Degradation of naphthalene by cells of Pseudomonas sp. strain NGK 1 immobilized in alginate, agar and polyacrylamide

A Pseudomonas sp. strain NGK 1 (NCIM 5120) was immobilized in various matrices, namely, alginate, agar (1.8 × 10¹¹ cfu g⁻¹ beads) and polyacrylamide (1.6 × 10¹¹ cfu g⁻¹ beads). The degradation of naphthalene was studied, by freely suspended cells (4 × 10¹⁰ cfu ml⁻¹) and immobilized cells in batches, with shaken culture and continuous degradation in a packed-bed reactor. Free cells brought about the complete degradation of 25 mmol naphthalene after 3 days of incubation, whereas, a maximum of 30 mmol naphthalene was degraded by the bacteria after 3–4 days of incubation with 50 mmol and 75 mmol naphthalene, and no further degradation was observed even after 15 days of incubation. Alginate-entrapped cells had degraded 25 mmol naphthalene after 3.5 days of incubation, whereas agar- and polyacrylamide-entrapped cells took 2.5 days; 50 mmol naphthalene was completely degraded by the immobilized cells after 6–7 days of incubation. Maximum amounts of 55 mmol, 70 mmol and 67 mmol naphthalene were degraded, from an initial 75 mmol naphthalene, by the alginate-, agar- and polyacrylamide-entrapped cells after 15 days of incubation. When the cell concentrations were doubled, 25 mmol and 50 mmol naphthalene were degraded after 2 and 5.5 days of incubation by the immobilized cells. Complete degradation of 75 mmol naphthalene occurred after 10 days incubation with agar- and polyacrylamide-entrapped␣cells, whereas only 60 mmol naphthalene was degraded by alginate-entrapped cells after 15 days of␣incubation. Further, with 25 mmol naphthalene, alginate-, agar- and polyacrylamide-entrapped cells (1.8 × 10¹¹ cfu g⁻¹ beads) could be reused 18, 12 and 23 times respectively. During continuous degradation in a packed-bed reactor, 80 mmol naphthalene 100 ml⁻¹ h⁻¹ was degraded by alginate- and polyacrylamide-entrapped cells whereas 80 mmol naphthalene 125 ml⁻¹␣h⁻¹ was degraded by agar-entrapped cells. Received: 21 October 1997 / Received revision: 15 January 1998 / Accepted: 18 January 1998     

Degradation of 2-methylnaphthalene by free and immobilized cells of Pseudomonas sp. strain NGK1

A Pseudomonas sp. strain NGK1 (NCIM 5120) capable of utilizing 2-methylnaphthalene (2-MN) was immobilized in various matrices namely, polyurethane foam (PUF), alginate, agar and polyvinyl alcohol (PVA) (1.5 × 10¹² c.f.u. g^–1 beads). The degradation rates of 25 and 50 mM 2-MN by freely suspended cells (2 × 10¹¹ c.f.u. ml^–1) and immobilized cells in batches, semi-continuous with shaken culture and continuous degradation in a packed-bed reactor were compared. The PUF-immobilized cells achieved higher degradation of 25 and 50 mM of 2-MN than freely suspended cells and the cells immobilized in alginate, agar or PVA. The PVA- and PUF-immobilized cells could be reused for more than 30 and 20 cycles respectively, without losing any degradation capacity. The effect of dilution rates on the rate of degradation of 25 and 50 mM 2-MN with freely suspended and immobilized cells were compared in the continuous system. Increase in dilution rate increased the degradation rate only up to 1 h^–1 in free cells with 25 mM 2-MN and no significant increase was observed with 50 mM 2-MN. With immobilized cells, the degradation rate increased with increase in dilution rate up to 1.5 h^–1 for 25 mM and 1 h^–1 for 50 mM 2-MN. These results revealed that the immobilized cell systems are more efficient than freely suspended cells for biodegradation of 2-MN.     

Degradation of 2-Methylnaphthalene by Pseudomonas sp. Strain NGK1

Pseudomonas sp. strain NGK1, a soil bacterium isolated by naphthalene enrichment from biological waste effluent treatment, capable of utilizing 2-methylnaphthalene as sole source of carbon and energy. To deduce the pathway for biodegradation of 2-methylnaphthalene, metabolites were isolated from the spent medium and identified by thin-layer chromatography and high-performance liquid chromatography. The characterization of purified metabolites, oxygen uptake studies, and enzyme activities revealed that the strain degrades 2-methylnaphthalene through more than one pathway. The growth of the bacterium, utilization of 2-methylnaphthalene, and 4-methylsalicylate accumulation by Pseudomonas sp. strain NGK1 were studied at various incubation periods. Received: 20 March 2001 / Accepted: 25 April 2001     

Monooxygenase-mediated 1,2-dichloroethane degradation by Pseudomonas sp. strain DCA1.

A bacterial strain, designated Pseudomonas sp. strain DCA1, was isolated from a 1,2-dichloroethane (DCA)-degrading biofilm. Strain DCA1 utilizes DCA as the sole carbon and energy source and does not require additional organic nutrients, such as vitamins, for optimal growth. The affinity of strain DCA1 for DCA is very high, with a Km value below the detection limit of 0.5 microM. Instead of a hydrolytic dehalogenation, as in other DCA utilizers, the first step in DCA degradation in strain DCA1 is an oxidation reaction. Oxygen and NAD(P)H are required for this initial step. Propene was converted to 1,2-epoxypropane by DCA-grown cells and competitively inhibited DCA degradation. We concluded that a monooxygenase is responsible for the first step in DCA degradation in strain DCA1. Oxidation of DCA probably results in the formation of the unstable intermediate 1,2-dichloroethanol, which spontaneously releases chloride, yielding chloroacetaldehyde. The DCA degradation pathway in strain DCA1 proceeds from chloroacetaldehyde via chloroacetic acid and presumably glycolic acid, which is similar to degradation routes observed in other DCA-utilizing bacteria.     

Co-metabolic degradation of chlorinated hydrocarbons by Pseudomonas sp. strain DCA1

Pseudomonas sp. strain DCA1, which is capable of utilizing 1,2-dichloroethane (DCA) as sole carbon and energy source, was used to oxidize chlorinated methanes, ethanes, propanes, and ethenes. Chloroacetic acid, an intermediate in the DCA degradation pathway of strain DCA1, was used as a co-substrate since it was readily oxidized by DCA-grown cells of strain DCAI and did not compete for the monooxygenase. All of the tested compounds except tetrachloroethylene (PER) were oxidized by cells expressing DCA monooxygenase. Strain DCAI could not utilize any of these compounds as a growth substrate. Co-metabolic oxidation during growth on DCA was studied with 1,2-dichloropropane. Although growth on this mixture occurred, 1,2-dichloropropane strongly inhibited growth of strain DCAI. This inhibition was not caused by competition for the monooxygenase. It was shown that the oxidation of 1,2dichloropropane resulted in the accumulation of 2,3-dichloro-1-propanol and 2-chloroethanol.     

Enhanced degradation of lignin by the strain fusion of Pseudomonas putida and Gordonia sp

The protoplast fusion technique was applied to construct a more efficient engineering microbial strain to degrade lignin by fusing two strains, Pseudomonas putida and Gordonia sp. At an initial lignin concentration of 900?mg/L, COD, BOD, TOC removal efficiencies increased from 69–76%, 69–72%, and 70–72% by the parent stains to 83%, 83%, and 83% of the fused strain, respectively. IR and HPLC analyses of the treated solution suggested that the fused strains were more capable of breaking the C_α–C_β bonds of the benzene ring in lignin compared to its parent strains, yielding syringyls as the main product. GC–MS analysis was used to identify the release of three-types of lower molecular intermediates: ring-opening, monomer, and dipolymer products. The phenolic hydroxyl group in lignin was oxidized to carbonyls, followed by further degradation to acids and esters. The carboxyl group on the ether linkage that maintains the macromolecular structure of lignin was oxidized to acyls, which further led to depolymerization and the opening of benzene ring.     

Enhanced phenol degradation by immobilized Acinetobacter sp. strain AQ5NOL 1

A locally isolated Acinetobacter sp. Strain AQ5NOL 1 was encapsulated in gellan gum and its ability to degrade phenol was compared with the free cells. Optimal phenol degradation was achieved at gellan gum concentration of 0.75% (w/v), bead size of 3 mm diameter (estimated surface area of 28.26 mm²) and bead number of 300 per 100 ml medium. At phenol concentration of 100 mg l⁻¹, both free and immobilized bacteria exhibited similar rates of phenol degradation but at higher phenol concentrations, the immobilized bacteria exhibited a higher rate of degradation of phenol. The immobilized cells completely degrade phenol within 108, 216 and 240 h at 1,100, 1,500 and 1,900 mg l⁻¹ phenol, respectively, whereas free cells took 240 h to completely degrade phenol at 1,100 mg l⁻¹. However, the free cells were unable to completely degrade phenol at higher concentrations. Overall, the rates of phenol degradation by both immobilized and free bacteria decreased gradually as the phenol concentration was increased. The immobilized cells showed no loss in phenol degrading activity after being used repeatedly for 45 cycles of 18 h cycle. However, phenol degrading activity of the immobilized bacteria experienced 10 and 38% losses after the 46 and 47th cycles, respectively. The study has shown an increased efficiency of phenol degradation when the cells are encapsulated in gellan gum.     

Atrazine degradation in saline wastewater by Pseudomonas sp strain ADP

Wastewater from atrazine manufacturing plants contains large amounts of residual atrazine and atrazine synthesis products, which must be removed before disposal. One of the obstacles to biological treatment of these wastewaters is their high salt content, eg, up to 4% NaCl (w/v). To enable biological treatment, bacteria capable of atrazine mineralization must be adapted to high-salinity conditions. A recently isolated atrazine-degrading bacterium, Pseudomonas sp strain ADP, originally isolated from contaminated soils was adapted to biodegradation of atrazine at salt concentrations relevant to atrazine manufacturing wastewater. The adaptation mechanism was based on the ability of the bacterium to produce trehalose as its main osmolyte. Trehalose accumulation was confirmed by natural-abundance ¹H NMR spectral analysis. The bacterium synthesized trehalose de novo in the cells, but could not utilize trehalose added to the growth medium. Interestingly, the bacterium could not produce glycine betaine (a common compatible solute), but addition of 1 mM of glycine betaine to the medium induced salt tolerance. Osmoregulated Pseudomonas sp strain ADP, feeding on citrate decreased the concentration of atrazine in non-sterile authentic wastewater from 25 ppm to below 1 ppm in less than 2 days. The results of our study suggest that salt-adapted Pseudomonas sp strain ADP can be used for atrazine degradation in salt-containing wastewater. Received 26 August 1997/ Accepted in revised form 06 December 1997     

Oxidation of naphthalene by a multicomponent enzyme system from Pseudomonas sp. strain NCIB 9816.

The initial reactions in the oxidation of naphthalene by Pseudomonas sp. strain NCIB 9816 involves the enzymatic incorporation of one molecule of oxygen into the aromatic nucleus to form (+)-cis-(1R,2S)-dihydroxy-1,2-dihydronaphthalene. The enzyme catalyzing this reaction, naphthalene dioxygenase, was resolved into three protein components, designated A, B, and C, by DEAE-cellulose chromatography. Incubation of naphthalene with components A, B, and C in the presence of NADH resulted in the formation of (+)-cis-(1R,2S)-dihydroxy-1,2-dihydronaphthalene. The ratio of oxygen and NADH utilization to product formation was 1:1:1. NADPH also served as an electron donor for naphthalene oxygenation. However, its activity was less than 50% of that observed with NADH. Component A showed NAD(P)H-cytochrome c reductase activity which was stimulated by the addition of flavin adenine dinucleotide and flavin mononucleotide. A similar stimulation was observed when these flavin nucleotides were added to the naphthalene dioxygenase assay system. These preliminary observations indicate that naphthalene dioxygenase has properties in common with both monooxygenase and dioxygenase multicomponent enzyme systems.     

Combination of degradation pathways for naphthalene utilization in Rhodococcus sp. strain TFB

Rhodococcus sp. strain TFB is a metabolic versatile bacterium able to grow on naphthalene as the only carbon and energy source. Applying proteomic, genetic and biochemical approaches, we propose in this paper that, at least, three coordinated but independently regulated set of genes are combined to degrade naphthalene in TFB. First, proteins involved in tetralin degradation are also induced by naphthalene and may carry out its conversion to salicylaldehyde. This is the only part of the naphthalene degradation pathway showing glucose catabolite repression. Second, a salicylaldehyde dehydrogenase activity that converts salicylaldehyde to salicylate is detected in naphthalene‐grown cells but not in tetralin‐ or salicylate‐grown cells. Finally, we describe the chromosomally located nag genes, encoding the gentisate pathway for salicylate conversion into fumarate and pyruvate, which are only induced by salicylate and not by naphthalene. This work shows how biodegradation pathways in Rhodococcus sp. strain TFB could be assembled using elements from different pathways mainly because of the laxity of the regulatory systems and the broad specificity of the catabolic enzymes.     

Characterization of Gordonia sp. strain CC-NAPH129-6 capable of naphthalene degradation

A naphthalene-degrading isolate able to utilize naphthalene as a sole carbon source was identified as Gordonia sp. CC-NAPH129-6. Here a detail characterization of the naphthalene catabolic genes present in this strain was conducted. In nar region four structural genes (narAa, narAb, narB, narC), two regulatory genes (narR1, narR2), a rubredoxin encoding gene (rub1) and a gene (orf7) with unknown function were obtained. When compared with most of the members within naphthalene-degrading Rhodococcus, these naphthalene catabolic genes in strain CC-NAPH129-6 were organized into an operon-like gene cluster and present in the same order. This naphthalene gene cluster located in a 97-kb small plasmid of strain CC-NAPH129-6, as can be seen from the PFGE and Southern blot hybridization data. Besides, a partial transposase sequence containing an IS element structure with 12-nt inverted repeat at both ends was found, which was flanked by direct repeats downstream the narC gene in strain CC-NAPH129-6. This novel transposase gene sequence was unlike to the transposase sequence found between narR2 and rub1 genes in Rhodococcus opacus R7. The comparative analyses of the naphthalene catabolic genes, 16S rRNA and gyrB gene present in strain CC-NAPH129-6 and naphthalene-degrading Rhodococcus species imply that the naphthalene catabolic genes in strain CC-NAPH129-6 might be horizontally transferred from Rhodococcus members. This is the first report demonstrating that naphthalene catabolic genes organized into an operon-like gene cluster in the genus Gordonia, and this might provide evidence of the importance of this actinobacterial lineage in the bioremediation of oil-contaminated soils.     

Polycyclic aromatic hydrocarbon degradation by biosurfactant-producing Pseudomonas sp. IR1

We characterized a newly isolated bacterium, designated as IR1, with respect to its ability to degrade polycyclic aromatic hydrocarbons (PAHs) and to produce biosurfactants. Isolated IR1 was identified as Pseudomonas putida by analysis of 16S rRNA sequences (99.6% homology). It was capable of utilizing two-, three- and four-ring PAHs but not hexadecane and octadecane as a sole carbon and energy source. PCR and DNA hybridization studies showed that enzymes involved in PAH metabolism were related to the naphthalene dioxygenase pathway. Observation of both tensio-active and emulsifying activities indicated that biosurfactants were produced by IR1 during growth on both water miscible and immiscible substrates. The biosurfactants lowered the surface tension of medium from 54.9 dN cm(-1) to 35.4 dN cm(-1) and formed a stable and compact emulsion with an emulsifying activity of 74% with diesel oil, when grown on dextrose. These findings indicate that this isolate may be useful for bioremediation of sites contaminated with aromatic hydrocarbons.     

Microbial degradation of lipid by Acinetobacter sp. strain SOD-1

Acinetobacter sp. strain SOD-1, capable of rapidly degrading salad oil, was isolated from soil. Strain SOD-1 showed good growth and degraded 68.7+/-2.7 and 83.0% of an initial 3000 ppm salad oil suspension in 24 h at 20 degrees C and pH 7.0 and at 35 degrees C and pH 8.0, respectively. The degradation rate depended on pH, temperature, phosphate concentration, and initial cell density.     

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.     

Toluene and ethylbenzene oxidation by purified naphthalene dioxygenase from Pseudomonas sp. strain NCIB 9816-4.

Purified naphthalene dioxygenase (NDO) from Pseudomonas sp. strain NCIB 9816-4 oxidized toluene to benzyl alcohol and benzaldehyde by reactions involving benzylic monooxygenation and dioxygen-dependent alcohol oxidation, respectively. Xylene and nitrotoluene isomers were also oxidized to substituted benzyl alcohol and benzaldehyde derivatives. NDO oxidized ethylbenzene sequentially through (S)-1-phenethyl alcohol (77% enantiomeric excess) and acetophenone to 2-hydroxyacetophenone. In addition, NDO also oxidized ethylbenzene through styrene to (R)-1-phenyl-1,2-ethanediol (74% enantiomeric excess) by reactions involving desaturation and dihydroxylation, respectively. Isotope experiments with 18O2, H2 18O, and D2O suggest that 1-phenethyl alcohol is oxidized to acetophenone by a minor reaction involving desaturation followed by tautomerization. The major reaction in the conversion of 1-phenethyl alcohol and benzyl alcohol to acetophenone and benzaldehyde, respectively, probably involves monohydroxylation to form a gem-diol intermediate which stereospecifically loses the incoming hydroxyl group to leave the carbonyl product. These results are compared with similar reactions catalyzed by cytochrome P-450.     

施氏假单胞菌YC-YH1的萘降解特性及产物分析

【目的】萘是一种重要的环境污染物,它在环境中的积累会对人类健康造成危害,生物降解是解决这一问题的有效方法。本实验室保存的施氏假单胞菌YC-YH1对萘具有较强的降解能力,在此基础上,研究和分析菌株对萘的降解特性、环境因素对萘降解率的影响以及代谢产物。【方法】本文首先采用单因素实验法研究pH、温度、接种量、萘初始浓度对萘降解率的影响;并在单因素实验结果的基础上,利用Design-Expert 8.0.5软件和Box-Behnken设计对pH、温度、接种量3个影响因素进行响应面优化分析,建立环境因素对萘降解率影响的优化模型。利用LC-MS检测萘降解过程中产生的重要代谢产物,从而推测菌株对萘的代谢途径。【结果】响应面分析结果表明,优化模型极显著(P<0.001),拟合度良好,预测结果可信度高。降解实验证明,在培养温度为32.4 °C、pH为7.10、接种量5.74% (体积比)的优化条件下培养3 d即可将浓度为100 mg/L的萘100%降解。LC-MS分析表明,菌株降解萘的过程中,能够被检测到的主要代谢产物有1,2-二羟基萘、水杨酸、邻苯二酚等。【结论】施氏假单胞菌YC-YH1对萘有高的降解效率,pH、温度、接种量3个因素对菌株的降解率有较大影响。利用响应面法优化菌株对萘的降解条件,能够提高YC-YH1菌株对萘的生物降解性能。初步推测菌株YC-YH1对萘的降解是通过水杨酸途径,萘首先被其代谢为1,2-二羟基萘,而后被转化为水杨酸和邻苯二酚,最后进入三羧酸循环被彻底降解。     

Uptake of methylamine and methanol by Pseudomonas sp. strain AM1.

The uptake of methylamine and of methanol by the facultative methylotroph Pseudomonas sp. strain AM1 was investigated. It was found that this organism possesses two uptake systems for methylamine. One of these operates when methylamine is the sole source of carbon, nitrogen, and energy. It has a Km of 1.33 X 10(-4) M and a Vmax of 67 nmol/min per mg of cells (dry weight). The other system, found when methylamine is the sole nitrogen source only, has a Km of 1.2 X 10(-5) M and a Vmax of 8.9 nmol/min per mg of cells (dry weight). Both uptake systems were severely inhibited by azide, cyanide, carbonyl cyanide-m-chlorophenyl hydrazone, and N-ethylmaleimide, but only the high-affinity system was inhibited by ammonium ions with a Ki of 7.7 mM. Both systems were susceptible to osmotic shock treatment, competitively inhibited by ethylamine, and unaffected by most amino acids. Methanol uptake showed a Km of 4.8 microM and a Vmax of 60.6 nmol/min per mg of cells (dry weight) and was not inhibited by osmotic shock treatment. Azide, cyanide, and N-ethylmaleimide curtailed uptake, but carbonyl cyanide-m-chlorophenyl hydrazone merely reduced the rate of uptake. A methanol dehydrogenase mutant, M15A, was unable to take up methanol. It is proposed that methanol diffuses into the cell where it is rapidly oxidized by methanol dehydrogenase.     

Naphtho[1,2- b]thiophene degradation by Pseudomonas sp. HKT554: involvement of naphthalene dioxygenase

Pseudomonas sp. strain HKT554 degrades naphtho[1,2- b]thiophene and two other isomers, naphtho[2,1- b]thiophene and naphtho[2,3- b]thiophene, by cometabolism, in the absence of any specific inducer, at similar degradation rates. A mutant of strain HKT554, deficient in dibenzothiophene degradation, was generated by using a recently developed transposition system. Sequence analysis of the mutant revealed that the knocked out gene was almost identical to naphthalene dioxygenase (EC 1.14.12.12). The mutant, HKT554M, degraded neither the naphthothiophene isomers nor dibenzothiophene, suggesting that the naphthalene dioxygenase is responsible for the initial catabolic reactions onto naphthothiophenes and dibenzothiophene.     

Evidence for a novel pathway in the degradation of fluorene by Pseudomonas sp. strain F274.

A fluorene-utilizing microorganism, identified as a species of Pseudomonas, was isolated from soil severely contaminated from creosote use and was shown to accumulate six major metabolites from fluorene in washed-cell incubations. Five of these products were identified as 9-fluorenol, 9-fluorenone, (+)-1,1a-dihydroxy-1-hydro-9-fluorenone, 8-hydroxy-3,4-benzocoumarin, and phthalic acid. This last compound was also identified in growing cultures supported by fluorene. Fluorene assimilation into cell biomass was estimated to be approximately 50%. The structures of accumulated products indicate that a previously undescribed pathway of fluorene catabolism is employed by Pseudomonas sp. strain F274. This pathway involves oxygenation of fluorene at C-9 to give 9-fluorenol, which is then dehydrogenated to the corresponding ketone, 9-fluorenone. Dioxygenase attack on 9-fluorenone adjacent to the carbonyl group gives an angular diol, 1,1a-dihydroxy-1-hydro-9-fluorenone. Identification of 8-hydroxy-3,4-benzocoumarin and phthalic acid suggests that the five-membered ring of the angular diol is opened first and that the resulting 2'-carboxy derivative of 2,3-dihydroxy-biphenyl is catabolized by reactions analogous to those of biphenyl degradation, leading to the formation of phthalic acid. Cell extracts of fluorene-grown cells possessed high levels of an enzyme characteristic of phthalate catabolism, 4,5-dihydroxyphthalate decarboxylase, together with protocatechuate 4,5-dioxygenase. On the basis of these findings, a pathway of fluorene degradation is proposed to account for its conversion to intermediary metabolites. A range of compounds with structures similar to that of fluorene was acted on by fluorene-grown cells to give products consistent with the initial reactions proposed.