Metabolism of dibenzofuran and dibenzo-p-dioxin by the biphenyl dioxygenase of Burkholderia xenovorans LB400 and Comamonas testosteroni B-356

We examined the metabolism of dibenzofuran (DF) and dibenzo-p-dioxin (DD) by the biphenyl dioxygenase (BPDO) of Comamonas testosteroni B-356 and compared it with that of Burkholderia xenovorans LB400. Data showed that both enzymes oxygenated DF at a low rate, but Escherichia coli cells expressing LB400 BPDO degraded DF at higher rate (30 nmol in 18 h) compared with cells expressing B-356 BPDO (2 nmol in 18 h). Furthermore, both BPDOs produced dihydro-dihydroxy-dibenzofuran as a major metabolite, which resulted from the lateral oxygenation of DF. 2,2,3-Trihydroxybiphenyl (resulting from angular oxygenation of DF) was a minor metabolite produced by both enzymes. Deuterated DF was used to demonstrate the production of 2,2,3-dihydroxybiphenyl through angular oxygenation of DF. When tested for their ability to oxygenate DD, both enzymes produced as sole metabolite, 2,2,3-trihydroxybiphenyl ether at about the same rate, indicating similar catalytic properties toward this substrate. Altogether, although LB400 and B-356 BPDOs oxygenate a different range of chlorobiphenyls, their metabolite profiles toward DF and DD are similar. This suggests that co-planarity influences the regiospecificity of BPDO toward DF and DD to a higher extent than the presence of an ortho substituent on the molecule.     

Sequencing of Comamonas testosteroni strain B-356-biphenyl/chlorobiphenyl dioxygenase genes: evolutionary relationships among Gram-negative bacterial biphenyl dioxygenases

In a previous work, all three components of Comamonas testosteroni B-356 biphenyl (BPH)/chlorobiphenyls (PCBs) dioxygenase (dox) have been purified and characterized. They include an iron-sulphur protein (ISP_BPH) which is the terminal oxygenase composed of two subunits (encoded by bphA and bphE), a ferredoxin (FER_BPH) encoded by bphF and a reductase (RED_BPH) encoded by bphG. bphG Is not located in the neighbourhood of bphAEF in B-356. We are reporting the cloning of B-356-bphG and the sequencing of B-356-BPH dox genes. Comparative analysis of the genes provided genetic evidence showing that two BPH dox lineages have emerged in Gram-negative bacteria. The main features of the lineage that includes B-356 are the location of bphG outside the bph gene cluster and the structure of RED_BPH which is very distinct from all other aryl dioxygenase-reductases.     

Purification and characterization of the Comamonas testosteroni B-356 biphenyl dioxygenase components.

In this report, we describe some of the characteristics of the Comamonas testosteroni B-356 biphenyl (BPH)-chlorobiphenyl dioxygenase system, which includes the terminal oxygenase, an iron-sulfur protein (ISPBPH) made up of an alpha subunit (51 kDa) and a beta subunit (22 kDa) encoded by bphA and bphE, respectively; a ferredoxin (FERBPH; 12 kDa) encoded by bphF; and a ferredoxin reductase (REDBPH; 43 kDa) encoded by bphG. ISPBPH subunits were purified from B-356 cells grown on BPH. Since highly purified FERBPH and REDBPH were difficult to obtain from strain B-356, these two components were purified from recombinant Escherichia coli strains by using the His tag purification system. These His-tagged fusion proteins were shown to support BPH 2,3-dioxygenase activity in vitro when added to preparations of ISPBPH in the presence of NADH. FERBPH and REDBPH are thought to pass electrons from NADH to ISPBPH, which then activates molecular oxygen for insertion into the aromatic substrate. The reductase was found to contain approximately 1 mol of flavin adenine dinucleotide per mol of protein and was specific for NADH as an electron donor. The ferredoxin was found to contain a Rieske-type [2Fe-2S] center (epsilon 460, 7,455 M-1 cm-1) which was readily lost from the protein during purification and storage. In the presence of REDBPH and FERBPH, ISPBPH was able to convert BPH into both 2,3-dihydro-2,3-dihydroxybiphenyl and 3,4-dihydro-3,4-dihydroxybiphenyl. The significance of this observation is discussed.     

Metabolism of 2,2'- and 3,3'-dihydroxybiphenyl by the biphenyl catabolic pathway of Comamonas testosteroni B-356

The purpose of this investigation was to examine the capacity of the biphenyl catabolic enzymes of Comamonas testosteroni B-356 to metabolize dihydroxybiphenyls symmetrically substituted on both rings. Data show that 3,3'-dihydroxybiphenyl is by far the preferred substrate for strain B-356. However, the dihydrodiol metabolite is very unstable and readily tautomerizes to a dead-end metabolite or is dehydroxylated by elimination of water. The tautomerization route is the most prominent. Thus, a very small fraction of the substrate is converted to other hydroxylated and acidic metabolites. Although 2,2'-dihydroxybiphenyl is a poor substrate for strain B-356 biphenyl dioxygenase, metabolites were produced by the biphenyl catabolic enzymes, leading to production of 2-hydroxybenzoic acid. Data show that the major route of metabolism involves, as a first step, a direct dehydroxylation of one of the ortho-substituted carbons to yield 2,3,2'-trihydroxybiphenyl. However, other metabolites resulting from hydroxylation of carbons 5 and 6 of 2,2'-dihydroxybiphenyl were also produced, leading to dead-end metabolites.     

Metabolism of hydroxybiphenyl and chloro-hydroxybiphenyl by biphenyl/chlorobiphenyl degradingPseudomonas testosteroni,strain B-356

Summary A biphenyl (BP) and chlorobiphenyl (CBP) metabolizingPseudomonas testosteroni, strain B-356 was also capable of utilizing 2-, 3-, and 4-hydroxybiphenyl. Data presented here suggest that utilization of biphenyl and mono-subtituted biphenyls involves the enzymes of the same pathway. Chloro-hydroxybiphenyls were also metabolized by strain B-356. The unsubstituted ring is first hydroxylated in position 2 and 3 and then cleaved in ameta 1, and 2, position to ultimately generate the benzoic acid derivatives. Since strain B-356 was capable of utilizing benzoic acid and mono-hydroxybenzoic acids, the utilization of biphenyl, 2-, 3-, and 4-hydroxybiphenyl is complete at non-toxic concentrations of the substrates. Chlorobenzoic acids and chloro-hydroxybenzoic acids were not metabolized further by this strain. Studies usingPseudomonas putida, strain KT2440 carrying cloned BP/CBP genes from strain B-356 provided further evidence for the presence of a common pathway for the metabolism of the above compounds inP. testosteroni, strain B-356. Suggestions are made on significance of the broad substrate specificity of the enzymes of biphenyl/chlorobiphenyl pathway in regard to their possible origin and in relation to PCB mixture degradation.     

Biphenyl uptake by psychrotolerant Pseudomonas sp. strain Cam-1 and mesophilic Burkholderia sp. strain LB400

We investigated the uptake of biphenyl by the psychrotolerant, polychlorinated biphenyl (PCB)-degrader, Pseudomonas sp. strain Cam-1 and the mesophilic PCB-degrader, Burkholderia sp. strain LB400. The effects of growth substrates, metabolic inhibitors, and temperature on [14C]biphenyl uptake were studied. Biphenyl uptake by both strains was induced by growth on biphenyl, and was inhibited by dinitrophenol (DNP) and carbonyl cyanide m-chlorophenylhydrazone (CCCP), which are metabolic uncouplers. The Vmax and Km for biphenyl uptake by Cam-1 at 22 degrees C were 5.4 +/- 1.7 nmol x min(-1) x (mg of cell protein)(-1) and 83.1 +/- 15.9 micromol x L(-1), respectively. The Vmax and Km for biphenyl uptake by LB400 at 22 degrees C were 3.2 +/- 0.3 nmol x min(-1) x (mg of cell protein(-1)) and 51.5 +/- 9.6 micromol x L(-1), respectively. At 15 degrees C, the maximum rate for biphenyl uptake by Cam-1 and LB400 was 3.1 +/- 0.3 nmol x min(-1) x (mg of cell protein)(-1) and 0.89 +/- 0.1 nmol x min(-1) x (mg of cell protein)(-1), respectively. Thus, the maximum rate for biphenyl uptake by Cam-1 at 15 degrees C was more than 3 times higher than that for LB400.     

Induction of bphA, encoding biphenyl dioxygenase, in two polychlorinated biphenyl-degrading bacteria, psychrotolerant Pseudomonas strain Cam-1 and mesophilic Burkholderia strain LB400

We investigated induction of biphenyl dioxygenase in the psychrotolerant polychlorinated biphenyl (PCB) degrader Pseudomonas strain Cam-1 and in the mesophilic PCB degrader Burkholderia strain LB400. Using a counterselectable gene replacement vector, we inserted a lacZ-Gm(r) fusion cassette between chromosomal genes encoding the large subunit (bphA) and small subunit (bphE) of biphenyl dioxygenase in Cam-1 and LB400, generating Cam-10 and LB400-1, respectively. Potential inducers of bphA were added to cell suspensions of Cam-10 and LB400-1 incubated at 30 degrees C, and then beta-galactosidase activity was measured. Biphenyl induced beta-galactosidase activity in Cam-10 to a level approximately six times greater than the basal level in cells incubated with pyruvate. In contrast, the beta-galactosidase activities in LB400-1 incubated with biphenyl and in LB400-1 incubated with pyruvate were indistinguishable. At a concentration of 1 mM, most of the 40 potential inducers tested were inhibitory to induction by biphenyl of beta-galactosidase activity in Cam-10. The exceptions were naphthalene, salicylate, 2-chlorobiphenyl, and 4-chlorobiphenyl, which induced beta-galactosidase activity in Cam-10, although at levels that were no more than 30% of the levels induced by biphenyl. After incubation for 24 h at 7 degrees C, biphenyl induced beta-galactosidase activity in Cam-10 to a level approximately four times greater than the basal level in cells incubated with pyruvate. The constitutive level of beta-galactosidase activity in LB400-1 grown at 15 degrees C was approximately five times less than the level in LB400-1 grown at 30 degrees C. Thus, there are substantial differences in the effects of physical and chemical environmental conditions on genetic regulation of PCB degradation in different bacteria.     

Influence of chlorine substituents on rates of oxidation of chlorinated biphenyls by the biphenyl dioxygenase of Burkholderia sp. strain LB400

Biphenyl dioxygenase from Burkholderia (Pseudomonas) sp. strain LB400 catalyzes the first reaction of a pathway for the degradation of biphenyl and a broad range of chlorinated biphenyls (CBs). The effect of chlorine substituents on catalysis was determined by measuring the specific activity of the enzyme with biphenyl and 18 congeners. The catalytic oxygenase component was purified and incubated with individual CBs in the presence of electron transport proteins and cofactors that were required for enzyme activity. The rate of depletion of biphenyl from the assay mixture and the rate of formation of cis-biphenyl 2,3-dihydrodiol, the oxidation product, were almost equal, indicating that the assay accurately measured enzyme-specific activity. Four classes of CBs were defined based on their oxidation rates. Class I contained 3-CB and 2,5-CB, which gave rates that were approximately twice that of biphenyl. Class II contained 2,5,3',4'-CB, 2,3,2',5'-CB, 2,3,4,5-CB, 2,3,2',3'-CB, 2,4, 5,2',5'-CB, 2,5,3'-CB, 2,5,4'-CB, 2-CB, and 3,4,5-CB, which gave rates that ranged from 97 to 35% of the biphenyl rate. Class III contained only 2,3,4,2',5'-CB, which gave a rate that was 4% of the biphenyl rate. Class IV contained 2,4,4'-CB, 2,4,2',4'-CB, 3,4,5, 2'-CB, 3,4,5,3'-CB, 3,5,3',5'-CB, and 3,4,5,2',5'-CB, which showed no detectable depletion. Rates were not significantly correlated with the aqueous solubilities of the CBs or the number of chlorine substituents on the rings. Oxidation products were detected for all class I, II, and III congeners and were identified as chlorinated cis-dihydrodiols for classes I and II. The specificity of biphenyl dioxygenase for the CBs examined in this study was determined by the relative positions of the chlorine substituents on the aromatic rings rather than the number of chlorine substituents on the rings.     

Active site residues of cis-2,3-dihydro-2,3-dihydroxybiphenyl dehydrogenase from Comamonas testosteroni strain B-356

cis-2,3-dihydro-2,3-dihydroxybiphenyl dehydrogenase (BphB) from Comamonas testosteroni strain B-356 is the second enzyme of the biphenyl/polychlorinated biphenyl degradation pathway. Based on the crystal structure of a related BphB, three conserved residues, Ser142, Tyr155, and Lys159, have been suggested to function as a "catalytic triad" as for other members of the short-chain alcohol dehydrogenase/reductase (SDR) family. In this study, substitution of each triad residue was examined in BphB. At pH 9.0, turnover numbers relative to wild-type enzyme were as follows: Y155F, 0.1%; S142A, 1%; and K159A, 10%. Although the Michaelis constants of K159A and S142A for cis-2,3-dihydro-2,3-dihydroxybiphenyl increased about 20-fold, relatively little change was observed in the K(m) for dinucleotide. The K159A mutant, which showed little dehydrogenase activity at pH 7, was sharply activated by increasing the pH, reaching almost 25% of the activity of the wild-type enzyme at pH 9. 8. These three residues are therefore critical for BphB activity, as suggested by the crystal structure and similarity to other SDR family members. In addition, BphB showed a strong preference for NAD(+) over NADP(+), with a 260-fold higher specificity constant (k(cat)/K(m)). Evidence is presented that the inefficient use of NADP(+) by BphB might partly be due to the presence of an aspartate residue at position 36.     

Oxidation of biphenyl by a multicomponent enzyme system from Pseudomonas sp. strain LB400.

Pseudomonas sp. strain LB400 grows on biphenyl as the sole carbon and energy source. This organism also cooxidizes several chlorinated biphenyl congeners. Biphenyl dioxygenase activity in cell extract required addition of NAD(P)H as an electron donor for the conversion of biphenyl to cis-2,3-dihydroxy-2,3-dihydrobiphenyl. Incorporation of both atoms of molecular oxygen into the substrate was shown with 18O2. The nonlinear relationship between enzyme activity and protein concentration suggested that the enzyme is composed of multiple protein components. Ion-exchange chromatography of the cell extract gave three protein fractions that were required together to restore enzymatic activity. Similarities with other multicomponent aromatic hydrocarbon dioxygenases indicated that biphenyl dioxygenase may consist of a flavoprotein and iron-sulfur proteins that constitute a short electron transport chain involved in catalyzing the incorporation of both atoms of molecular oxygen into the aromatic ring.     

Phenotypic and Phylogenetic Characterization of Burkholderia (Pseudomonas) sp. Strain LB400

The relevant phenotypic traits and phylogenetic relationships between Burkholderia (Pseudomonas) sp. strain LB400 and B. cepacia ATCC 25416^T were compared to determine the degree to which these two strains might be related. Strain LB400 degrades chlorinated biphenyls and has been a model system for potential use in the bioremediation of polychlorinated biphenyls, while some strains of B. cepacia are plant and human pathogens. The fatty acid methyl ester profile, sole carbon source utilization, and biochemical tests confirmed that strain LB400 was a member of the genus Burkholderia. The 16S rRNA gene sequence showed that this strain was not as closely related to B. cepacia as previously suspected or to other known pathogens of this genus, but is closely related to B. phenazinium, B. caribensis, B. graminis, and three unnamed Burkholderia spp. not known to be pathogenic. Received: 16 August 2000 / Accepted: 27 September 2000     

Characterization of Comamonas thiooxidans sp. nov., and Comparison of Thiosulfate Oxidation with Comamonas testosteroni and Comamonas composti

Comamonas thiooxidans (strain S23^T) capable of oxidizing thiosulfate under a mixotrophic growth condition was isolated from a sulfur spring. DNA–DNA homology study showed 55% similarity with Comamonas testosteroni KCTC2990^T and 52% with Comamonas composti LMG24008^T, the nearest phylogenetic relative (16S rRNA sequence similarity <97%). Comparative genomic fingerprinting by using ERIC and Rep-PCR further delineated species identity of the strain S23^T for which Comamonas thiooxidans sp. nov. is proposed. In addition, thiosulfate oxidation potential of the strain S23^T was compared with Comamonas testosteroni and Comamonas composti.     

Characterization of active recombinant 2,3-dihydro-2,3-dihydroxybiphenyl dehydrogenase from Comamonas testosteroni B-356 and sequence of the encoding gene (bphB).

2,3-Dihydro-2,3-dihydroxybiphenyl-2,3-dehydrogenase (B2,3D) catalyzes the second step in the biphenyl degradation pathway. The nucleotide sequence of Comamonas testosteroni B-356 bphB, which encodes B2,3D, was determined. Structural analysis showed that the dehydrogenases involved in the bacterial degradation of aromatic compounds are related to each other and that their phylogenetic relationships are very similar to the relationships observed for dioxygenases that catalyze the initial reaction in the degradation pathway. The bphB sequence was used to produce recombinant active His-tagged B2,3D, which allowed us to describe for the first time some of the main features of a B2,3D. This enzyme requires NAD+, its optimal pH is 9.5, and its native M(r) was found to be 123,000, which makes it a tetramer. These characteristics are very similar to those reported for the related enzyme cis-toluene dihydrodiol dehydrogenase. The Km value and maximum rate of metabolism for 2,3-dihydro-2,3-dihydroxybiphenyl were 73 +/- 16 microM and 46 +/- 4 nmol min-1 microgram-1, respectively. Compared with the cis-toluene dihydrodiol dehydrogenase, B2,3D appeared to be more substrate specific since it was unable to attack cis-1,2-dihydroxy-cyclohexa-3,5-diene.     

Dihydroxylation and dechlorination of chlorinated biphenyls by purified biphenyl 2,3-dioxygenase from Pseudomonas sp. strain LB400.

Oxidation of biphenyl and nine chlorinated biphenyls (CBs) by the biphenyl 2,3-dioxygenase from Pseudomonas sp. strain LB400 was examined. The purified terminal oxygenase required the addition of partially purified electron transport components, NAD(P)H, and ferrous iron to oxidize biphenyl and CBs. cis-Biphenyl 2,3-dihydrodiol was produced with biphenyl as the substrate. Dihydrodiols were produced from all CBs, and more than one compound was produced with most substrates. Catechols were produced when the dioxygenase-catalyzed reaction occurred at the 2,3 position of a 2-chlorophenyl ring, resulting in dechlorination of the substrate. Oxidation at the 3,4 position of a 2,5-dichlorophenyl ring produced a 3,4-dihydrodiol. Compounds resulting from both types of reaction were produced during oxidation of 2,5,2'-trichlorobiphenyl. The broad substrate specificity and the ability to oxidize at different ring positions suggest that the biphenyl 2,3-dioxygenase is responsible for the wide range of CBs oxidized by Pseudomonas sp. strain LB400.     

Purification and characterization of the oxygenase component of biphenyl 2,3-dioxygenase from Pseudomonas sp. strain LB400.

The iron-sulfur protein of biphenyl 2,3-dioxygenase (ISPBPH) was purified from Pseudomonas sp. strain LB400. The protein is composed of a 1:1 ratio of a large (alpha) subunit with an estimated molecular weight of 53,300 and a small (beta) subunit with an estimated molecular weight of 27,300. The native molecular weight was 209,000, indicating that the protein adopts an alpha 3 beta 3 native conformation. Measurements of iron and acid-labile sulfide gave 2 mol of each per mol of alpha beta heterodimer. The absorbance spectrum showed peaks at 325 and 450 nm with a broad shoulder at 550 nm. The spectrum was bleached upon reduction of the protein with NADPH in the presence of catalytic amounts of ferredoxinBPH and ferredoxinBPH oxidoreductase. The electron paramagnetic resonance spectrum of the reduced protein showed three signals at gx = 1.74, gy = 1.92, and gz = 2.01. These properties are characteristic of proteins that contain a Rieske-type [2Fe-2S] center. Biphenyl was oxidized to cis-(2R,3S)-dihydroxy-1-phenylcyclohexa-4,6-diene by ISPBPH in the presence of ferredoxinBPH, ferredoxinBPH oxidoreductase, NADPH, and ferrous iron. Naphthalene was also oxidized to a cis-dihydrodiol, but only 3% was converted to product under the same conditions that gave 92% oxidation of biphenyl. Benzene, toluene, 2,5-dichlorotoluene, carbazole, and dibenzothiophene were not oxidized. ISPBPH is proposed to be the terminal oxygenase component of biphenyl 2,3-dioxygenase where substrate binding and oxidation occur via addition of molecular oxygen and two reducing equivalents.     

Identification of the bphA4 gene encoding ferredoxin reductase involved in biphenyl and polychlorinated biphenyl degradation in Pseudomonas sp. strain KKS102.

The nucleotide sequence of the downstream region of the bph operon from Pseudomonas sp. strain KKS102 was determined. Two open reading frames (ORF1 and ORF2) were found in this region, and the deduced amino acid sequence of ORF2 showed homology with the sequences of four ferredoxin reductases of dioxygenase systems. When this region was inserted just upstream of the bph operon, which does not contain a gene encoding ferredoxin reductase, biphenyl dioxygenase activity was detected. The 24- and 44-kDa polypeptides predicted from the two open reading frames were identified by sodium dodecyl sulfate-polyacrylamide gel electrophoresis. Crude extract which contained the products of ORF2 and bphA1A2A3 showed cytochrome c reduction activity. These data clearly suggest that ORF2 encodes ferredoxin reductase. The deduced amino acid sequence of ORF1 does not show significant homology with the sequences of any other proteins in the SWISS-PROT data bank, and the function of ORF1 is unknown.     

Characterization of two biphenyl dioxygenases for biphenyl/PCB degradation in A PCB degrader, Rhodococcus sp. strain RHA1

Rhodococcus sp. RHA1 induces two biphenyl dioxygenases, the BphA and EtbA/EbdA dioxygenases, during growth on biphenyl. Their subunit genes were expressed in R. erythropolis IAM1399 to investigate the involvement of each subunit gene in their activity and their substrate preferences. The recombinant expressing ebdA1A2A3etbA4 and that expressing bphA1A2A3A4 exhibited 4-chlorobiphenyl (4-CB) transformation activity, suggesting that these gene sets are responsible for the EtbA/EbdA and BphA dioxygenases respectively. When bphA4 and etbA4 were swapped to construct the recombinants expressing ebdA1A2A3bphA4 and bphA1A2A3etbA4 respectively, compatibility between BphA4 and EtbA4 was suggested by their 4-CB transformation activities. When bphA3 and ebdA3 were swapped, incompatibility between BphA3 and EbdA3 was suggested. BphA and EtbA/EbdA dioxygenases exhibited the highest transformation activity toward biphenyl and naphthalene respectively, and also attacked dibenzofuran and dibenzo-p-dioxin. The wide substrate preference of EtbA/EbdA dioxygenase suggested that it plays a more important role in polychlorinated biphenyl (PCB) degradation than does BphA dioxygenase.     

Purification and properties of ferredoxinBPH, a component of biphenyl 2,3-dioxygenase of Pseudomonas sp strain LB400

The ferredoxin component (ferredoxin_BPH) of biphenyl 2,3-dioxygenase was purified to homogeneity from crude cell extract of Pseudomonas sp strain LB400 using ion exchange, hydrophobic interaction and gel filtration column chromatography. The protein was a monomer with a molecular weight of 15000 and contained 2 gram-atoms each of iron and acid-labile sulfur. Ultraviolet-visible absorbance spectroscopy showed peaks at 325 nm and 460 nm with a broad shoulder around 575 nm. The spectrum was partially bleached in the visible region upon reduction by reductase_BPH with NADPH as the source of electrons. Electron paramagnetic resonance spectrometry showed no signals for the oxidized protein. Upon reduction with sodium dithionite, signals with g_x = 1.82, g_y = 1.92 and g_z = 2.02 were detected. These results indicate that the protein contains a Rieske-type (2Fe-2S) iron-sulfur center. Ferredoxin_BPH was required for the oxidation of biphenyl by the terminal oxygenase component of the enzyme and is probably involved in the transfer of reducing equivalents from reductase_BPH to the terminal oxygenase during catalysis. Received 01 November 1996/ Accepted in revised form 27 May 1997     

Purification and characterization of the NADH:ferredoxinBPH oxidoreductase component of biphenyl 2,3-dioxygenase from Pseudomonas sp. strain LB400

Mucor circinelloides LU M40 and Penicillium aurantiogriseum P 35 produce extracellular β-glycosidases that are active on the cyanogenic glycoside amygdalin. From the culture broths of M. circinelloides, only one β-glycosidase could be identified, while two different enzymes – both having amygdalase activity – were found in culture broths of P. aurantiogriseum. The study of the mechanism of hydrolysis of the β-bis-glycoside amygdalin with purified enzymes from the two organisms indicated a possible sequential (two-step) reaction. In all cases, the first step of hydrolysis from amygdalin to prunasin was very rapid, while the second step from prunasin to cyanohydrin was much slower. No cyanohydrin lyase activity was found in the culture broths of either fungus. Received: 16 May 1997 / Accepted: 11 September 1997     

Regiospecificity of dioxygenation of di- to pentachlorobiphenyls and their degradation to chlorobenzoates by the bph-encoded catabolic pathway of Burkholderia sp. strain LB400.

Burkholderia sp. strain LB400 is one of the most potent aerobic polychlorobiphenyl (PCB)-degrading microorganisms that have been characterized. Its PCB-dioxygenating activity originates predominantly or exclusively from the biphenyl dioxygenase encoded by its bph gene cluster. Analysis of the dioxygenation products of several di- to pentachlorinated biphenyls formed by this enzyme revealed a complex dependence of the regiospecificity and the yield of dioxygenation on the substitution patterns of both the oxidized and the nonoxidized rings. No dioxygenolytic attack involving chlorinated meta or para carbons was observed. Therefore, the ability of the enzyme to hydroxylate chlorinated carbons appears to be limited to the ortho position. However, it is not limited to monochlorinated rings, as evidenced by dioxygenation of the 2, 4-disubstituted ring at carbons 2 and 3. This site of attack is strikingly different from that of the 2,5-dichlorinated ring, which has been shown to be dihydroxylated at positions 3 and 4 (J. D. Haddock, J. R. Horton, and D. T. Gibson, J. Bacteriol. 177:20-26, 1995). These results demonstrate that a second substituent of ortho-chlorinated rings crucially influences the site of dioxygenation at this ring and thereby determines whether or not the initial chlorobiphenyl oxidation product is further metabolized through the bph-encoded pathway. The 2,4-dichlorinated ring can alternatively be attacked at carbons 5 and 6. The preferred site crucially depends on the substitution pattern of the other ring. The formation of more than a single dioxygenation product was found predominantly with congeners that contain two chlorinated rings, both of which are similarly prone to dioxygenation or one is substituted only at carbon 3.