Carbazole Degradation Research Articles

Degradation of carbazole, dibenzothiophene, and dibenzofuran at low temperature by Pseudomonas sp. strain C3211

Pseudomonas sp. strain C3211 was isolated from a temperate climate soil contaminated with creosote. This strain was able to degrade carbazole, dibenzothiophene and dibenzofuran at 10 degrees C with acetone as a co-substrate. When dibenzothiophene was degraded by strain C3211, an orange compound, which absorbed at 472 nm, accumulated in the medium. Degradation of dibenzofuran was followed by accumulation of a yellowish compound, absorbing at 462 nm. The temperature optimum of strain C3211 for degradation of dibenzothiophene and dibenzofuran was at 20 to 21 degrees C, while the maximum temperature for degradation was at 27 degrees C. Both compounds were degraded at 4 degrees C. Degradation at 10 degrees C was faster than degradation at 25 degrees C. This indicates that strain C3211 is adapted to life at low temperatures.

Crystal structure of a histidine-tagged serine hydrolase involved in the carbazole degradation (CarC enzyme)

2-Hydroxy-6-oxo-6-(2 ′-aminophenyl)-hexa-2,4-dienoate hydrolases (CarC enzymes) from two carbazole-degrading bacteria were purified using recombinant Escherichia coli strains with the histidine (His)-tagged purification system. The His-tagged CarC (ht-CarC) enzymes from Pseudomonas resinovorans strain CA10 (ht-CarC CA10) and Janthinobacterium sp. strain J3 (ht-CarC J3) exhibited hydrolase activity toward 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoate as the purified native CarC CA10 did. ht-CarC J3 was crystallized in the space group I422 with cell dimensions of a= b=130.3 Å, c=84.5 Å in the hexagonal setting, and the crystal structure of ht-CarC J3 was determined at 1.86 Å resolution. The final refined model of ht-CarC J3 yields an R-factor of 21.6%, although the electron-density corresponding to Ile146 to Asn155 was ambiguous in the final model. We compared the known structures of BphD from Rhodococcus sp. strain RHA1 and CumD from Pseudomonas fluorescens strain IP01. The backbone conformation of ht-CarC J3 was better superimposed with CumD than with BphD RHA1. The side-chain directions of Arg185 and Trp262 residues in the substrate binding pockets of these enzymes were different among these proteins, suggesting that these residues may take a conformational change during the catalytic cycles.

Purification and properties of 2-hydroxy-6-oxo-6-(2 ′-aminophenyl)hexa-2,4-dienoic acid hydrolase involved in microbial degradation of carbazole

Hydrolysis following meta-ring cleavage by a dioxygenase is a well-known step in aromatic compound metabolism. The 2-hydroxy-6-oxo-6-(2 ′-aminophenyl)hexa-2,4-dienoic acid hydrolase from Pseudomonas LD2 is a new member of the small group of characterized aromatic hydrolases that catalyze the cleavage of C–C bonds. In this study, the His 6-tagged 2-hydroxy-6-oxo-6-(2 ′-aminophenyl)hexa-2,4-dienoic acid (HOPDA) hydrolase was purified from a recombinant Escherichia coli strain utilizing immobilized metal affinity chromatography. 2-Hydroxy-6-oxo-6-(2 ′-aminophenyl)hexa-2,4-dienoic acid hydrolase is a colorless homodimer with no cofactor requirement. The enzyme actively converted HOPDA into benzoic acid and 2-hydroxypenta-2,4-dienoic acid. The enzyme exhibited activity between pH 6.5 and 10.5 with a maximum activity at pH 7.0. The optimum temperature at pH 7.0 was 60 °C. The calculated K ′ m for HOPDA was 4.6 μM, the V max was 3.3 μmol min −1, and the K s was 70.0 μM. This corresponds to a maximum specific turnover rate of 1300 HOPDA s −1 dimer −1 . The deduced amino acid sequence of CarC showed 30.3, 31.3, and 31.8% identity with TodF ( P. putida F1), XylF ( P. putida), and DmpD ( Pseudomonas sp. CF600), respectively, which are meta-cleavage compound hydrolases from other Pseudomonads. The amino acid sequence Gly–X–Ser–X–Gly, which is highly conserved in these hydrolases, is also found in CarC. Lysates from a strain expressing enzyme in which the putative active site serine is mutated to alanine showed a significant reduction in activity.

Expression, purification, and characterization of 2'-aminobiphenyl-2,3-diol 1,2-dioxygenase from carbazole-degrader Pseudomonas resinovorans strain CA10.

The two-subunit meta-cleavage enzyme, 2'-aminobiphenyl-2,3-diol 1,2-dioxygenase (CarBaBb), from the carbazole degrader Pseudomonas resinovorans strain CA10 was purified to homogeneity from an Escherichia coli strain carrying the expression vector pUCA503, in which two copies of the carBaBb genes are tandemly linked. SDS-PAGE and gel filtration showed that CarB was a alpha2beta2-heterotetrameric enzyme with subunit molecular masses of approximately 10,000 for CarBa and 29,000 for CarBb. The optimum pH for activity was 8.5 and that of temperature was 35 degrees C. The CarB enzyme had a Km of 14 microM and a kcat/Km of 0.25 microM(-1) s(-1) for 2'-aminobiphenyl-2,3-diol, and the catalytic activities for biphenyl-type catecholic substrates were higher than those for monoaromatic catechol derivatives. The enzyme was originally isolated as a meta-cleavage enzyme for 2'-aminobiphenyl-2,3-diol involved in carbazole degradation, but the enzyme was highly specific for 2,3-dihydroxybiphenyl.

Purification and Characterization ofmeta-Cleavage Compound Hydrolase from a Carbazole DegraderPseudomonas resinovoransStrain CA10

2-Hydroxy-6-oxo-6-(2'-aminophenyl)-hexa-2,4dienoic acid [6-(2'-aminophenyl)-HODA] hydrolase, involved in carbazole degradation by Pseudomonas resinovorans strain CA10, was purified to near homogeneity from an overexpressing Escherichia coli strain. The enzyme was dimeric, and its optimum pH was 7.0-7.5. Phylogenetic analysis showed the close relationship of this enzyme to other hydrolases involved in the degradation of monocyclic aromatic compounds, and this enzyme was specific for 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid (6-phenyl-HODA), having little activity toward 2-hydroxy-6-oxohepta-2,4-dienoic acid and 2-hydroxymuconic semialdehyde. The enzyme had a Km of 2.51 microM and k(cat) of 2.14 (s(-1)) for 6-phenyl-HODA (50 mM sodium phosphate, pH 7.5, 25 degrees C). The effect of the presence of an amino group or hydroxyl group at the 2'-position of phenyl moiety of 6-phenyl-HODA on the enzyme activity was found to be small; the activity decreased only in the order of 6-(2'-aminophenyl)-HODA (2.44 U/mg) > 6-phenyl-HODA (1.99 U / mg) > 2-hydroxy-6-oxo-6-(2'-hydroxyphenyl)-hexa-2,4-dienoic acid (1.05 U/mg). The effects of 2'-substitution on the activity were in accordance with the predicted reactivity based on the calculated lowest unoccupied molecular orbital energy for these substrates.

Evaluation of carbazole degradation by Pseudomonas rhodesiae strain KK1 isolated from soil contaminated with coal tar.

In this study, strain KK1 isolated from coal tar-contaminated soil was found to be able to mineralize carbazole as a sole source of carbon by radiorespirometric analysis. KK1 cells pregrown on phenanthrene were able to mineralize carbazole much more rapidly than cells pregrown on naphthalene, suggesting a possible close linkage between the pathways for carbazole and phenanthrene catabolism. Also, Rieske-type iron sulfur center sequence of dioxygenase from KK1 was analyzed to evaluate carbazole catabolism by KK1. A gene cloned out from KK1 using a universal dioxygenase primer set was found a dioxygenase for initial catabolism of carbazole based on deduced amino acid sequences. Northern hybridization using the putative carbazole dixoygenase gene fragment as a probe provided the information that catabolism of carbazole might be greatly activated in phenanthrene-grown cells. Analysis of PLFAs extracted from KK1 cells exposed to carbazole revealed that lipids 10:0 3OH, 17:0 cyclo, and 18:0 were representatives produced or significantly increased in response to carbazole. Strain KK1 was identified as Pseudomonas species with 94% confidence when BIOLOG system was applied, as Pseudomonas sp. with over 90% confidence by total cellular compositions of fatty acid, and as Pseudomonas rhodesiae with 99% confidence by 16S rRNA sequence. Accordingly, strain KK1 was identified as Pseudomonas rhodesiae based on combination of the data, and designated Pseudomonas rhodesiae KK1. The phylogenetic tree based on 16S rRNA suggested that strain KK1 was far away in the phylogenetic distance from the strains that can degrade carbazole.

Isolation and characterization of Sphingomonas sp. GTIN11 capable of carbazole metabolism in petroleum

A bacterial culture was isolated from a manufactured gas plant (MGP) soil based on its ability to metabolize the nitrogen-containing heterocycle carbazole. The culture was identified as a Sphingomonas sp. and was given the designation GTIN11. A cloned 4.2 kb DNA fragment was confirmed to contain genes responsible for carbazole degradation. DNA sequence analysis revealed that the fragment contained five open reading frames (ORFs) with the deduced amino acid sequence showing homology to; carbazole terminal dioxygenase (ORF1), 2,3-dihydroxybiphenyl dioxygenase subunits (ORF2 and ORF3), meta-cleavage compound hydrolases (ORF4), and ferrodoxin component of bacterial multicomponent dioxygenases (ORF5). The percent similarity was 61% of these proteins or less to known proteins. The specific activity of Sphingomonas sp. GTIN11 for the degradation of carbazole at 37 °C was determined to be 8.0 μ mol carbazole degraded/min/g dry cell. This strain is unique in expressing the carbazole degradation trait constitutively. Resting cells of Sphingomonas sp. GTIN11 removed 95% of carbazole and 50% of C1-carbazoles from petroleum in a 16-h treatment time.

Enhanced degradation of carbazole and 2,3-dichlorodibenzo-p-dioxin in soils by Pseudomonas resinovorans strain CA10.

We studied the degradation of carbazole (CAR) and 2,3-dichlorodibenzo-p-dioxin (2,3-DCDD) in soils inoculated with carbazole- and dioxin-degrader Pseudomonas resinovorans strain CA10. By using Tn5-based transposon delivery systems, this bacterium was chromosomally marked with a tandem green fluorescent protein (gfp) gene. Real-time competitive PCR and direct counting using the (gfp) marker were employed to monitor the total number of carbazole 1,9a-dioxygenase gene (carAa) and survival of CA10 cells in the soil and soil slurry microcosms. Bioaugmentation studies indicated that the survival of the marked CA10 cells in soil microcosms was strongly influenced by pH and organic matter. While the number of the marked CA10 cells decreased rapidly in pH 6 with low organic matter, a high cell density was maintained in pH 7.3 with 2.5% organic matters up to 21 days after inoculation. In pH 7.3 soil, the period needed for complete degradation of CAR (100 microg kg(-1)) was markedly shortened from 21 to 7 days by the inoculation with the CA10 cells. Single inoculation of CA10 cells into the soil slurry system of 2,3-DCDD-contaminated soil enhanced the degradation of 2,3-DCDD from 25.0% to 37.0%. In this system, the population density of CA10 cells and the total number of carAa gene were maintained up to 14 days after inoculation. By repeated inoculation (every 2 days) with CA10 cells each at a density of 10(9) CFU g(-1) of soil, almost all of the 2,3-DCDD (1 microg kg(-1)) was degraded within 14 days. Results of these experiments suggest that P. resinovorans strain CA10 may be an important resource for bioremediation of CAR and chlorinated dibenzo-p-dioxin in contaminated soils.

Inhibition of p-cresol on aerobic biodegradation of carbazole, and sodium salicylate by Pseudomonas putida

A PAH- and phenol-degrading microorganism, Pseudomonas putida (ATCC 17484), was used to study the substrate interactions during cell growth on carbazole-containing mixtures with p-cresol and sodium salicylate. Both p-cresol and sodium salicylate could be utilised by the bacteria as the sole carbon and energy sources. When cells grew on the mixture of carbazole, p-cresol and sodium salicylate, strong substrate interactions were observed. Carbazole degradation started only after p-cresol was significantly or completely removed, and the removal of carbazole was incomplete when the initial p-cresol concentration was higher than 20 mg/l. No carbazole was removed at all when the initial p-cresol concentration in the system was higher than 120 mg/l. When cells grew on the ternary substrates, the specific growth rate was found to increase with p-cresol concentration up to 50 mg/l (from 0.33 to 0.45 h −1) but decreased monotonically with higher concentrations. At 120 mg/l p-cresol, specific growth rate fell to 0.33 h −1. The inhibitory effect of p-cresol was demonstrated where carbazole degradation was immediately halted when 50 mg/l p-cresol was spiked to a system containing carbazole and sodium salicylate. Besides, the addition of p-cresol was also found to inhibit the degradation of sodium salicylate. With p-cresol, an increase in lag time was observed and the utilisation of sodium salicylate as carbon source was severely retarded.

Recycle use of Sphingomonas sp. CDH-7 cells for continuous degradation of carbazole in the presence of MgCl2.

Carbazole (CA) is a heterocyclic nitrogen compound contained in the crude petroleum oil and recalcitrant to removal through the refinery processes. For development of the efficient CA-degradation bioprocess, conditions for the recycle use of Sphingomonas sp. CDH-7 resting cells were examined. When the resting cells (O.D.(660) 3.3) were shaken in 50 m M K2HPO4-KH2PO4 buffer (pH 7.0) containing CA 1000 mg/L, CA 880 mg/L was degraded within 3 h, but thereafter the activity decreased markedly. However, the activity was found to be restored to the initial level after the shaking treatment for 3 h in CA-free medium solution or in the buffer containing 20 m M MgCl2. Although the CA-degradation activity of CDH-7 resting cells was lost after 3 h of shaking in the buffer containing 100 m M EDTA, it was restored through the shaking treatment for 3 h in the buffer containing 20 m M MgCl2. When CA was periodically added eight times at a concentration of 100 mg/L (0.599 m M) to the reaction mixture containing the resting cells, CA 778 mg/L (4.66 m M) was continuously degraded within 35 h by the recycle use of resting cells, with the restoration treatment after each CA-degradation reaction by the resting cells.

Organization and transcriptional characterization of catechol degradation genes involved in carbazole degradation by Pseudomonas resinovorans strain CA10.

Pseudomonas resinovorans strain CA10 assimilates catechol, which is an intermediate of carbazole degradation, by ortho cleavage pathway enzymes encoded by the catR, catBCA operon. Cat proteins of strain CA10 were very similar to those of P. putida, although the relatedness in non-coding regions was not high. It was found that catBCA genes were induced in carbazole-grown cells as a single transcriptional unit.

Genetic characterization and evolutionary implications of a car gene cluster in the carbazole degrader Pseudomonas sp. strain CA10.

The nucleotide sequences of the 27,939-bp-long upstream and 9,448-bp-long downstream regions of the carAaAaBaBbCAc(ORF7)Ad genes of carbazole-degrading Pseudomonas sp. strain CA10 were determined. Thirty-two open reading frames (ORFs) were identified, and the car gene cluster was consequently revealed to consist of 10 genes (carAaAaBaBbCAcAdDFE) encoding the enzymes for the three-step conversion of carbazole to anthranilate and the degradation of 2-hydroxypenta-2,4-dienoate. The high identities (68 to 83%) with the enzymes involved in 3-(3-hydroxyphenyl)propionic acid degradation were observed only for CarFE. This observation, together with the fact that two ORFs are inserted between carD and carFE, makes it quite likely that the carFE genes were recruited from another locus. In the 21-kb region upstream from carAa, aromatic-ring-hydroxylating dioxygenase genes (ORF26, ORF27, and ORF28) were found. Inductive expression in carbazole-grown cells and the results of homology searching indicate that these genes encode the anthranilate 1,2-dioxygenase involved in carbazole degradation. Therefore, these ORFs were designated antABC. Four homologous insertion sequences, IS5car1 to IS5car4, were identified in the neighboring regions of car and ant genes. IS5car2 and IS5car3 constituted the putative composite transposon containing antABC. One-ended transposition of IS5car2 together with the 5' portion of antA into the region immediately upstream of carAa had resulted in the formation of IS5car1 and ORF9. In addition to the insertion sequence-dependent recombination, gene duplications and presumed gene fusion were observed. In conclusion, through the above gene rearrangement, the novel genetic structure of the car gene cluster has been constructed. In addition, it was also revealed that the car and ant gene clusters are located on the megaplasmid pCAR1.

Kinetics of carbazole degradation by Pseudomonas putida in presence of sodium salicylate

The feasibility of a PAH- and phenol-degrading microorganism ( Pseudomonas putida ATCC 17484) to degrade carbazole was investigated. While the culture could not utilize carbazole as a sole carbon and energy source, carbazole could be completely degraded in the presence of 200 mg/l sodium salicylate. It was found that there was a trace accumulation of autopolymerization products resulting from the degradation of sodium salicylate at the end of the experiments. Based on mass-spectrometric analysis, the identities of these products were proposed as a dimer of catechol and its derivative. Cell growth and degradation kinetics models were developed and experimentally validated over a wide range of concentrations of sodium salicylate (50–600 mg/l) and carbazole (0.5–4.5 mg/l). Cells grew on sodium salicylate based on Haldane kinetics with parameters of μ m1=0.520 h −1, K S1=36.2 mg/l and K I1=1201.7 mg/l, while carbazole exerted toxicity inhibition to growth. When both carbazole and sodium salicylate were present, ATCC 17484 utilized them simultaneously but with lower specific rates. Model analysis indicates that carbazole inhibited sodium salicylate degradation more than the self-inhibition of sodium salicylate.

Biodegradation of carbazole byRalstoniasp. RJGII.123 isolated from a hydrocarbon contaminated soil

The use of microorganisms for bioremediation of contaminated soils may be enhanced with an understanding of the pathways involved in their degradation of hazardous compounds. Ralstonia sp. strain RJGII.123 was isolated from soil located at a former coal gasification plant, based on its ability to mineralize carbazole, a three-ring N-heterocyclic pollutant. Experiments were carried out with strain RJGHII.123 and 14C-carbazole (2 mg/L and 500 mg/L) as the sole organic carbon source. At 15 days, 80% of the 2 mg/L carbazole was recovered as CO2, and <1% remained as undegraded carbazole, while 24% of the 500 mg/L carbazole was recovered as CO2 and approximately 70% remained as undegraded carbazole. Several stable intermediates were formed during this time. These intermediates were separated by high performance liquid chromatography (HPLC) and were characterized using high resolution mass spectroscopy (HR-MS) and gas chromatography - mass spectroscopy (GC-MS). At least 10 ring cleavage products of carbazole degradation were identified; four of these were confirmed as anthranilic acid, indole-2-carboxylic acid, indole-3-carboxylic acid, and (1H)-4-quinolinone by comparison with standards. These data indicate that strain RJGII.123 shares aspects of carbazole degradation with previously described Pseudomonas spp., and may be useful in facilitating the bioremediation of NHA from contaminated soils.

Selective and continuous degradation of carbazole contained in petroleum oil by resting cells of Sphingomonas sp. CDH-7.

Microbial degradation of carbazole (CA), a model of hard-removal heterocyclic nitrogen compounds contained in petroleum oil, was examined using Sphingomonas sp. CDH-7 isolated from a soil sample by screening for CA-assimilating microorganisms. CDH-7 used CA as a sole source of carbon and nitrogen, and metabolized CA to ammonia via anthranilic acid as an intermediate product. When CDH-7 was cultivated in the medium containing CA at the concentration of 500 mg/l (2.99 mM), CA was completely degraded within 50 h. By the reaction with the resting cells of CDH-7, 500 mg/l of CA was completely degraded within 4 h, with 1.64 mM of ammonia accumulated in the reaction mixture. When CA was added at the concentration of 100 mg/l (0.599 mM) periodically to the reaction mixture ten times, 925 mg/l (5.54 mM) of CA was degraded within 48 h by the resting cells, and 4.50 mM of ammonia was accumulated in the reaction mixture with a 75.1% molar conversion yield based on total CA added. The resting cells could almost completely degrade CA in a two-liquid-phase system which consists of water and organic solvent, even in the presence of 20% (v/v) isooctane, n-hexane, cyclohexane, and kerosene as a model petroleum oil. In the presence of an organic solvent system such as 20% (v/v) pxylene, toluene, and heptanol, however, CA degradation yields decreased.

Novel Carbazole Degradation Genes ofSphingomonasCB3: Sequence Analysis, Transcription, and Molecular Ecology

The degradation of aromatic compounds by bacteria is dependent upon specific catabolic operons. The uniquecarlocus isolated fromSphingomonasCB3 encodes the first four enzymes involved in the catabolism of the azaarene carbazole. These include a class II three-component dioxygenase enzyme system, a dihydrodiol dehydrogenase, an extradiol (meta-cleavage) dioxygenase, and a hydrolase. Homology of deduced amino acid sequences is closer to corresponding biphenyl catabolic genes than to previously characterised carbazole degradation genes. Gene arrangement is also identical to that found in somebphloci. Thecargenes are transcribed when carbazole is utilised as a sole carbon source, and although biphenyl does not serve as a growth substrate forSphingomonasCB3 it is able to act as a non-metabolisable inducer of thecarlocus. Ecologically thecargenes were detected in polycyclic aromatic hydrocarbon (PAH) contaminated soil associated with a former town gas site.

Cloning of genes involved in carbazole degradation of Pseudomonas sp. strain CA10: nucleotide sequences of genes and characterization of meta-cleavage enzymes and hydrolase.

The DNA fragment encoding meta-cleavage enzymes and the meta-cleavage compound hydrolase, involved in carbazole degradation, was cloned from the carbazole-utilizing bacterium Pseudomonas sp. strain CA10. DNA sequence analysis of this 2.6-kb SmaI-SphI fragment revealed that there were three open reading frames (ORF1, ORF2, and ORF3, in this gene order). ORF1 and ORF2 were indispensable for meta-cleavage activity for 2'-aminobiphenyl-2,3-diol and its easily available analog, 2,3-dihydroxybiphenyl, and were designated carBa and carBb, respectively. The alignment of CarBb with other meta-cleavage enzymes indicated that CarBb may have a non-heme iron cofactor coordinating site. On the basis of the phylogenetic tree, CarBb was classified as a member of the protocatechuate 4,5-dioxygenase family. This unique extradiol dioxygenase, CarB, had significantly higher affinity and about 20-times-higher meta-cleavage activity for 2,3-dihydroxybiphenyl than for catechol derivatives. The putative polypeptide encoded by ORF3 was homologous with meta-cleavage compound hydrolases in other bacteria, and ORF3 was designated carC. The hydrolase activity of CarC for 2-hydroxy-6-oxo-6-phenylhexa-2,4-dienoic acid, the meta-cleavage compound of 2,3-dihydroxybiphenyl, was 40 times higher than that for 2-hydroxy-6-oxohepta-2,4-dienoic acid, the meta-cleavage compound of 3-methylcatechol. Alignment analysis and the phylogenetic tree indicate that CarC has greatest homologies with hydrolases involved in the monoaromatic compound degradation pathway. These results suggest the possibility that CarC is a novel type of hydrolase.

Carbazole Degradation by Pseudomonas sp. LD2: Metabolic Characteristics and the Identification of Some Metabolites

A carbazole-degrading bacterium was isolated by enrichment from a creosote-contaminated soil. This organism, designated Pseudomonas sp. LD2, utilized carbazole as a sole source of carbon, nitrogen, and energy. When isolate LD2 was grown in nitrogen-free mineral medium with 14C-labeled carbazole, 43% was recovered as 14CO2 after 3 days of incubation. Numerous aromatic and heterocyclic compounds were tested as growth substrates for isolate LD2, but few supported the growth of this bacterium. Anthranilic acid and catechol served as growth substrates and were positively identified as intermediates of carbazole degradation by isolate LD2. In addition, 10 nitrogen-containing metabolites were observed in acidified extracts of LD2 culture supernatants, four of which were unequivocally identified. These included indole-3-acetic acid, 5-(2-aminophenyl)-5-oxopentanoic acid, and the cyclized products of 5-(2-aminophenyl)-5-oxopent-3-enoic acid and 6-(2-aminophenyl)-2-hydroxy-6-oxohexa-2,4-dienoic acid.

Isolation and description of carbazole-degrading bacteria

Carbazole is a nitrogen heterocyclic compound associated with fossil fuels and their products. Enrichment cultures were established to isolate bacteria able to degrade carbazole and a plate assay was developed to select carbazole-degrading microorganisms from the enrichments. Three different bacterial isolates capable of mineralizing carbazole were obtained. No intermediates of carbazole degradation were detected. The bacteria had a limited substrate specificity; all used benzoate for growth but were unable to utilize the analogues of carbazole, fluorene, or dibenzothiophene.

Indigenous and enhanced mineralization of pyrene, benzo[a]pyrene, and carbazole in soils

We studied the mineralization of pyrene, carbazole, and benzo[a]pyrene in soils obtained from three abandoned coal gasification plants in southern Illinois. The soils had different histories of past exposure to hydrocarbon contamination and different amounts of total organic carbon, microbial biomass, and microbial activity. Mineralization was measured by using serum bottle radiorespirometry. The levels of indigenous mineralization of 14C-labeled compounds ranged from 10 to 48% for pyrene, from undetectable to 46% for carbazole, and from undetectable to 25% for benzo[a]pyrene following long-term (greater than 180-day) incubations. Pyrene and carbazole were degraded with short or no lag periods in all soils, but benzo[a]pyrene mineralization occurred after a 28-day lag period. Mineralization was not dependent on high levels of microbial biomass and activity in the soils. Bacterial cultures that were capable of degrading pyrene and carbazole were isolated by enrichment, grown in pure culture, and reintroduced into soils. Reintroduction of a pyrene-degrading bacterium enhanced mineralization to a level of 55% within 2 days, compared with a level of 1% for the indigenous population. The carbazole degrader enhanced mineralization to a level of 45% after 7 days in a soil that showed little indigenous carbazole mineralization. The pyrene and carbazole degraders which we isolated were identified as a Mycobacterium sp. and a Xanthamonas sp., respectively. Our results indicated that mineralization of aromatic hydrocarbons can be significantly enhanced by reintroducing isolated polycyclic aromatic hydrocarbon-degrading bacteria.