The metabolism of carbaryl by three bacterial isolates, Pseudomonas spp. (NCIB 12042 & 12043) and Rhodococcus sp. (NCIB 12038) from garden soil

At an alkaline pH and in aqueous solution, carbaryl hydrolyses to form 1-naphthol, methylamine and carbon dioxide, but it is much more stable at an acid pH. Two bacterial isolated from garden soil, Pseudomonas sp. (NCIB 12042) and Rhodococcus sp. (NCIB 12038), could grow on carbaryl as sole carbon and nitrogen source at pH 6.8 but failed to metabolize carbaryl rapidly. Both could use 1-naphthol as sole carbon source and NCIB 12042 metabolized 1-naphthol via salicylic acid which induced higher expression of enzymes in the pathway. Strain NCIB 12038 metabolized 1-naphthol via salicylic and gentisic acids. In contrast, Pseudomonas sp. (NCIB 12043) was selected in a soil perfusion column enrichment at pH 5.2 and metabolized carbaryl rapidly to 1-naphthol and methylamine. 1-Naphthol was metabolized via gentisic acid. Neither salicylate nor gentisate induced higher expression of enzymes for 1-naphthol catabolism in NCIB 12038 and NCIB 12043.     

The specificity of 1-naphthol oxygenases from three bacterial isolates, Pseudomonas spp. (NCIB 12042 and 12043) and Rhodococcus sp. (NCIB 12038) isolated from garden oil

Abstract Three bacterial isolates which appeared to use the insecticide, carbaryl (1-naphthyl, N -methyl-carbamate) as their sole carbon and nitrogen sources were originally selected from garden soil. Only one isolate, Pseudomonas sp. (NCIB 12043) could metabolise carbaryl rapidly to 1-naphthol and methylamine. The other two isolates, Pseudomonas sp. (NCIB 12042) and Rhodococcus sp. (NCIB 12038) relied on slow chemical hydrolysis of carbaryl to 1-naphthol and methylamine. All three isolates used 1-naphthol as their sole carbon source; however, their ability to use naphthalene and a range of mono- and dihydroxy-substituted naphthalene compounds varied. NCIB 12038 and NCIB 12043 showed little or no growth on naphthalene, 2,3-dihydroxynaphthalene or 1,3-dihydroxynaphthalene as sole carbon sources and their 1-naphthol oxygenases had little activity with these substrates. In contrast, NCIB 12042 could use these compounds as sole carbon sources and its 1-naphthol oxygenase also showed activity with them. We conclude that 1-naphthol oxygenase from NCIB 12042 is a relatively non-specific dioxygenase, whereas the 1-naphthol oxygenases from NCIB 12038 and NCIB 12043 are relatively specific monooxygenases requiring hydroxylated naphthalene compounds as substrates.     

The effect of pH on the selection of carbaryl-degrading bacteria from garden soil

At an alkaline pH and in an aqueous solution carbaryl hydrolyses to form 1-naphthol, methylamine and carbon dioxide, but it is much more stable at an acid pH. Soil perfusion column experiments indicated that the rate of carbaryl degradation at pH 6.0 to 7.0 was limited by the rate of chemical hydrolysis. Bacterial communities of at least 12 and 14 members were selected in continuous cultures using carbaryl as the sole carbon and nitrogen source at pH 6.0. These communities were supported by the slow formation of hydrolysis products and a carbaryl-degrading bacterium was not selected after > 2000 h. A bacterial community of at least eight members was selected using equimolar 1-naphthol and methylamine as its sole carbon and nitrogen source. In contrast, after a lag of between 10 and 50 days, soil perfusion column and continuous culture enrichments at pH 5.2 and 5.0, respectively, led to the selection of a Pseudomonas sp. which could utilize carbaryl as its sole carbon and nitrogen source.     

The effect of pH on the selection of carbaryl-degrading bacteria from garden soil

At an alkaline pH and in an aqueous solution carbaryl hydrolyses to form 1-naphthol, methylamine and carbon dioxide, but it is much more stable at an acid pH. Soil perfusion column experiments indicated that the rate of carbaryl degradation at pH 6.0 to 7.0 was limited by the rate of chemical hydrolysis. Bacterial communities of at least 12 and 14 members were selected in continuous cultures using carbaryl as the sole carbon and nitrogen source at pH 6.0. These communities were supported by the slow formation of hydrolysis products and a carbaryl-degrading bacterium was not selected after greater than 2000 h. A bacterial community of at least eight members was selected using equimolar 1-naphthol and methylamine as its sole carbon and nitrogen source. In contrast, after a lag of between 10 and 50 days, soil perfusion column and continuous culture enrichments at pH 5.2 and 5.0, respectively, led to the selection of a Pseudomonas sp. which could utilize carbaryl as its sole carbon and nitrogen source.     

Biodegradation of Carbaryl by a Micrococcus Species

A bacterium capable of utilizing carbaryl as sole source of carbon was isolated from garden soil and identified as a Micrococcus species. The organism also utilized carbofuran, naphthalene, 1-naphthol, and several other aromatic compounds as growth substrates. The organism degraded carbaryl by hydrolysis to yield 1-naphthol and methylamine. 1-Naphthol was further metabolized via salicylate by a gentisate pathway, as evidenced by oxygen uptake and enzymatic studies. Received: 27 November 2000 / Accepted: 29 December 2000     

Metabolism of carbaryl via 1,2-dihydroxynaphthalene by soil isolates Pseudomonas sp. strains C4, C5, and C6

Pseudomonas sp. strains C4, C5, and C6 utilize carbaryl as the sole source of carbon and energy. Identification of 1-naphthol, salicylate, and gentisate in the spent media; whole-cell O2 uptake on 1-naphthol, 1,2-dihydroxynaphthalene, salicylaldehyde, salicylate, and gentisate; and detection of key enzymes, viz, carbaryl hydrolase, 1-naphthol hydroxylase, 1,2-dihydroxynaphthalene dioxygenase, and gentisate dioxygenase, in the cell extract suggest that carbaryl is metabolized via 1-naphthol, 1,2-dihydroxynaphthalene, and gentisate. Here, we demonstrate 1-naphthol hydroxylase and 1,2-dihydroxynaphthalene dioxygenase activities in the cell extracts of carbaryl-grown cells. 1-Naphthol hydroxylase is present in the membrane-free cytosolic fraction, requires NAD(P)H and flavin adenine dinucleotide, and has optimum activity in the pH range 7.5 to 8.0. Carbaryl-degrading enzymes are inducible, and maximum induction was observed with carbaryl. Based on these results, the proposed metabolic pathway is carbaryl --> 1-naphthol --> 1,2-dihydroxynaphthalene --> salicylaldehyde --> salicylate --> gentisate --> maleylpyruvate.     

Degradation of I-Naphthol by a Soil Pseudomonad

A soil Pseudomonas sp. grew with 1-naphthol as sole organic carbon source and produced a 3,4-dihydro-dihydroxy-1(2H)-naphthalenone as the main early intermediary metabolite. Washed 1-naphthol-grown organisms oxidized naphthalene, 1- or 2-naphthol, salicylic acid and, to some extent, 2,3-dihydroxybenzoic acid.     

Hydrolysis of carbaryl by a Pseudomonas sp. and construction of a microbial consortium that completely metabolizes carbaryl.

Two Pseudomonas spp. (isolates 50552 and 50581) isolated from soil degraded 1-naphthol and carbaryl, an N-methylcarbamate pesticide, respectively. They utilized these compounds as a sole source of carbon. 1-Naphthol was completely metabolized to CO2 by the isolate 50552, while the carbaryl was first hydrolyzed to 1-naphthol and then converted into a brown-colored compound by the isolate 50581. The colored metabolite was not degraded, but 1-naphthol produced by the isolate 50581 during the exponential phase of growth was metabolized by the isolate 50552. The two isolates were used to construct a bacterial consortium which completely catabolized carbaryl to CO2. No metabolite was detected in the cell cultures of the consortium. The isolate 50581 harbored a 50-kb plasmid pCD1, while no plasmid was detected in the isolate 50552. The isolated bacteria individually or as a consortium may be used for detoxification of certain industrial and agricultural wastes.     

Hydrolysis of carbaryl by a Pseudomonas sp. and construction of a microbial consortium that completely metabolizes carbaryl

Two Pseudomonas spp. (isolates 50552 and 50581) isolated from soil degraded 1-naphthol and carbaryl, an N-methylcarbamate pesticide, respectively. They utilized these compounds as a sole source of carbon. 1-Naphthol was completely metabolized to CO2 by the isolate 50552, while the carbaryl was first hydrolyzed to 1-naphthol and then converted into a brown-colored compound by the isolate 50581. The colored metabolite was not degraded, but 1-naphthol produced by the isolate 50581 during the exponential phase of growth was metabolized by the isolate 50552. The two isolates were used to construct a bacterial consortium which completely catabolized carbaryl to CO2. No metabolite was detected in the cell cultures of the consortium. The isolate 50581 harbored a 50-kb plasmid pCD1, while no plasmid was detected in the isolate 50552. The isolated bacteria individually or as a consortium may be used for detoxification of certain industrial and agricultural wastes.     

Metabolism of Carbaryl via 1,2-Dihydroxynaphthalene by Soil Isolates Pseudomonas sp. Strains C4, C5, and C6

Pseudomonas sp. strains C4, C5, and C6 utilize carbaryl as the sole source of carbon and energy. Identification of 1-naphthol, salicylate, and gentisate in the spent media; whole-cell O₂ uptake on 1-naphthol, 1,2-dihydroxynaphthalene, salicylaldehyde, salicylate, and gentisate; and detection of key enzymes, viz, carbaryl hydrolase, 1-naphthol hydroxylase, 1,2-dihydroxynaphthalene dioxygenase, and gentisate dioxygenase, in the cell extract suggest that carbaryl is metabolized via 1-naphthol, 1,2-dihydroxynaphthalene, and gentisate. Here, we demonstrate 1-naphthol hydroxylase and 1,2-dihydroxynaphthalene dioxygenase activities in the cell extracts of carbaryl-grown cells. 1-Naphthol hydroxylase is present in the membrane-free cytosolic fraction, requires NAD(P)H and flavin adenine dinucleotide, and has optimum activity in the pH range 7.5 to 8.0. Carbaryl-degrading enzymes are inducible, and maximum induction was observed with carbaryl. Based on these results, the proposed metabolic pathway is carbaryl → 1-naphthol → 1,2-dihydroxynaphthalene → salicylaldehyde → salicylate → gentisate → maleylpyruvate.     

Metabolism of DDT analogues by a Pseudomonas sp.

A Pseudomonas sp. rapidly metabolized several nonchlorinated analogues of DDT, with the exception of 2,2-diphenylethanol, as the sole carbon source. Several of the mono-p-chloro-substituted diphenyl analogues were also metabolized as the sole carbon source by the bacterium. The resulting chlorinated aromatic acid metabolites were not further metabolized. The isolate was unable to metabolize p,p'-dichlorodiphenyl analogues as the sole carbon source.     

Involvement of two plasmids in the degradation of carbaryl by Arthrobacter sp. strain RC100

A bacterium capable of utilizing carbaryl (1-naphthyl N-methylcarbamate) as the sole carbon source was isolated from carbaryl-treated soil. This bacterium was characterized taxonomically as Arthrobacter and was designated strain RC100. RC100 hydrolyzes the N-methylcarbamate linkage to 1-naphthol, which was further metabolized via salicylate and gentisate. Strain RC100 harbored three plasmids (designated pRC1, pRC2, and pRC3). Mutants unable to degrade carbaryl arose at a high frequency after treating the culture with mitomycin C. All carbaryl-hydrolysis-deficient mutants (Cah-) lacked pRC1, and all 1-naphthol-utilization-deficient mutants (Nat-) lacked pRC2. The plasmid-free strain RC107 grew on gentisate as a carbon source. These two plasmids could be transferred to Cah- mutants or Nat- mutants by conjugation, resulting in the restoration of the Cah and Nah phenotypes.     

Degradation of phenanthrene via meta-cleavage of 2-hydroxy-1-naphthoic acid by Ochrobactrum sp. strain PWTJD

The present study describes the assimilation of phenanthrene by an aerobic bacterium, Ochrobactrum sp. strain PWTJD, isolated from municipal waste-contaminated soil sample utilizing phenanthrene as a sole source of carbon and energy. The isolate was identified as Ochrobactrum sp. based on the morphological, nutritional and biochemical characteristics as well as 16S rRNA gene sequence analysis. A combination of chromatographic analyses, oxygen uptake assay and enzymatic studies confirmed the degradation of phenanthrene by the strain PWTJD via 2-hydroxy-1-naphthoic acid, salicylic acid and catechol. The strain PWTJD could also utilize 2-hydroxy-1-naphthoic acid and salicylic acid, while the former was metabolized by a ferric-dependent meta-cleavage dioxygenase. In the lower pathway, salicylic acid was metabolized to catechol and was further degraded by catechol 2,3-dioxygenase to 2-hydroxymuconoaldehyde acid, ultimately leading to tricarboxylic acid cycle intermediates. This is the first report of the complete degradation of a polycyclic aromatic hydrocarbon molecule by Gram-negative Ochrobactrum sp. describing the involvement of the meta-cleavage pathway of 2-hydroxy-1-naphthoic acid in phenanthrene assimilation.     

Metabolism of Dibenzofuran by Pseudomonas sp. Strain HH69 and the Mixed Culture HH27

A Pseudomonas sp. strain, HH69, and a mixed culture, designated HH27, were isolated by selective enrichment from soil samples. The pure strain and the mixed culture grew aerobically on dibenzofuran as the sole source of carbon and energy. Degradation proceeded via salicylic acid which was branched into the gentisic acid and the catechol pathway. Both salicylic acid and gentisic acid accumulated in the culture medium of strain HH69. The acids were slowly metabolized after growth ceased. The enzymes responsible for their metabolism showed relatively low activities. Besides the above-mentioned acids, 2-hydroxyacetophenone, benzopyran-4-one (chromone), several 2-substituted chroman-4-ones, and traces of the four isomeric monohydroxydiben-zofurans were identified in the culture medium. 2,2′,3-Trihydroxybiphenyl was isolated from the medium of a dibenzofuran-converting mutant derived from parent strain HH69, which can no longer grow on dibenzofuran. This gives evidence for a novel type of dioxygenases responsible for the attack on the biarylether structure of the dibenzofuran molecule. A meta-fission mechanism for cleavage of the dihydroxylated aromatic nucleus of 2,2′,3-trihydroxybiphenyl is suggested as the next enzymatic step in the degradative pathway.     

Isolation of phenanthrene-degrading bacteria and characterization of phenanthrene metabolites

Three aerobic bacterial consortia GY2, GS3 and GM2 were enriched from polycyclic aromatic hydrocarbon-contaminated soils with water-silicone oil biphasic systems. An aerobic bacterial strain utilizing phenanthrene as the sole carbon and energy source was isolated from bacterial consortium GY2 and identified as Sphingomonas sp. strain GY2B. Within 48 h and at 30°C the strain metabolized 99.1% of phenanthrene (100 mg/l) added to batch culture in mineral salts medium and the cell number increased by about 40-fold. Three metabolites 1-hydroxy-2-naphthoic acid, 1-naphthol and salicylic acid, were identified by gas chromatographic mass spectrometry and UV–visible spectroscopy analysis. A degradation pathway was proposed based on the identified metabolites. In addition to phenanthrene, strain GY2B could use other aromatic compounds such as naphthalene, 2-naphthol, salicylic acid, catechol, phenol, benzene and toluene as a sole source of carbon and energy.     

Cyanase-mediated utilization of cyanate in Pseudomonas fluorescens NCIB 11764.

Pseudomonas fluorescens NCIB 11764 was capable of utilizing cyanate (OCN-) as a sole nitrogen source for growth. Crude cell extracts from cells grown on cyanate, but not on ammonium sulfate, were induced for an enzyme catalyzing cyanate conversion to ammonia. Enzymatic activity was shown to be bicarbonate dependent and specific for cyanate as a substrate, suggesting that cyanate utilization in this organism is facilitated by an enzyme resembling cyanase (cyanate amidohydrolase; EC 3.5.5.3), as described previously in Escherichia coli and Flavobacterium sp.     

Transport of methylamine by Pseudomonas sp. MA.

Pseudomonas sp. MA grows on methylamines as a sole source of carbon, nitrogen, and energy. The transport of methylamine into the organism was investigated. It was found that this organism possesses an inducible transport system for methylamine having the following physical parameters: pH optimum, 7.2; temperature optimum, 30 to 35 degrees C; Km, 1 to 30 mM; Vmax, 90 to 120 nmol/min per mg (dry weight) of cells. Methylamine uptake was curtailed by azide, cyanide, and carbonyl cyanide-m-chlorophenylhydrazone; osmotic shock treatment reduced the uptake by 50%. The uptake was not effectively inhibited by ammonium ion, amino acids, or amides, but was competitively inhibited by short-chain alkylamines. Cells grown on succinate-ammonium chloride did not possess the transport system, but it could be induced in such cells by methylamine in 20 h. Cells grown with methylamine as a sole nitrogen, but not carbon, source transported methylamine at a reduced rate.     

Catabolism of homophthalic acid by a soil bacterium

A microorganism capable of degrading homophthalic acid as a sole source of carbon was isolated from soil. The strain was tentatively identified as Pseudomonas sp. Oxygen uptake studies were carried out with possible intermediates. Assays for several different enzymes were performed. Homophthalic acid may be metabolized by this bacterium via p-hydroxyphenyl acetic acid and homogentisic acid intermediates.     

Microbial desulfonation of substituted naphthalenesulfonic acids and benzenesulfonic acids.

Sulfur-limited batch enrichment cultures containing one of nine multisubstituted naphthalenesulfonates and an inoculum from sewage yielded several taxa of bacteria which could quantitatively utilize 19 sulfonated aromatic compounds as the sole sulfur source for growth. Growth yields were about 4 kg of protein per mol of sulfur. Specific degradation rates were about 4 to 14 mu kat/kg of protein. A Pseudomonas sp., an Arthrobacter sp., and an unidentified bacterium were examined. Each desulfonated at least 16 aromatic compounds, none of which served as a carbon source. Pseudomonas sp. strain S-313 converted 1-naphthalenesulfonic acid, 2-naphthalenesulfonic acid, 5-amino-1-naphthalenesulfonic acid, benzenesulfonic acid, and 3-aminobenzenesulfonic acid to 1-naphthol, 2-naphthol, 5-amino-1-naphthol, phenol, and 3-aminophenol, respectively. Experiments with 18O2 showed that the hydroxyl group was derived from molecular oxygen.     

Decomposition of β-Naphthol by a Soil Pseudomonad

Summary: A pseudomonad resembling Pseudomonas fluorescens , which grows with β-naphthol as sole source of carbon, was isolated from soil. It did not grow on either naphthalene, α-naphthol, 1,2- or 2,3 dihydroxynaphthalene. Phenol, benzoic acid, o-, p - and (to a small extent) m -hydroxybenzoic acids supported growth of the organism. A maroon coloured substance was produced from β-naphthol in cultures and by washed organisms. β-Naphthol oxidation depended on an induced enzyme system. β-Naphthol-grown organisms oxidized β-naphthol and 2,3- and 2,6-dihydroxynaphthalene immediately and several mono- and di-hydroxybenzoic acids, including salicylic acid, only after a lag. 2,3-Dihydroxynaphthalene may be a metabolite of β-naphthol.