Degradation of chlorotoluenes by in vivo constructed hybrid strains: problems of enzyme specificity, induction and prevention of meta-pathway

The activities of the TOL plasmid-coded xylene oxygenase, benzylalcohol dehydrogenase, benzaldehyde dehydrogenase of Pseudomonas putida strain PaW1 were tested with substituted toluenes, benzylalcohols and benzaldehydes, respectively, as substrates. Several chlorinated toluenes were shown to induce enzymes of the xylene degradation sequence. Conjugative transfer of the TOL plasmid from Pseudomonas putida strain PaW1 to Pseudomonas sp. strain B13 and Pseudomonas cepacia strain JH230 allowed the isolation of hybrid strains capable of growing in the presence of 3-chloro-, 4-chloro- and 3,5-dichlorotoluene. Hybrid strains revealed new ways to prevent the dead-end meta-pathway for cholorocatechols.     

Degradation of 2-chlorobenzoate by in vivo constructed hybrid pseudomonads

Abstract 5-Chlorosalicylate degrading bacteria were obtained from the mating between Pseudomonas sp. strain WR401 and Pseudomonas sp. strain B13. Further selection of the hybrid organisms for growth on 2-chlorobenzoate allowed the isolation of strains such as JH230. During growth on 2-chlorobenzoate stoichiometric amounts of chloride were released. Steps in the pathway for 2-chlorobenzoate degradation were determined by simultaneous adaptation studies, assays of enzymes in cell extracts and cooxidation of the analogous substrate 2-methylbenzoate. Results indicate that 2-chlorobenzoate was degraded to 3-chlorocatechol. Ring cleavage of 3-chlorocatechol was by a catechol 1,2-dioxygenase to from 2-chloro- cis, cis - muconate. Further degradation runs via 4-carboxymethylenebut-2-en-4-olide.     

Degradation of chlorophenols by a defined mixed microbial community.

Synthetic sewage containing phenol, acetone, and alkanols plus 4-chlorophenol or a mixture of isomeric chlorophenols is completely degraded by a defined mixed culture with Pseudomonas sp. strain B13 as a chlorocatechol-dissimilating member of the community. Total degradation of the organic carbon was indicated by release of stoichiometric amounts of chloride and low content of dissolved organic carbon in the cell-free effluents. During adaptation to high loads of chlorophenols the initial meta-cleavage activity was completely replaced by ortho-cleavage activity of type I and II. In the fully acclimated culture, hybrid strains such as Alcaligenes sp. strain A7-2 were detected, which are more competitive than Pseudomonas sp. strain B13 with respect to chlorophenol degradation.     

Degradation of chlorophenols by a defined mixed microbial community

Synthetic sewage containing phenol, acetone, and alkanols plus 4-chlorophenol or a mixture of isomeric chlorophenols is completely degraded by a defined mixed culture with Pseudomonas sp. strain B13 as a chlorocatechol-dissimilating member of the community. Total degradation of the organic carbon was indicated by release of stoichiometric amounts of chloride and low content of dissolved organic carbon in the cell-free effluents. During adaptation to high loads of chlorophenols the initial meta-cleavage activity was completely replaced by ortho-cleavage activity of type I and II. In the fully acclimated culture, hybrid strains such as Alcaligenes sp. strain A7-2 were detected, which are more competitive than Pseudomonas sp. strain B13 with respect to chlorophenol degradation.     

Degradation of 3-phenoxybenzoic acid in soil by Pseudomonas pseudoalcaligenes POB310(pPOB) and two modified Pseudomonas strains.

Pseudomonas pseudoalcaligenes POB310(pPOB) and Pseudomonas sp. strains B13-D5(pD30.9) and B13-ST1(pPOB) were introduced into soil microcosms containing 3-phenoxybenzoic acid (3-POB) in order to evaluate and compare bacterial survival, degradation of 3-POB, and transfer of plasmids to a recipient bacterium. Strain POB310 was isolated for its ability to use 3-POB as a growth substrate; degradation is initiated by POB-dioxygenase, an enzyme encoded on pPOB. Strain B13-D5 contains pD30.9, a cloning vector harboring the genes encoding POB-dioxygenase; strain B13-ST1 contains pPOB. Degradation of 3-POB in soil by strain POB310 was incomplete, and bacterial densities decreased even under the most favorable conditions (100 ppm of 3-POB, supplementation with P and N, and soil water-holding capacity of 90%). Strains B13-D5 and B13-ST1 degraded 3-POB (10 to 100 ppm) to concentrations of <50 ppb with concomitant increases in density from 10(6) to 10(8) CFU/g (dry weight) of soil. Thus, in contrast to strain POB310, the modified strains had the following two features that are important for in situ bioremediation: survival in soil and growth concurrent with removal of an environmental contaminant. Strains B13-D5 and B13-ST1 also completely degraded 3-POB when the inoculum was only 30 CFU/g (dry weight) of soil. This suggests that in situ bioremediation may be effected, in some cases, with low densities of introduced bacteria. In pure culture, transfer of pPOB from strains POB310 and B13-ST1 to Pseudomonas sp. strain B13 occurred at frequencies of 5 x 10(-7) and 10(-1) transconjugant per donor, respectively. Transfer of pPOB from strain B13-ST1 to strain B13 was observed in autoclaved soil but not in nonautoclaved soil; formation of transconjugant bacteria was more rapid in soil containing clay and organic matter than in sandy soil. Transfer of pPOB from strain POB310 to strain B13 in soil was never observed.     

Response of a chlorophenols degrading mixed culture to changing loads of phenol,chlorophenol and cresols

Summary A phenol and solvents degrading mixed culture from soil and sludge supplemented with Pseudomonas sp. strain B13 which harbors genes coding the sequence for chlorocatechol breakdown was acclimated to monochlorophenol degradation. Pyrocatechase activity was used as an indicator for the adaptation status of the culture.In the fully acclimated culture, strain B13 was partially replaced by hybrid strains which had acquired the chlorocatechol degrading sequence. This culture degraded changing loads of phenol, chlorophenols and cresols without accumulation of DOC (dissolved organic carbon). When high cresol concentrations were supplied simultaneously with the chlorophenols, strains were enriched which degrade cresols and 3-methylbenzoate via ortho-cleavage pathway.     

Genetic diversity among 3-chloroaniline- and aniline-degrading strains of the Comamonadaceae

We examined the diversity of the plasmids and of the gene tdnQ, involved in the oxidative deamination of aniline, in five bacterial strains that are able to metabolize both aniline and 3-chloroaniline (3-CA). Three strains have been described and identified previously, i.e., Comamonas testosteroni I2 and Delftia acidovorans CA28 and BN3.1. Strains LME1 and B8c were isolated in this study from linuron-treated soil and from a wastewater treatment plant, respectively, and were both identified as D. acidovorans. Both Delftia and Comamonas belong to the family Comamonadaceae. All five strains possess a large plasmid of ca. 100 kb, but the plasmids from only four strains could be transferred to a recipient strain by selection on aniline or 3-CA as a sole source of carbon and/or nitrogen. Plasmid transfer experiments and Southern hybridization revealed that the plasmid of strain I2 was responsible for total aniline but not 3-CA degradation, while the plasmids of strains LME1 and B8c were responsible only for the oxidative deamination of aniline. Several transconjugant clones that had received the plasmid from strain CA28 showed different degradative capacities: all transconjugants could use aniline as a nitrogen source, while only some of the transconjugants could deaminate 3-CA. For all four plasmids, the IS1071 insertion sequence of Tn5271 was found to be located on a 1.4-kb restriction fragment, which also hybridized with the tdnQ probe. This result suggests the involvement of this insertion sequence element in the dissemination of aniline degradation genes in the environment. By use of specific primers for the tdnQ gene from Pseudomonas putida UCC22, the diversity of the PCR-amplified fragments in the five strains was examined by denaturing gradient gel electrophoresis (DGGE). With DGGE, three different clusters of the tdnQ fragment could be distinguished. Sequencing data showed that the tdnQ sequences of I2, LME1, B8c, and CA28 were very closely related, while the tdnQ sequences of BN3.1 and P. putida UCC22 were only about 83% identical to the other sequences. Northern hybridization revealed that the tdnQ gene is transcribed only in the presence of aniline and not when only 3-CA is present.     

Degradation of mixtures of chloroaromatic compounds in soil slurry by mixed cultures of specialized organisms

The degradation of a mixture of 13 chloroaromatics, 2-chloro-, 3-chloro-, 4-chloro- and 3,4-dichloroaniline,2-chloro-, 3-chloro-,4-chloro-, 3,4-dichloro-and 3,5-dichlorobenzoate, and chloro-,1,2-dichloro-, 1,4-dichloro- and 1,2,4-trichlorobenzene in soil slurries by a mixed culture of Pseudomonas acidovorans strain BN 3.1, Pseudomonas ruhlandii strain FRB2, Pseudomonas cepacia strain JH230 and Pseudomonas aeruginosa strain RHO1 was studied. About 70% of the organic bound chlorine was eliminated after 25 days from soil with a carbon content of 8% (soil 1) when 2–3 × 10⁵ cells/g soil of each of the strains were added to the slurries. The effect of the clean-up was demonstrated by a biological test using cress and wheat. Both plants showed good germination and growth on both non-contaminated soils and the contaminated soil 1 after the biotreatment with the strains. No growth was observed when the plants were incubated with the contaminated soil 1 and with the contaminated and biotreated soil 2 (carbon content 2.6%). This indicates that the remaining 30% of organic chlorine in soil 1 after biotreatment does not influence the germination and growth of the two plants tested. *** DIRECT SUPPORT *** AG903062 00010     

The unique aromatic catabolic genes in sphingomonads degrading polycyclic aromatic hydrocarbons (PAHs)

Many members of the sphingomonad genus isolated from different geological areas can degrade a wide variety of polycyclic aromatic hydrocarbons (PAHs) and related compounds. These sphingomonads such as Sphingobium yanoikuyae strain B1, Novosphingobium aromaticivorans strain F199, and Sphingobium sp. strain P2 have been found to possess a unique group of genes for aromatic degradation, which are distantly related with those in pseudomonads and other genera reported so far both in sequence homology and gene organization. Genes for aromatics degradation in these sphingomonads are complexly arranged; the genes necessary for one degradation pathway are scattered through several clusters. These aromatic catabolic gene clusters seem to be conserved among many other sphingomonads such as Sphingobium yanoikuyae strain Q1, Sphingomonas paucimobilis strain TNE12, S. paucimobilis strain EPA505, Sphingobium agrestis strain HV3, and Sphingomonas chungbukensis strain DJ77. Furthermore, some genes for naphthalenesulfonate degradation found in Sphingomonas xenophaga strain BN6 also share a high sequence homology with their homologues found in these sphingomonads. On the other hand, protocatechuic catabolic gene clusters found in fluorene-degrading Sphingomonas sp. strain LB126 appear to be more closely related with those previously found in lignin-degrading S. paucimobilis SYK-6 than the genes in this group of sphingomonads. This review summarizes the information on the distribution of these strains and relationships among their aromatic catabolic genes.     

Degradation of 1,4-dichlorobenzene by enriched and constructed bacteria

Summary Three strains, RHO1, R3 and B1, tentatively identified as a Pseudomonas sp., an Alcaligenes sp. and a Pseudomonas sp. which were able to use 1,4-dichlorobenzene as the sole carbon and energy source were isolated from water of the Rhine river and from the sewage plant at Leverkusen-Bürrig. A hybrid strain, WR1313, which uses chlorobenzene as the growth substrate, was obtained by mating the benzene-growing Pseudomonas putida strain F1 with strain B13, a Pseudomonas sp. degrading chlorocatechols. Further selection of this strain for growth on 1,4-dichlorobenzene allowed the isolation of strain WR1323. During growth on 1,4-dichlorobenzene the strains released stoichiometric amounts of chloride. The affinity of the organisms to 1,4-dichlorobenzene was measured with strain R3 showing a K_s value of 1.2 mg/l. Respiration data and enzyme activities in cell extracts as well as the isolation of 3,6-dichlorocatechol from the culture fluid are consistent with the degradation of 1,4-dichlorobenzene via 3,6-dichlorocatechol, 2,5-dichloro-cis,cis-muconate, 2-chloro-4-carboxymethylenebut-2-en-4-olide.     

Community shifts in a seeded 3-chlorobenzoate degrading membrane biofilm reactor: indications for involvement of in situ horizontal transfer of the clc-element from inoculum to contaminant bacteria

Pseudomonas putida BN210, carrying the self- transferable clc-element encoding degradation of 3-chlorobenzoate on the chromosome, was used as inoculum in different membrane biofilm reactors treating 3-chlorobenzoate-contaminated model wastewater. Analysis of the bacterial population in the effluent and in the biofilm showed the loss of BN210 beyond detection from the reactors and the appearance of several novel 3-chlorobenzoate mineralizing bacteria mainly belonging to the beta-proteobacteria. In contrast, in non-inoculated reactors, no 3-chlorobenzoate degradation was observed and no 3-chlorobenzoate degraders could be recovered. Southern blots hybridization of genomic DNA using clc-element-specific probes and FIGE analysis indicated the presence of the complete clc-element in one or more copies in the isolates. Moreover, the isolates could transfer the clc genes to Ralstonia metallidurans recipients. Two representative reactor isolates, Ralstonia sp. strains KP3 and KP9 demonstrated a higher growth rate on 3-chlorobenzoate than strain BN210 in batch cultures. When BN210, KP3 and KP9 were simultaneously inoculated in a membrane reactor supplied with 3-chlorobenzoate, strain KP3 outcompeted the two other strains and remained the major 3-chlorobenzoate degrading population in the reactor. Our data suggest that in situ horizontal transfer of the clc-element from the inoculum to contaminant bacteria in the reactors was involved in the establishment of novel 3-chlorobenzoate degrading populations that were more competitive under the defined reactor conditions than the inoculum strain.     

Degradation of 3-Phenoxybenzoic Acid in Soil by Pseudomonas pseudoalcaligenes POB310(pPOB) and Two Modified Pseudomonas Strains

Pseudomonas pseudoalcaligenes POB310(pPOB) and Pseudomonas sp. strains B13-D5(pD30.9) and B13-ST1(pPOB) were introduced into soil microcosms containing 3-phenoxybenzoic acid (3-POB) in order to evaluate and compare bacterial survival, degradation of 3-POB, and transfer of plasmids to a recipient bacterium. Strain POB310 was isolated for its ability to use 3-POB as a growth substrate; degradation is initiated by POB-dioxygenase, an enzyme encoded on pPOB. Strain B13-D5 contains pD30.9, a cloning vector harboring the genes encoding POB-dioxygenase; strain B13-ST1 contains pPOB. Degradation of 3-POB in soil by strain POB310 was incomplete, and bacterial densities decreased even under the most favorable conditions (100 ppm of 3-POB, supplementation with P and N, and soil water-holding capacity of 90%). Strains B13-D5 and B13-ST1 degraded 3-POB (10 to 100 ppm) to concentrations of <50 ppb with concomitant increases in density from 10⁶ to 10⁸ CFU/g (dry weight) of soil. Thus, in contrast to strain POB310, the modified strains had the following two features that are important for in situ bioremediation: survival in soil and growth concurrent with removal of an environmental contaminant. Strains B13-D5 and B13-ST1 also completely degraded 3-POB when the inoculum was only 30 CFU/g (dry weight) of soil. This suggests that in situ bioremediation may be effected, in some cases, with low densities of introduced bacteria. In pure culture, transfer of pPOB from strains POB310 and B13-ST1 to Pseudomonas sp. strain B13 occurred at frequencies of 5 × 10⁻⁷ and 10⁻¹ transconjugant per donor, respectively. Transfer of pPOB from strain B13-ST1 to strain B13 was observed in autoclaved soil but not in nonautoclaved soil; formation of transconjugant bacteria was more rapid in soil containing clay and organic matter than in sandy soil. Transfer of pPOB from strain POB310 to strain B13 in soil was never observed.     

The nature of the cellulose-binding domain effects the activities of a bacterial endoglucanase on different forms of cellulose

Abstract The hybrid Pseudomonas cepacia strain JHR22 was tested for its ability to degrade Aroclor 1221 in soil. The influence of supplements—mineral salts and trace elements—on the degradation was investigated. Disapperance of Aroclor 1221 congeners, occurence of metabolites, and release of chloride were measured under different conditions. After 45 days the hybrid organism, strain JHR22, was still present at high numbers in soil, independently of whether the soil had been sterilized prior to inoculation or not. There was only a minor difference in degradation efficiency between sterilized and untreated soil with about 70% release of chloride when 10⁷ cells/g soil were inoculated. The whole hybrid pathway, originating from three different strains, was found to be stable under the conditions tested. Mineral salts did not significantly affect the degradation rate or survival of the hybrid strain.     

黄曲霉毒素B1降解菌的分离鉴定及其降解特性

【目的】黄曲霉毒素是一类强毒、致癌的真菌次级代谢产物。本文旨在筛选出能高效降解黄曲霉毒素B1(AFB1)的细菌。【方法】以AFB1结构类似物香豆素为惟一碳源进行AFB1降解菌株初筛,得到的活性菌株的培养液分别与AFB1标准品(2.5μg/mL)共同作用,以AFB1降解率为指标进行复筛。对降解活性最好的菌株通过形态、生理生化特性以及16S rRNA序列分析进行初步鉴定;并对细胞浓度、pH、温度、金属离子等对菌株降解活性的影响进行考察。【结果】初筛获得了10株在香豆素培养基上生长良好的细菌,复筛发现这些菌均具有良好的AFB1降解活性,其中从金毛羚牛粪便中筛选出的菌株F4降解活性最好,去除AFB1能力达到90.03%。根据F4菌株16S rRNA序列同源性分析,结合形态、生理生化特性,初步确定菌株F4为施氏假单胞菌(Pseudomonas stutzeri)。F4的降解活性与细胞浓度呈正相关。当pH 7.0,35℃,菌细胞作用72 h后毒素降解率达到82.91%。Mg2+可增强F4的降解活性,降解率提高7.68%,而Cu2+可抑制其降解活性,降解率降低51.1%。【结论】筛选到能高效降解AFB1的施氏假单胞菌(Pseudomonas stutzeri)F4,F4降解毒素的活性物质主要存在于菌体细胞,其作用受到温度、pH等的影响,可能是一种胞内酶。     

Genetic Diversity among 3-Chloroaniline- and Aniline-Degrading Strains of the Comamonadaceae

We examined the diversity of the plasmids and of the gene tdnQ, involved in the oxidative deamination of aniline, in five bacterial strains that are able to metabolize both aniline and 3-chloroaniline (3-CA). Three strains have been described and identified previously, i.e., Comamonas testosteroni I2 and Delftia acidovorans CA28 and BN3.1. Strains LME1 and B8c were isolated in this study from linuron-treated soil and from a wastewater treatment plant, respectively, and were both identified as D. acidovorans. Both Delftia and Comamonas belong to the family Comamonadaceae. All five strains possess a large plasmid of ca. 100 kb, but the plasmids from only four strains could be transferred to a recipient strain by selection on aniline or 3-CA as a sole source of carbon and/or nitrogen. Plasmid transfer experiments and Southern hybridization revealed that the plasmid of strain I2 was responsible for total aniline but not 3-CA degradation, while the plasmids of strains LME1 and B8c were responsible only for the oxidative deamination of aniline. Several transconjugant clones that had received the plasmid from strain CA28 showed different degradative capacities: all transconjugants could use aniline as a nitrogen source, while only some of the transconjugants could deaminate 3-CA. For all four plasmids, the IS1071 insertion sequence of Tn5271 was found to be located on a 1.4-kb restriction fragment, which also hybridized with the tdnQ probe. This result suggests the involvement of this insertion sequence element in the dissemination of aniline degradation genes in the environment. By use of specific primers for the tdnQ gene from Pseudomonas putida UCC22, the diversity of the PCR-amplified fragments in the five strains was examined by denaturing gradient gel electrophoresis (DGGE). With DGGE, three different clusters of the tdnQ fragment could be distinguished. Sequencing data showed that the tdnQ sequences of I2, LME1, B8c, and CA28 were very closely related, while the tdnQ sequences of BN3.1 and P. putida UCC22 were only about 83% identical to the other sequences. Northern hybridization revealed that the tdnQ gene is transcribed only in the presence of aniline and not when only 3-CA is present.     

Microbial metabolism of chloroanilines: enhanced evolution by natural genetic exchange

2-, 3-, and 4-chloroaniline degrading bacteria were obtained by natural genetic exchange between an aniline or toluidine degrading Pseudomonas strain and the chlorocatechol assimilating Pseudomonas sp. B13. Hybrid organisms were isolated through cocultivation of the parent strains in the chemostat as well as through conjugation on solid media in presence of chloroanilines as the selective substrates. Biochemical analysis of the gene products in the hybrid strains clearly showed that the genes coding for the aniline dioxygenase or the genes for the chlorocatechol assimilatory sequence had been transferred.     

Degradation of substituted naphthalenesulfonic acids by Sphingomonas xenophaga BN6

Sphingomonas xenophaga BN6 was isolated from the river Elbe as a member of a multispecies bacterial culture which mineralized 6-aminonaphthalene-2-sulfonate. Pure cultures of strain BN6 converted a wide range of amino- and hydroxynaphthalene-2-sulfonates via a catabolic pathway similar to that described for the metabolism of naphthalene to salicylate by Pseudomonas putida NAH7 or Pseudomonas sp NCIB 9816. In contrast to the naphthalene-degrading pseudomonads, S. xenophaga BN6 only partially degraded the naphthalenesulfonates and excreted the resulting amino- and hydroxysalicylates in almost stoichiometric amounts. Enzymes that take part in the degradative pathway of the naphthalenesulfonates by strain BN6 were purified, characterized and compared with the isofunctional enzymes from the naphthalene-degrading pseudomonads. According to the enzyme structures and the catalytic constants, no fundamental differences were found between the 1,2-dihydroxynaphthalene dioxygenase or the 2′-hydroxybenzalpyruvate aldolase from strain BN6 and the isofunctional enzymes from the naphthalene-degrading pseudomonads. The limited available sequence information about the enzymes from strain BN6 suggests that they show about 40–60% sequence identity to the isofunctional enzymes from the pseudomonads. In addition to the gene for the 1,2-dihydroxynaphthalene dioxygenase, the genes for two other extradiol dioxygenases were cloned and sequenced from strain BN6 and the corresponding gene products were studied. S. xenophaga BN6 has also been used as a model organism to study the mechanism of the non-specific reduction of azo dyes under anaerobic conditions and to establish combined anaerobic/aerobic treatment systems for the degradation of sulfonated azo dyes. Furthermore, the degradation of substituted naphthalenesulfonates by mixed cultures containing strain BN6 was studied in continuous cultures and was described by mathematical models. Received 02 April 1999/ Accepted in revised form 09 July 1999     

Phytase activity in some groups of bacteria. Search for and cloning of genes for bacterial phytases

A search for phytase genes in 9 Bacillus strains from the collection of IMGAN was implemented. The growth optimum of strains IX-22, IX-12B, K17-2, K18, IMG I, IMG II, M4 and M8 was 50-60 degrees C; the optimal growth temperature for Bacillus sp. 790 was 45-47 degrees C. According to the sequence data of 16S RNA genes, Bacillus sp. 790 belongs to the B. subtilis/amyloliquefaciens group. The other 8 strains were identified as B. licheniformis. Selection of Bacillus strains, potentially containing the phytase genes, was performed via PCR with primers designed on the basis of the conserved sequence regions of the phyA gene from B. amyloliquefaciens FZB45 with chromosomal DNA being used as the template. The nucleotide sequences of all PCR fragments showed a high level of homology to the known Bacillus phytase genes. The gene libraries of B. licheniformis M8 and B. amyloliquefaciens 790 in E. coli were constructed and phytase-containing clones were selected from them. Twenty-four Pseudomonas strains of different species, 5 Xanthomonas maltophilia strains and 1 Xanthomonas malvacearum (all from the mentioned collection) were tested for phytase activity. Such activity was found in 13 Pseudomonas strains and in 6 Xanthomonas strains. The accumulation of phytase in Pseudomonas was shown to take place at later (over 2 days') growth stages. The optimum pH for phytase from 3 Pseudomonas strains were established. The enzymes were found to be most active at pH 5.5.     

Effect of rhamnolipids on degradation of anthracene by two newly isolated strains, Sphingomonas sp. 12A and Pseudomonas sp. 12B

Anthracene is a PAH that is not readily degraded, plus its degradation mechanism is still not clear. Thus, two strains of bacteria-degrading bacteria were isolated from longterm petroleum-polluted soil and identified as Sphingomonas sp. 12A and Pseudomonas sp. 12B by a 16S rRNA sequence analysis. To further enhance the anthracene-degrading ability of the two strains, the biosurfactants produced by Pseudomonas aeruginosa W3 were used, which were characterized as rhamnolipids. It was found that these rhamnolipids dramatically increased the solubility of anthracene, and a reverse-phase HPLC assay showed that the anthracene degradation percentage after 18 days with Pseudomonas sp. 12B was significantly enhanced from 34% to 52%. Interestingly, their effect on the degradation by Sphingomonas sp. 12A was much less, from 35% to 39%. Further study revealed that Sphingomonas sp. 12A also degraded the rhamnolipids, which may have hampered the effect of the rhamnolipids on the anthracene degradation.     

Purification and characterization of a 1,2-dihydroxynaphthalene dioxygenase from a bacterium that degrades naphthalenesulfonic acids.

1,2-Dihydroxynaphthalene dioxygenase was purified to homogeneity from a bacterium that degrades naphthalenesulfonic acids (strain BN6). The enzyme requires Fe2+ for maximal activity and consists of eight identical subunits with a molecular weight of about 33,000. Analysis of the NH2-terminal amino acid sequence revealed a high degree of homology (22 of 29 amino acids) with the NH2-terminal amino acid sequence of 2,3-dihydroxybiphenyl dioxygenase from strain Pseudomonas paucimobilis Q1. 1,2-Dihydroxynaphthalene dioxygenase from strain BN6 shows a wide substrate specificity and also cleaves 5-, 6-, and 7-hydroxy-1,2-dihydroxynaphthalene, 2,3- and 3,4-dihydroxybiphenyl, catechol, and 3-methyl- and 4-methylcatechol. Similar activities against the hydroxy-1,2-dihydroxynaphthalenes were also found in cell extracts from naphthalene-degrading bacteria.