Degradation of 2-chloroethanol by wild type and mutants of Pseudomonas putida US2

A strain of Pseudomonas putida was isolated that was able to degrade 2-chloroethanol. The degradation proceeded via 2-chloroacetaldehyde and chloroacetate to glycolate. In crude extracts the enzymes for this degradation pathway could be detected. All enzymes proved to be inducible. The dehalogenase that catalyzed the dehalogenation of chloroacetate to glycolate was further characterized. It consisted of a single polypeptide chain with a molecular mass of 28 kDa. After induction the dehalogenase was expressed at a high level. In a mutant resistant to high concentrations of 2-chloroethanol the dehalogenase was no longer expressed. The mechanism of resistance seemed to be due to the inability to convert chloroacetate and export of this compound out of the cell.Non-standard abbreviations CEO 2-chloroethanol - DCPIP 2,6-dichlorophenolindophenol - FPLC fast protein liquid chromatography - PAGE polyacrylamide gelelectrophoresis - PES phenazine ethosulfate - PMS phenazine methosulfate - PQQ pyrroloquinoline quinone     

Isolation of a Xanthobacter sp. degrading dichloromethane and characterization of the gene involved in the degradation

A bacterial strain able to degrade dichloromethane (DCM) as the sole carbon source was isolated from a wastewater treatment plant receiving domestic and pharmaceutical effluent. 16S rDNA studies revealed the strain to be a Xanthobacter sp. (strain TM1). The new isolated strain when grown aerobically on DCM showed Luong type growth kinetics, with μ_max of 0.094 h⁻¹ and S _m of 1,435 mg l⁻¹. Strain TM1 was able to degrade other aromatic and aliphatic halogenated compounds, such as halobenzoates, 2-chloroethanol and dichloroethane. The gene for DCM dehalogenase, which is the key enzyme in DCM degradation, was amplified through PCR reactions. Strain TM1 contains type A DCM dehalogenase (dcmAa), while no product could be obtained for type B dehalogense (dcmAb). The sequence was compared against 12 dcmAa from other DCM degrading strains and 98% or 99% similarity was observed with all other previously isolated DCM dehalogenase genes. This is the first time a Xanthobacter sp. is reported to degrade DCM.     

Structure and denaturation of 4-chlorobenzoyl coenzyme A dehalogenase from <Emphasis Type="Italic">Arthrobacter</Emphasis> sp. strain TM-1

The secondary structure of the trimeric protein 4-chlorobenzoyl coenzyme A dehalogenase from Arthrobacter sp. strain TM-1, the second of three enzymes involved in the dechlorination of 4-chlorobenzoate to form 4-hydroxybenzoate, has been examined. E_mM for the enzyme was 12.59. Analysis by circular dichroism spectrometry in the far uv indicated that 4-chlorobenzoyl coenzyme A dehalogenase was composed mostly of α-helix (56%) with lesser amounts of random coil (21%), β-turn (13%) and β-sheet (9%). These data are in close agreement with a computational prediction of secondary structure from the primary amino acid sequence, which indicated 55.8% α-helix, 33.7% random coil and 10.5% β-sheet; the enzyme is, therefore, similar to the 4-chlorobenzoyl coenzyme A dehalogenase from Pseudomonas sp. CBS-3. The three-dimensional structure, including that of the presumed active site, predicted by computational analysis, is also closely similar to that of the Pseudomonas dehalogenase. Study of the stability and physicochemical properties revealed that at room temperature, the enzyme was stable for 24 h but was completely inactivated by heating to 60°C for 5 min; thereafter by cooling at 1°C min⁻¹ to 45°C, 20.6% of the activity could be recovered. Mildly acidic (pH 5.2) or alkaline (pH 10.1) conditions caused complete inactivation, but activity was fully recovered on returning the enzyme to pH 7.4. Circular dichroism studies also indicated that secondary structure was little altered by heating to 60°C, or by changing the pH from 7.4 to 6.0 or 9.2. Complete, irreversible destruction of, and maximal decrease in the fluorescence yield of the protein at 330–350 nm were brought about by 4.5 M urea or 1.1 M guanidinium chloride. Evidence was obtained to support the hypothetical three-dimensional model, that residues W140 and W167 are buried in a non-polar environment, whereas W182 appears at or close to the surface of the protein. At least one of the enzymes of the dehalogenase system (the combined 4-chlorobenzoate:CoA ligase, the dehalogenase and 4-hydroxybenzoyl coenzyme A thioesterase) appears to be capable of association with the cell membrane.

Genetics and biochemistry of 1,2-dichloroethane degradation

Dichloroethane (1,2-DCE) is a synthetic compound that is not known to be formed naturally. Nevertheless, several pure microbial cultures are able to use it as a sole carbon source for growth. Degradation of 1,2-DCE proceeds via 2-chloroethanol, chloroacetaldehyde and chloroacetate to glycolate. The genes encoding the enzymes responsible for the conversion of 1,2-DCE to glycolic acid have been isolated. The haloalkane dehalogenase and an aldehyde dehydrogenase are plasmid encoded. Two other enzymes, the alcohol dehydrogenase and the haloacid dehalogenase, are chromosomally encoded. Sequence analysis indicates that the haloacid dehalogenase belongs to the L-specific 2-chloroproprionic acid dehalogenases. From the three-dimensional structure and sequence similarities, the haloalkane dehalogenase appears to be a member of the / hydrolase fold hydrolytic enzymes, of which several are involved in the degradation of aromatic and aliphatic xenobiotic compounds.     

Properties of tetrachloroethene and trichloroethene dehalogenase of Dehalospirillum multivorans

Some properties of tetrachloroethene and trichloroethene dehalogenase of the recently isolated, tetrachloroethene-utilizing anaerobe, Dehalospirillum multivorans, were studied with extracts of cells grown on pyruvate plus fumarate. The dehalogenase catalyzed the oxidation of reduced methyl viologen with tetrachloroethene (PCE) or trichloroethene (TCE) as electron acceptor. All other artificial or physiological electron donors tested were ineffective. The PCE and TCE dehalogenase activity was insensitive towards oxygen in crude extracts. When extracts were incubated under anoxic conditions in the presence of titanium citrate as reducing agent, the dehalogenase was rapidly inactivated by propyl iodide (50 M). Inactivation did not occur in the absence of titanium citrate. The activity of propyl-iodide-treated extracts was restored almost immediately by illumination. The dehalogenase was inhibited by cyanide. The inhibition profile was almost the same under oxic and anoxic conditions independent of the presence or absence of titanium citrate. In addition, N₂O, nitrite, and ethylene diamine tetra-acetate (EDTA) were inhibitors of PCE and TCE dehalogenase. Carbon monoxide and azide had no influence on the dehalogenase activity. Trans-1,2-dichloroethene or 1,1-dichloroethene, both of which are isomers of the dechlorination product cis-1,2-dichloroethene, neither inhibited nor inactivated the dehalogenase. PCE and TCE dechlorination appeared to be mediated by the same enzyme since the inhibitors tested had nearly the same effects on the PCE and TCE dehalogenating activity. The data indicated the involvement of a corrinoid and possibly of an additional transition metal in reductive PCE and TCE dechlorination.Abbreviations PCE Tetrachloroethene - TCE Trichloroethene - DCE Dichloroethene - EDTA Ethylene diamine tetra-acetate - MV Methyl viologen - BV Benzyl viologen - PI Propyl iodide, 1-iodopropane - TC Titanium(III) citrate     

Cloning and characterization of dichloromethane dehalogenase from Methylobacterium rhodesianum for dichloromethane degradation

The gene encoding dichloromethane dehalogenase from Methylobacterium rhodesianum was cloned. Bioinformatic analysis showed that dichloromethane dehalogenase gene sequence from M. rhodesianum is almost identical to the one from Methylobacterium extorquens, with only one base difference. Dichloromethane dehalogenase was subsequently expressed in Escherichia coli BL21 (DE3) and purified. It was found that enzyme activity in recombinant cells was 3 times higher than that in the wild-type M. rhodesianum. Further investigation showed that recombinant dichloromethane dehalogenase was most active at 40°C at pH 7–8, and its K_M was 10.96 mM when treated with dichloromethane as substrate. The fitted curve of dichloromethane degradation gave a V_max of 0.43 mM/h of in 0.01 M phosphate buffer. Degradation efficiency of dichloromethane reached 86.11% within 20 h. In addition, it was found that degradation efficiency of dichloromethane was highly associated with glutathione concentration, supporting the reports that glutathione functions as coenzyme of dichloromethane dehalogenase for dichloromethane degradation.     

Molecular characterization of the enzymes involved in the degradation of a brominated aromatic herbicide

Dehalogenation is the key step in the degradation of halogenated aromatics, while reductive dehalogenation is originally thought to rarely occur in aerobes. In this study, an aerobic strain of Comamonas sp. 7D‐2 was shown to degrade the brominated aromatic herbicide bromoxynil completely and release two equivalents of bromides under aerobic conditions. The enzymes involved in the degradation of bromoxynil to 4‐carboxy‐2‐hydroxymuconate‐6‐semialdehyde, including nitrilase, reductive dehalogenase (BhbA), 4‐hydroxybenzoate 3‐monooxygenase and protocatechuate 4,5‐dioxygenase, were molecularly characterized. The novel dehalogenase BhbA was shown to be a complex of a respiration‐linked reductive dehalogenase (RdhA) domain and a NAD(P)H‐dependent oxidoreductase domain and to have key features of anaerobic respiratory RdhAs, including two predicted binding motifs for [4Fe‐4S] clusters and a close association with a hydrophobic membrane protein (BhbB). BhbB was confirmed to anchor BhbA to the membrane. BhbA was partially purified and found to use NAD(P)H as electron donors. Full‐length bhbA homologues were found almost exclusively in marine aerobic proteobacteria, suggesting that reductive dehalogenation occurs extensively in aerobes and that bhbA is horizontally transferred from marine microorganisms. The discovery of a functional reductive dehalogenase and ring‐cleavage oxygenases in an aerobe opens up possibilities for basic research as well as the potential application for bioremediation.     

Dehalogenation of 4-chlorobenzoate

Pseudomonas sp. CBS3 is capable of growing with 4-chlorobenzoate as sole source of carbon and energy. The removal of the chlorine of 4-chlorobenzoate is performed in the first degradation step by an enzyme system consisting of three proteins. A 4-halobenzoate-coenzyme A ligase activates 4-chlorobenzoate in a coenzyme A, ATP and Mg²⁺ dependent reaction to 4-chlorobenzoyl-coenzyme A. This thioester intermediate is dehalogenated by the 4-chlorobenzoyl-coenzyme A dehalogenase. Finally coenzyme A is split off by a 4-hydroxybenzoyl-CoA thioesterase to form 4-hydroxybenzoate. The involved 4-chlorobenzoyl-coenzyme A dehalogenase was purified to apparent homogeneity by a five-step purification procedure. The native enzyme had an apparent molecular mass of 120,000 and was composed of four identical polypeptide subunits of 31 kDa. The enzyme displayed an isoelectric point of 6.7. The maximal initial rate of catalysis was achieved at pH 10 at 60 °C. The apparent K _m value for 4-chlorobenzoyl-coenzyme A was 2.4–2.7 µM. V _max was 1.1 × 10^–7 M sec^–1 (2.2 µmol min^–1 mg^–1 of protein). The NH₂-terminal amino acid sequence was determined. All 4-halobenzoyl-coenzyme A thioesters, except 4-fluorobenzoyl-coenzyme A, were dehalogenated by the 4-chlorobenzoyl-CoA dehalogenase.Abbreviations CBA chlorobenzoate - CoA coenzyme A - HBA hydroxybenzoate - DTT dithiothreitol - HPLC high performance liquid chromatography - PAGE polyacrylamide gel electrophoresis     

Dichloromethane as the sole carbon source forHyphomicrobium sp. strain DM2 under denitrification conditions

Hyphomicrobium sp. strain DM2 was found to grow anaerobically in the presence of nitrate with methanol, formaldehyde, formate or dichloromethane. The estimated growth rate constants with methanol and dichloromethane under denitrification conditions were 0.04 h^–1 and 0.015 h^–1, respectively, which is twofold and fourfold lower than the rates of aerobic growth with these substrates. Slight accumulation of nitrite was observed in all cultures grown anaerobically with nitrate. Dichloromethane dehalogenase, the key enzyme in the utilization of this carbon source, was induced under denitrification conditions to the same specific activity level as under aerobic conditions. In a fed batch culture under denitrification conditionsHyphomicrobium sp. DM2 cumulatively degraded 35 mM dichloromethane within 24 days. This corresponds to a volumetric degradation rate of 5 mg dichloromethane/l·h and demonstrates that denitrificative degradation offers an attractive possibility for the development of anaerobic treatment systems to remove dichloromethane from contaminated groundwater.     

Degradation pathway of 2-chloroethanol in <Emphasis Type="Italic">Pseudomonas stutzeri</Emphasis> strain JJ under denitrifying conditions

The pathway of 2-chloroethanol degradation in the denitrifying Pseudomonas stutzeri strain JJ was investigated. In cell-free extracts, activities of a phenazine methosulfate (PMS)-dependent chloroethanol dehydrogenase, an NAD-dependent chloroacetaldehyde dehydrogenase, and a chloroacetate dehalogenase were detected. This suggested that the 2-chloroethanol degradation pathway in this denitrifying strain is the same as found in aerobic bacteria that degrade chloroethanol. Activity towards primary alcohols, secondary alcohols, diols, and other chlorinated alcohols could be measured in cell-free extracts with chloroethanol dehydrogenase (CE-DH) activity. PMS and phenazine ethosulfate (PES) were used as primary electron acceptors, but not NAD, NADP or ferricyanide. Cells of strain JJ cultured in a continuous culture under nitrate limitation exhibited chloroethanol dehydrogenase activity that was a 12 times higher than in cells grown in batch culture. However, under chloroethanol-limiting conditions, CE-DH activity was in the same range as in batch culture. Cells grown on ethanol did not exhibit CE-DH activity. Instead, NAD-dependent ethanol dehydrogenase (E-DH) activity and PMS-dependent E-DH activity were detected.     

Biochemical and structural studies of a l-haloacid dehalogenase from the thermophilic archaeon Sulfolobus tokodaii

Haloacid dehalogenases have potential applications in the pharmaceutical and fine chemical industry as well as in the remediation of contaminated land. The l-2-haloacid dehalogenase from the thermophilic archaeon Sulfolobus tokodaii has been cloned and over-expressed in Escherichia coli and successfully purified to homogeneity. Here we report the structure of the recombinant dehalogenase solved by molecular replacement in two different crystal forms. The enzyme is a homodimer with each monomer being composed of a core-domain of a β-sheet bundle surrounded by α-helices and an α-helical sub-domain. This fold is similar to previously solved mesophilic l-haloacid dehalogenase structures. The monoclinic crystal form contains a putative inhibitor l-lactate in the active site. The enzyme displays haloacid dehalogenase activity towards carboxylic acids with the halide attached at the C2 position with the highest activity towards chloropropionic acid. The enzyme is thermostable with maximum activity at 60°C and a half-life of over 1 h at 70°C. The enzyme is relatively stable to solvents with 25% activity lost when incubated for 1 h in 20% v/v DMSO.     

Identification of 4-chlorobenzoyl-coenzyme A as intermediate in the dehalogenation catalysed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3

The intermediate in the reaction catalysed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 was identified as 4-chlorobenzoyl-CoA. One component of 4-chlorobenzoate debalogenase worked as a a 4-chlorobenzoyl-CoA ligase catalysing the formation of 4-chlorobenzoyl-CoA from 4-chlorobenzoate, coenzyme A and ATP. This intermediate was detected spectrophotometrically and by HPLC. 4-chlorobenzoyl-CoA was the substrate for the dehalogenase component, which catalysed the conversion to 4-hydroxybenzoate with concomitant release or coenzyme A.     

Biochemical and molecular characterisation of the 2,3-dichloro-1-propanol dehalogenase and stereospecific haloalkanoic dehalogenases from a versatile <Emphasis Type="Italic">Agrobacterium</Emphasis> sp.

We previously reported the presence of both haloalcohol and haloalkanoate dehalogenase activity in the Agrobacterium sp. strain NHG3. The versatile nature of the organism led us to further characterise the genetic basis of these dehalogenation activities. Cloning and sequencing of the haloalcohol dehalogenase and subsequent analysis suggested that it was part of a highly conserved catabolic gene cluster. Characterisation of the haloalkanoate dehalogenase enzyme revealed the presence of two stereospecific enzymes with a narrow substrate range which acted on d -2-chloropropionic and I-2-chloropropionoic acid, respectively. Cloning and sequencing indicated that the two genes were separated by 87 bp of non-coding DNA and were preceded by a putative transporter gene 66 bp upstream of the d-specific enzyme.     

Enzyme systems for biodegradation of polychlorinated dibenzo-p-dioxins

The angular dioxygenase, cytochrome P450, lignin peroxidase, and dehalogenase are known as dioxin-metabolizing enzymes. All of these enzymes have metal ions in their active centers, and the enzyme systems except for peroxidase have each distinct electron transport chain. Although the enzymatic properties of the angular dioxygenase, lignin peroxidase, and cytochrome P450 have been studied well, the information about dehalogenase is much less than other enzyme systems due to its instability under the aerobic conditions. However, this enzyme system appears to be quite promising from the viewpoint of practical use for bioremediation, because dehalogenases are capable of degradation of polychlorinated dibenzo-p-dioxins (PCDDs) with more than four chlorine substituents, whereas the other three enzyme systems prefer low-chlorinated PCDDs. On the other hand, protein engineering of angular dioxygenase, lignin peroxidase, and cytochrome P450 based on their tertiary structures has great potential to generate highly efficient dioxin-metabolizing enzymes. Actually, we successfully generated 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-metabolizing enzyme by site-directed mutagenesis of cytochrome P450. We hope that recombinant microorganisms harboring genetically engineered dioxin-metabolizing enzymes will be used for bioremediation of soil contaminated with PCDDs and polychlorinated dibenzofurans in the near future.     

Overexpression and feasible purification of thermostable L-2-halo acid dehalogenase ofPseudomonas sp. YL

The gene encoding thermostable L-2-halo acid dehalogenase ofPseudomonas sp. YL was isolated, and its over-expression system was constructed. Gene library was prepared fromSau3AI fragments of total DNA fromPs. sp. YL, pUC118 as a vector andEscherichia coli JM109 as a host. The recombinant cells resistant to bromoacetate, a germicide, were isolated and shown to produce L-2-halo acid dehalogenase. Subsequently, subcloning was carried out with pKK223-3 as a vector, and the length of DNA inserted was reduced to 1.1 kbp. One of the subclones showed very high activity, and the amount of the dehalogenase produced corresponded to about 30% of the soluble protein. From 5 g (wet weight) of cells, 105 mg of dehalogenase was efficiently purified by heat treatment and DEAE-Toyopearl chromatography. This overexpression system provides a large amount of the thermostable enzyme to enable us to study the properties, structure and application of the enzyme.Abbreviations IPTG isopropyl -D-thiogalactopyranoside - KPB potassium phosphate buffer - SDS sodium dodecyl sulfate - X-gal 5-bromo-4-chloro-3-indolyl--D-galactoside     

Metabolism of mono- and dihalogenated C1 and C2 compounds by <Emphasis Type="Italic">Xanthobacter autotrophicus</Emphasis> growing on 1,2-dichloroethane

The conversion of and toxic effects exerted by several mono- and dihalogenated C1 and C2 compounds on cultures of Xanthobacter autotrophicus GJ10 growing on 1,2-dichloroethane were investigated. Bromochloromethane, dibromomethane and 1-bromo-2-chloroethane were utilized by strain GJ10 in batch culture as a cosubstrate and sole carbon source. The rate of degradation of dihalomethanes by whole cells was lower than that of 1,2-dichloroethane, but a significant increase of the rate of dihalomethane biodegradation was observed when methanol or ethanol were added as a cosubstrate. Products of the degradation of several tested compounds by haloalkane dehalogenase were analyzed and a new metabolic pathway based on hydrolytic conversion to formaldehyde was proposed for the dihalomethanes. Strain GJ10 growing on 1,2-dichloroethane converted 2-fluoroethanol and 1-chloro-2-fluoroethane to 2-fluoroacetate, which was tolerated up to a concentration of 2.5 mM. On the basis of the results from batch cultures an inert (dichloromethane), a growth-supporting (dibromomethane) and a toxic (1,2-dibromoethane) compound were selected for testing their effects on a continuous culture of strain GJ10 growing on 1,2-dichloroethane. The compounds were added as pulses to a steady-state chemostat and the response of the culture was followed. The effects varied from a temporary decrease in cell density for dibromomethane to severe toxicity and culture washout with 1,2-dibromoethane. Our results extend the spectrum of halogenated C1 and C2 compounds that are known to be degraded by strain GJ10 and provide information on toxic effects and transformation of compounds not serving as a carbon source for this bacterium.     

Phylogeny of Sphingomonas species that degrade pentachlorophenol

Four pentachlorophenol (PCP)-degrading bacteria isolated from geographically diverse areas have been examined in detail as regards their physiology and phylogeny. According to traditional biochemical methods, these strains had been classified as members of the genera Arthrobacter, Flavobacterium, Pseudomonas, and Sphingomonas. The PCP degradation pathway has been studied extensively in Sphingomonas (Flavobacterium) sp strain ATCC 39723 and the first three degradation steps catalyzed by a PCP-4-monooxygenase (PcpB) and a reductive dehalogenase (PcpC) that functions twice are well established. A fourth step appears to involve ring-fission of the aromatic nucleus (PcpA). Molecular analyses revealed that the PCP degradation pathway in these four strains was rather conserved, leading to a phylogenetic analysis using 16S rDNA. The results revealed a much closer phylogenetic relationship between these organisms than traditional classification indicated, placing them into the more recently established genus Sphingomonas where they may even represent a single species. With 16S rDNA analysis, many bacterial isolates involved in degradation of xenobiotic compounds that were previously classified into diverse genera have been reclassified into the genus Sphingomonas. Received 14 April 1999/ Accepted in revised form 20 July 1999     

Purification and properties of fluoroacetate dehalogenase from <Emphasis Type="Italic">Pseudomonas fluorescens</Emphasis> DSM 8341

The degradation of fluoroacetate by microorganisms has been established for some time, although only a handful of dehalogenases capable of hydrolyzing the stable C–F bond have been studied. Pseudomonas fluorescens DSM 8341 was originally isolated from soil and readily degrades fluoroacetate, thus it was thought that its dehalogenase might have some desirable properties. The enzyme was purified from cell-free extracts and characterised: it is a monomer of 32,500 Da, with a pH optimum of 8 and is stable between pH 4 and 10; its activity is stimulated by some metal ions (Mg²⁺, Mn²⁺ and Fe³⁺), but inhibited by others (Hg²⁺, Ag²⁺). The enzyme is specific for fluoroacetate, and the K _m for this substrate (0.68 mM) is the lowest determined for enzymes of this type that have been investigated to date.     

Cloning and expression of a haloacid dehalogenase fromPseudomonas sp. strain 19 S

A dehalogenase gene specifying the utilization of a variety of haloacids byPseudomonas sp. Strain 19S has been cloned and expressed inE. coli. Our cloning strategy employed specific amplification of a fragment homologous toPseudomonas dehalogenase gene by Polymerase Chain Reaction (PCR). The PCR amplicon successfully acted as a probe to detect the dehalogenase gene in the Southern Blot of the digestedPseudomonas total DNA. Corresponding fragments were cloned into pUC 18 vector and amplified inE. coli MV 1190. One clone with a substantial dehalogenation activity carried a recombinant plasmid containing a 5.5 kb insert.Abbreviations 2-CPA 2-chloropropionate - MCA monochloro acetate - IPTG isopropyl-1-thio--D-galactoside - NBT nitroblue tetrazolium salt - PCR polymerase chain reaction - X-gal 5-bromo-4-chloro-3-indolyl--D-galactoside - X-phosphate 5-bromo-4-chloro-3-indolyl phosphate     

Degradation of 4-chlorobiphenyl and 4-chlorobenzoic acid by the strain <Emphasis Type="Italic">Rhodococcus ruber</Emphasis> P25

The strain Rhodococcus ruber P25 utilizes 4-chlorobiphenyl (4CB) and 4-chlorobenzoic acid (4CBA) as sole carbon and energy sources. 4CB degradation by washed cells of strain P25 was accompanied by transient formation of 4CBA, followed by its utilization and release of equimolar amounts of chloride ions into the medium. The strain R. ruber P25 possessed active enzyme systems providing 4CBA degradation via the stages of formation of intermediates, para-hydroxybenzoate (PHBA) and protocatechuic acid (PCA), to compounds of the basic metabolism. The involvement of protocatechuate 4,5-dioxygenase in 4CBA degradation by rhodococci was revealed. It was established that the initial stage of 4CBA degradation (dehalogenation) in the strain R. ruber P25 was controlled by the fcbA and fcbB genes encoding 4-CBA-CoA ligase and 4-CBA-CoA dehalogenase, respectively. The genes encoding 4CBA dehalogenase components have not been previously detected and characterized in bacteria of the genus Rhodococcus.