Two Angular Dioxygenases Contribute to the Metabolic Versatility of Dibenzofuran-Degrading Rhodococcus sp. Strain HA01

ABSTRACT Rhodococcus sp. strain HA01, isolated through its ability to utilize dibenzofuran (DBF) as the sole carbon and energy source, was also capable, albeit with low activity, of transforming dibenzo-p-dioxin (DD). This strain could also transform 3-chlorodibenzofuran (3CDBF), mainly by angular oxygenation at the ether bond-carrying carbon (the angular position) and an adjacent carbon atom, to 4-chlorosalicylate as the end product. Similarly, 2-chlorodibenzofuran (2CDBF) was transformed to 5-chlorosalicylate. However, lateral oxygenation at the 3,4-positions was also observed and yielded the novel product 2-chloro-3,4-dihydro-3,4-dihydroxydibenzofuran. Two gene clusters encoding enzymes for angular oxygenation (dfdA1A2A3A4 and dbfA1A2) were isolated, and expression of both was observed during growth on DBF. Heterologous expression revealed that both oxygenase systems catalyze angular oxygenation of DBF and DD but exhibited complementary substrate specificity with respect to CDBF transformation. While DfdA1A2A3A4 oxygenase, with high similarity to DfdA1A2A3A4 oxygenase from Terrabacter sp. strain YK3, transforms 3CDBF by angular dioxygenation at a rate of 29% ± 4% that of DBF, 2CDBF was not transformed. In contrast, DbfA1A2 oxygenase, with high similarity to the DbfA1A2 oxygenase from Terrabacter sp. strain DBF63, exhibited complementary activity with angular oxygenase activity against 2CDBF but negligible activity against 3CDBF. Thus, Rhodococcus sp. strain HA01 constitutes the first described example of a bacterial strain where coexpression of two angular dioxygenases was observed. Such complementary activity allows for the efficient transformation of chlorinated DBFs.

Cometabolic Degradation of Dibenzofuran and Dibenzothiophene by a Newly Isolated Carbazole-Degrading Sphingomonas sp. Strain

ABSTRACT A carbazole-utilizing bacterium was isolated by enrichment from petroleum-contaminated soil. The isolate, designated Sphingomonas sp. strain XLDN2-5, could utilize carbazole (CA) as the sole source of carbon, nitrogen, and energy. Washed cells of strain XLDN2-5 were shown to be capable of degrading dibenzofuran (DBF) and dibenzothiophene (DBT). Examination of metabolites suggested that XLDN2-5 degraded DBF to 2-hydroxy-6-(2-hydroxyphenyl)-6-oxo-2,4-hexadienic acid and subsequently to salicylic acid through the angular dioxygenation pathway. In contrast to DBF, strain XLDN2-5 could transform DBT through the ring cleavage and sulfoxidation pathways. Sphingomonas sp. strain XLDN2-5 could cometabolically degrade DBF and DBT in the growing system using CA as a substrate. After 40 h of incubation, 90% of DBT was transformed, and CA and DBF were completely removed. These results suggested that strain XLDN2-5 might be useful in the bioremediation of environments contaminated by these compounds.

Plasmid-Borne Genes Code for an Angular Dioxygenase Involved in Dibenzofuran Degradation by Terrabacter sp. Strain YK3

ABSTRACT The genes responsible for angular dioxygenation of dibenzofuran in actinomycetes were cloned by using a degenerate set of PCR primers designed by using conserved sequences of the dioxygenase alpha subunit genes. One sequence of alpha subunit genes was commonly amplified from four dibenzofuran-utilizing actinomycetes: Terrabacter sp. strains YK1 and YK3, Rhodococcus sp. strain YK2, and Microbacterium sp. strain YK18. A 5.2-kb PstI fragment encoding the alpha and beta subunits of the terminal dioxygenase, ferredoxin, and ferredoxin reductase (designated dfdA1 to dfdA4, respectively) was cloned from the large circular plasmid pYK3 isolated from Terrabacter sp. strain YK3. We confirmed that transcription of the dfdA1 gene was induced by dibenzofuran in Terrabacter sp. strain YK3. Southern blot hybridization analysis revealed that this type of dioxygenase gene is distributed among diverse dibenzofuran-utilizing actinomycetes. However, genes homologous to dfdA1 were not detected in dibenzofuran utilization-deficient mutants of Terrabacter, Rhodococcus, and Microbacterium species. When the dfdA1 to dfdA4 genes were introduced into a non-dibenzofuran-degrading mutant of Rhodococcus sp. strain YK2, strain YK2-RD2, which had spontaneously lost the gene homologous to dfdA1, the ability to degrade dibenzofuran was restored. Analysis of the breakdown products indicated that DfdA has angular dioxygenase activity. This dfdA transformant degraded several aromatic compounds, indicating that the novel angular dioxygenase possesses broad substrate specificity.

Degradation of Chlorinated Dibenzofurans and Dibenzo-p-Dioxins by Two Types of Bacteria Having Angular Dioxygenases with Different Features

ABSTRACT Two kinds of bacteria having different-structured angular dioxygenases—a dibenzofuran (DF)-utilizing bacterium,Terrabacter sp. strain DBF63, and a carbazole (CAR)-utilizing bacterium, Pseudomonas sp. strain CA10—were investigated for their ability to degrade some chlorinated dibenzofurans (CDFs) and chlorinated dibenzo-p-dioxins (CDDs) (or, together, CDF/Ds) using either wild-type strains or recombinant Escherichia coli strains. First, it was shown that CAR 1,9a-dioxygenase (CARDO) catalyzed angular dioxygenation of all mono- to triCDF/Ds investigated in this study, but DF 4,4a-dioxygenase (DFDO) did not degrade 2,7-diCDD. Secondly, degradation of CDF/Ds by the sets of three enzymes (angular dioxygenase, extradiol dioxygenase, and meta-cleavage compound hydrolase) was examined, showing that these enzymes in both strains were able to convert 2-CDF to 5-chlorosalicylic acid but not other tested substrates to the corresponding chlorosalicylic acid (CSA) or chlorocatechol (CC). Finally, we tested the potential of both wild-type strains for cooxidation of CDF/Ds and demonstrated that both strains degraded 2-CDF, 2-CDD, and 2,3-diCDD to the corresponding CSA and CC. We investigated the sites for the attack of angular dioxygenases in each CDF/D congener, suggesting the possibility that the angular dioxygenation of 2-CDF, 2-CDD, 2,3-diCDD, and 1,2,3-triCDD (10 ppm each) by both DFDO and CARDO occurred mainly on the nonsubstituted aromatic nuclei.

Diverse Oxygenations Catalyzed by Carbazole 1,9a-Dioxygenase from Pseudomonas sp. Strain CA10

ABSTRACT Carbazole 1,9a-dioxygenase (CARDO) from Pseudomonas sp. strain CA10 is a multicomponent enzyme that catalyzes the angular dioxygenation of carbazole, dibenzofuran, and dibenzo-p-dioxin. It was revealed by gas chromatography-mass spectrometry and 1H and 13C nuclear magnetic resonance analyses that xanthene and phenoxathiin were converted to 2,2′,3-trihydroxydiphenylmethane and 2,2′,3-trihydroxydiphenyl sulfide, respectively. Thus, for xanthene and phenoxathiin, angular dioxygenation by CARDO occurred at the angular position adjacent to the oxygen atom to yield hetero ring-cleaved compounds. In addition to the angular dioxygenation, CARDO catalyzed the cis dihydroxylation of polycyclic aromatic hydrocarbons and biphenyl. Naphthalene and biphenyl were converted by CARDO tocis-1,2-dihydroxy-1,2-dihydronaphthalene andcis-2,3-dihydroxy-2,3-dihydrobiphenyl, respectively. On the other hand, CARDO also catalyzed the monooxygenation of sulfur heteroatoms in dibenzothiophene and of the benzylic methylenic group in fluorene to yield dibenzothiophene-5-oxide and 9-hydroxyfluorene, respectively. These results indicate that CARDO has a broad substrate range and can catalyze diverse oxygenation: angular dioxygenation,cis dihydroxylation, and monooxygenation. The diverse oxygenation catalyzed by CARDO for several aromatic compounds might reflect the differences in the binding of the substrates to the reaction center of CARDO.

Genetic Analysis of Dioxin Dioxygenase ofSphingomonas sp. Strain RW1: Catabolic Genes Dispersed on the Genome

ABSTRACT The dioxin dioxygenase of Sphingomonas sp. strain RW1 activates dibenzo-p-dioxin and dibenzofuran for further metabolism by introducing two atoms of oxygen at a pair of vicinal carbon atoms, one of which is involved in one of the bridges between the two aromatic rings, i.e., an angular dioxygenation. ThedxnA1 and dxnA2 cistrons encoding this dioxygenase have been cloned and shown to be located just upstream of a hydrolase gene which specifies an enzyme involved in the subsequent step of the dibenzofuran biodegradative pathway. Genes encoding the electron supply system of the dioxygenase are not clustered with the dioxygenase gene but rather are located on two other distinct and separate genome segments. Moreover, whereas expression ofdxnA1A2 is modulated according to the available carbon source, expression of the dbfB gene encoding the ring cleavage enzyme of the dibenzofuran pathway, which is located in the neighborhood of dxnA1A2 but oriented in the opposite direction, is constitutive. The scattering of genes for the component proteins of dioxin dioxygenase system around the genome ofSphingomonas sp. strain RW1, and the differential expression of dioxin pathway genes, is unusual and contrasts with the typical genetic organization of catabolic pathways where component cistrons tend to be clustered in multicistronic transcriptional units. The sequences of the α and β subunits of the dioxin dioxygenase exhibit only weak similarity to other three component dioxygenases, but some motifs such as the Fe(II) binding site and the [2Fe-2S] cluster ligands are conserved. Dioxin dioxygenase activity in Escherichia coli cells containing the cloned dxnA1A2 gene was achieved only through coexpression of the cognate electron supply system from RW1. Under these conditions, exclusively angular dioxygenation of dibenzofuran and dibenzo-p-dioxin was obtained. The dioxin dioxygenase was not active in E. colicells coexpressing a class IIB electron supply system. In the course of the isolation of the dxnA1 and dxnA2 cistrons, a number of other catabolic genes dispersed over different genome segments were identified, which may indicate greater catabolic potential than was previously suspected. This finding is consistent with the catabolic versatility of members of the genusSphingomonas, which is becoming increasingly evident, and may indicate a less well evolved and regulated but more dynamic genetic organization in this organism than is the case for better-studied pathways in organisms such as Pseudomonas species.

Isolation and characterization of a 9-fluorenone-degrading bacterial strain and its role in synergistic degradation of fluorene by a consortium

Pseudomonas mendocina MC2, able to use 9-fluorenone but not fluorene as its sole source of carbon and energy, was isolated. Identification of metabolites in growth media and washed cell suspensions indicated that strain MC2 metabolizes 9-fluorenone via angular dioxygenation of the ketone, to give 1,1a-dihydroxy-1-hydro-9-fluorenone, followed by the opening of the five-membered ring and further degradation of the resulting biphenyl derivative by reactions akin to those of biphenyl metabolism, which produce phthalate as an intermediate. The aim of this research was to study the biodegradation of fluorene by a co-culture of strain MC2 and Arthrobacter sp.strain F101, which grows on fluorene and simultaneously transforms a fraction of the substrate to 9-fluorenone, which accumulates as a dead-end product. Growing with 0.1 g fluorene/L, Arthrobacter sp. strain F101 caused the total removal of this compound from the cultures, but when this strain was grown with 1g fluorene/L, only 16% of the fluorene was used. The addition of 9-fluorenone to cultures growing on fluorene showed that 9-fluorenone inhibits fluorene degradation. Finally, when Pseudomonas mendocina MC2 and Arthrobacter sp. strain F101 were co-cultured with 1g fluorene/L as a sole source of carbon and energy, the growth of the strains completely removed fluorene in 2 days. 9-Fluorenone did not accumulate and the carbon assimilation into cell biomass was estimated as approximately 46%. Key words: microbial consortium, fluorene, 9-fluorenone, biodegradation.