExpressed as a percentage of the C23Os-specific activity toward catechol as a substrate which is set as 100%.

All data shown were expressed as mean standard deviation ().

Table 3: Kinetic parameters for catechol oxygenation to 2-hydroxymuconic semialdehyde by wild-type (wt) and mutant C23O dioxygenases.

Enzyme/substrate
C23Owt
C23OB61

(µM)
(mU/mg)
(µM)
(mU/mg)

Catechol

All data shown were expressed as mean standard deviation ().

(a)

(b)

(c)

Figure 3: Effects of substrate concentration on the activity of wild-type ((a), (c)) and mutant C23OB61 ((b), (c)) protein. The data points represent the mean ± SD of four experimental replicates.

3.5. Substrate Range of the Mutant Protein

Extradiol dioxygenases cleave a wide variety of catecholic and noncatecholic substrates [17]. From this group of enzymes, catechol 2,3-dioxygenases are known to catalyze ring cleavage of catechol and its chloro-, methyl-, and ethyl-derivatives [5, 12, 47]. However, the reactivity of C23Os to catechol is usually higher than the reactivity of these enzymes to substituted catechols [5, 47]. It has been suggested that substituted catechols promote more rapid inactivation of the enzyme because the substituent hinders the correct positioning of the substrate or of dioxygen at the active site [46, 48]. In this study the substrate range of C23Owt and mutant protein was examined by incubating the enzyme with catechol, 3-methylcatechol, 4-methylcatechol, or 4-chlorocatechol and determining the rate of appearance of products. Interestingly, the obtained mutations caused an increase in the activity of C23O against para-substituted catechol derivatives, while towards catechol the activity of mutant protein dropped to about 80% of that of the wild-type enzyme (Table 2). Considering that the C-terminal region of mutant protein is shorter compared with that from wild-type C23O there is a wider entrance to the active site in C23OB61 compared with C23Owt. This in turn facilitates the access and proper positioning of the substrates with chloro- and methyl-groups in the mutant enzyme active site. The role of C-terminal tail in determination of substrate specificity of AkbC by restricting the access of large substrates to the active site was also suggested by Cho et al. [12]. After removal of the last five of 305 amino acid residues of AkbC they observed 7-fold increase in the enzyme activity against 3-methylcatechol and even 9-fold increase in AkbC activity towards dihydroxybenzoate. Although for C23O enzymatic activity the C-terminal domain is essential, we cannot exclude the possibility that mutation C103R within N-domain of C23O may also affect the enzyme parameters. However, this speculation needs further investigations.

4. Conclusions

We showed that substrate specificity and activity of catechol 2,3-dioxygenase can be modulated by shortening the protein at C-terminal end. The removal of terminal amino acid residues forming the lid that covers the entrance to the substrate-binding pocket of C23O caused an increase in activity of the enzyme against 4-methylcatechol and 4-chlorocatechol. Obtained results may facilitate the engineering of the C23O for bioremediation of environments contaminated with cresols and chloroaromatic compounds.

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.

Acknowledgments

The authors thank Dr. Renata Zub (Department of Molecular Biology, Institute of Oncology, Warsaw, Poland) for DNA sequencing. Agnieszka Stawicka is acknowledged for an excellent technical assistance.

References

E. S. Shumkova, I. P. Solyanikova, E. G. Plotnikova, and L. A. Golovleva, “Phenol degradation by Rhodococcus opacus strain 1G,” Applied Biochemistry and Microbiology, vol. 45, no. 1, pp. 43–49, 2009.

J. Michałowicz and W. Duda, “Phenols—sources and toxicity,” Polish Journal of Environmental Studies, vol. 16, no. 3, pp. 347–362, 2007.

X. Li, T. Zhang, X. Min, and P. Liu, “Toxicity of aromatic compounds to Tetrahymena estimated by microcalorimetry and QSAR,” Aquatic Toxicology, vol. 98, no. 4, pp. 322–327, 2010.

I. Bertini, F. Briganti, S. Mangani, H. F. Nolting, and A. Scozzafava, “Biophysical investigation of bacterial aromatic extradiol dioxygenases involved in biodegradation processes,” Coordination Chemistry Reviews, vol. 144, pp. 321–345, 1995.

D. Kim, J.-C. Chae, J. Y. Jang et al., “Functional characterization and molecular modeling of methylcatechol 2,3-dioxygenase from o-xylene-degrading Rhodococcus sp. strain DK17,” Biochemical and Biophysical Research Communications, vol. 326, no. 4, pp. 880–886, 2005.

L. Djokic, T. Narancic, J. Nikodinovic-Runic, S. Bajkic, and B. Vasiljevic, “Four Bacillus sp. soil isolates capable of degrading phenol, toluene, biphenyl, naphthalene and other aromatic compounds exhibit different aromatic catabolic potentials,” Archives of Biological Sciences, vol. 63, no. 4, pp. 1057–1067, 2011.

T. D. H. Bugg, “Dioxygenase enzymes: catalytic mechanisms and chemical models,” Tetrahedron, vol. 59, no. 36, pp. 7075–7101, 2003.

S. Fetzner, “Ring-cleaving dioxygenases with a cupin fold,” Applied and Environmental Microbiology, vol. 78, no. 8, pp. 2505–2514, 2012.

E. Andujar and E. Santero, “Site-directed mutagenesis of an extradiol dioxygenase involved in tetralin biodegradation identifies residues important for activity or substrate specificity,” Microbiology, vol. 149, no. 6, pp. 1559–1567, 2003.

A. Viggiani, L. Siani, E. Notomista, L. Birolo, P. Pucci, and A. di Donato, “The role of the conserved residues His-246, His-199, and Tyr-255 in the catalysis of catechol 2,3-dioxygenase from Pseudomonas stutzeri OX1,” The Journal of Biological Chemistry, vol. 279, no. 47, pp. 48630–48639, 2004.

E. Kalogeris, Y. Sanakis, D. Mamma, P. Christakopoulos, D. Kekos, and H. Stamatis, “Properties of catechol 1,2-dioxygenase from Pseudomonas putida immobilized in calcium alginate hydrogels,” Enzyme and Microbial Technology, vol. 39, no. 5, pp. 1113–1121, 2006.

H. J. Cho, K. Kim, S. Y. Sohn et al., “Substrate binding mechanism of a type I extradiol dioxygenase,” The Journal of Biological Chemistry, vol. 285, no. 45, pp. 34643–34652, 2010.

M. Costas, M. P. Mehn, M. P. Jensen, and L. Que, “Dioxygen activation at mononuclear nonheme iron active sites: enzymes, models, and intermediates,” Chemical Reviews, vol. 104, no. 2, pp. 939–986, 2004.

S. Harayama and M. Rekik, “Bacterial aromatic ring-cleavage enzymes are classified into two different gene families,” The Journal of Biological Chemistry, vol. 264, no. 26, pp. 15328–15333, 1989.

A. Gibello, E. Ferrer, M. Martin, and A. Garrido-Pertierra, “3,4-Dihydroxyphenylacetate 2,3-dioxygenase from Klebsiella pneumoniae, a Mg²⁺-containing dioxygenase involved in aromatic catabolism,” Biochemical Journal, vol. 301, no. 1, pp. 145–150, 1994.

T. Hatta, G. Mukerjee-Dhar, J. Damborsky, H. Kiyohara, and K. Kimbara, “Characterization of a novel thermostable Mn(II)-dependent 2,3-dihydroxybiphenyl 1,2-dioxygenase from a polychlorinated biphenyl- and naphthalene-degrading Bacillus sp. JF8,” The Journal of Biological Chemistry, vol. 278, no. 24, pp. 21483–21492, 2003.

F. H. Vaillancourt, J. T. Bolin, and L. D. Eltis, “The ins and outs of ring-cleaving dioxygenases,” Critical Reviews in Biochemistry and Molecular Biology, vol. 41, no. 4, pp. 241–267, 2006.

G. Fuchs, M. Boll, and J. Heider, “Microbial degradation of aromatic compounds—from one strategy to four,” Nature Reviews Microbiology, vol. 9, no. 11, pp. 803–816, 2011.

I. Greń, K. Hupert-Kocurek, M. Osiecka, U. Guzik, and D. Wojcieszyńska, “Toxicity of 4-chlorophenol under cometabolic conditions depending on the bacterial cell wall structure?” Architecture Civil Engineering Environment, vol. 5, no. 3, pp. 101–107, 2012.

K. Hupert-Kocurek, U. Guzik, and D. Wojcieszyńska, “Characterization of catechol 2, 3-dioxygenase from Planococcus sp. strain S5 induced by high phenol concentration,” Acta Biochimica Polonica, vol. 59, no. 3, pp. 1–7, 2012.

S. Łabużek, K. T. Hupert-Kocurek, and M. Skurnik, “Isolation and characterisation of new Planococcus sp. strain able for aromatic hydrocarbons degradation,” Acta Microbiologica Polonica, vol. 52, no. 4, pp. 395–404, 2003.

K. Hupert-Kocurek, A. Stawicka, D. Wojcieszynska, and U. Guzik, “Cloning and mutagenesis of catechol 2, 3-dioxygenase gene from the gram-positive Planococcus sp. strain S5,” Journal of Molecular Microbiology and Biotechnology, vol. 23, pp. 381–390, 2013.

T. D. H. Bugg and S. Ramaswamy, “Non-heme iron-dependent dioxygenases: unravelling catalytic mechanisms for complex enzymatic oxidations,” Current Opinion in Chemical Biology, vol. 12, no. 2, pp. 134–140, 2008.

J. Sambrook, E. F. Fritsch, and T. Maniatis, Molecular Cloning: A Laboratory Manual, Cold Spring Harbor Laboratory, New York, NY, USA, 2nd edition, 1989.

D. Hanahan, “Studies on transformation of Escherichia coli with plasmids,” Journal of Molecular Biology, vol. 166, no. 4, pp. 557–580, 1983.

C. F. Feist and G. D. Hegeman, “Phenol and benzoate metabolism by Pseudomonas putida: regulation of tangential pathways,” Journal of Bacteriology, vol. 100, no. 2, pp. 869–877, 1969.

M. M. Bradford, “A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein dye binding,” Analytical Biochemistry, vol. 72, no. 1-2, pp. 248–258, 1976.

R. C. Bayly, S. Dagley, and D. T. Gibson, “The metabolism of cresols by species of Pseudomonas,” Biochemical Journal, vol. 101, no. 2, pp. 293–301, 1966.

H. S. Bae, M. Lee, J. B. Kim, and S. T. Lee, “Biodegradation of the mixtures of 4-chlorophenoI and phenol by Comamonas testosteroni CPW301,” Biodegradation, vol. 7, no. 6, pp. 463–469, 1996.

A. Kita, S. Kita, I. Fujisawa et al., “An archetypical extradiol-cleaving catecholic dioxygenase: the crystal structure of catechol 2,3-dioxygenase (metapyrocatechase) from Pseudomonas putida mt-2,” Structure, vol. 7, no. 1, pp. 25–34, 1999.

E. G. Kovaleva and J. D. Lipscomb, “Crystal structures of Fe²⁺ dioxygenase superoxo, alkylperoxo, and bound product intermediates,” Science, vol. 316, no. 5823, pp. 453–457, 2007.

T. Senda, K. Sugiyama, H. Narita et al., “Three-dimensional structures of free form and two substrate complexes of an extradiol ring-cleavage type dioxygenase, the BphC enzyme from Pseudomonas sp. strain KKS102,” Journal of Molecular Biology, vol. 255, no. 5, pp. 735–752, 1996.

J.-C. Chae, E. Kim, E. Bini, and G. J. Zylstra, “Comparative analysis of the catechol 2,3-dioxygenase gene locus in thermoacidophilic Archaeon Sulfolobus solfataricus strain 98/2,” Biochemical and Biophysical Research Communications, vol. 357, no. 3, pp. 815–819, 2007.

R. E. Milo, F. M. Duffner, and R. Muller, “Catechol 2,3-dioxygenase from the thermophilic, phenol-degrading Bacillus thermoleovorans strain A2 has unexpected low thermal stability,” Extremophiles, vol. 3, no. 3, pp. 185–190, 1999.

A. S. Silva, F. A. de Oliveira Camargo, R. Andreazza, R. J. S. Jacques, D. B. Baldoni, and F. M. Bento, “Enzymatic activity of catechol 1, 2-dioxygenase and catechol 2, 3-dioxygenase produced by Gordonia polyisoprenivorans,” Quimica Nova, vol. 35, no. 8, pp. 1587–1592, 2012.

D. Wojcieszyńska, K. Hupert-Kocurek, A. Jankowska, and U. Guzik, “Properties of catechol 2,3-dioxygenase from crude extract of Stenotrophomonas maltophilia strain KB2 immobilized in calcium alginate hydrogels,” Biochemical Engineering Journal, vol. 66, pp. 1–7, 2012.

J. Wei, Y. Zhou, T. Xu, and B. Lu, “Rational design of catechol-2, 3-dioxygenase for improving the enzyme characteristics,” Applied Biochemistry and Biotechnology, vol. 162, no. 1, pp. 116–126, 2010.

K.-P. Kim, D.-I. Seo, K.-H. Min, J.-O. Ka, Y.-K. Park, and C.-K. Kim, “Characteristics of catechol 2,3-dioxygenase produced by 4-chlorobenzoate-degrading Pseudomonas sp. S-47,” Journal of Microbiology, vol. 35, no. 4, pp. 295–299, 1997.

Y. Zhou, J. Wei, T. Jiang, W. Gao, Y. Ma, and D. Wei, “Characterisation of a thermostable catechol-2,3-dioxygenase from phenanthrene-degrading Pseudomonas sp. strain ZJF08,” Annals of Microbiology, vol. 57, no. 4, pp. 503–508, 2007.

S. R. Kaschabek, T. Kasberg, D. Müller, A. E. Mars, D. B. Janssen, and W. Reineke, “Degradation of chloroaromatics: purification and characterization of a novel type of chlorocatechol 2,3-dioxygenase of Pseudomonas putida GJ31,” Journal of Bacteriology, vol. 180, no. 2, pp. 296–302, 1998.

Y. Suzuki, K. Oishi, H. Nakano, and T. Nagayama, “A strong correlation between the increase in number of proline residues and the rise in thermostability of five Bacillus oligo-1,6-glucosidases,” Applied Microbiology and Biotechnology, vol. 26, no. 6, pp. 546–551, 1987.

F.-M. Dong, L.-L. Wang, C.-M. Wang et al., “Molecular cloning and mapping of phenol degradation genes from Bacillus stearothermophilus FDTP-3 and their expression in Escherichia coli,” Applied and Environmental Microbiology, vol. 58, no. 8, pp. 2531–2535, 1992.

F. M. Duffner, U. Kirchner, M. P. Bauer, and R. Müller, “Phenol/cresol degradation by the thermophilic Bacillus thermoglucosidasius A7: cloning and sequence analysis of five genes involved in the pathway,” Gene, vol. 256, no. 1-2, pp. 215–221, 2000.

J. Tian, P. Wang, S. Gao, X. Chu, N. Wu, and Y. Fan, “Enhanced thermostability of methyl parathion hydrolase from Ochrobactrum sp. M231 by rational engineering of a glycine to proline mutation,” FEBS Journal, vol. 277, no. 23, pp. 4901–4908, 2010.

C. Zhou, Y. Xue, and Y. Ma, “Enhancing the thermostability of α-glucosidase from Thermoanaerobacter tengcongensis MB4 by single proline substitution,” Journal of Bioscience and Bioengineering, vol. 110, no. 1, pp. 12–17, 2010.

U. Riegert, S. Bürger, and A. Stolz, “Altering catalytic properties of 3-chlorocatechol-oxidizing extradiol dioxygenase from Sphingomonas xenophaga BN6 by random mutagenesis,” Journal of Bacteriology, vol. 183, no. 7, pp. 2322–2330, 2001.

A. Okuta, K. Ohnishi, and S. Harayama, “Construction of chimeric catechol 2,3-dioxygenase exhibiting improved activity against the suicide inhibitor 4-methylcatechol,” Applied and Environmental Microbiology, vol. 70, no. 3, pp. 1804–1810, 2004.

A. E. Mars, J. Kingma, S. R. Kaschabek, W. Reineke, and D. B. Janssen, “Conversion of 3-chlorocatechol by various catechol 2,3-dioxygenases and sequence analysis of the chlorocatechol dioxygenase region of Pseudomonas putida GJ31,” Journal of Bacteriology, vol. 181, no. 4, pp. 1309–1318, 1999.