Expression and transfer of engineered catabolic pathways harbored by Pseudomonas spp. introduced into activated sludge microcosms.

Two genetically engineered microorganisms (GEMs), Pseudomonas sp. strain B13 FR1(pFRC20P) (FR120) and Pseudomonas putida KT2440(pWWO-EB62) (EB62), were introduced into activated sludge microcosms that had the level of aeration, nutrient makeup, and microbial community structure of activated sludge reactors. FR120 contains an experimentally assembled ortho cleavage route for simultaneous degradation of 3-chlorobenzoate (3CB) and 4-methyl benzoate (4MB); EB62 contains a derivative TOL plasmid-encoded degradative pathway for toluene experimentally evolved so that it additionally processes 4-ethyl benzoate (4EB). Experiments assessed survival of the GEMs, their ability to degrade target substrates, and lateral transfer of plasmid-encoded recombinant DNA. GEMs added at initial densities of 10(6) to 10(7) bacteria per ml of activated sludge declined to stable population densities of 10(4) to 10(5) bacteria per ml. FR120 degraded combinations of 3CB and 4MB (1 mM each) following 3 days of adaptation in the microcosms. Indigenous microorganisms required an 8-day adaptation period before degradation of 4MB was observed; 3CB was degraded only after the concentration of 4MB was much reduced. The indigenous microbial community was killed when both compounds were present at concentrations of 4.0 mM. However, in parallel microcosms containing FR120, the microbial community maintained a normal density of viable cells. Indigenous microbes readily degraded 4EB (2 mM), and EB62 did not significantly increase the observed rate of degradation. In filter matings, transfer of pFRC20P, which specifies mobilization but not transfer functions, from FR120 to P. putida UWC1 was not detectable (< 10(-7) transconjugants per donor cell).(ABSTRACT TRUNCATED AT 250 WORDS)     

Survival of genetically modified Pseudomonas fluorescens introduced into subtropical soil microcosms

Abstract A genetically modified strain of Pseudomonas fluorescens and its parent showed grossly similar decline rates following introduction into subtropical clay and sandy soils. In unplanted clay soit at pH 6.9 and 25°C, population densities declined progressively from about 10⁸ to 10³ colony forming units (cfu) g⁻¹ dry soil over 75 days, but in unplanted sandy soil the introduced populations could not be detected after 25 days. In clay soil at pH 8.7 or 4.7, or at environmental temperature, decay rates were enhanced as compared to those at pH 6.9 and 25°C. Counts of introduced strains in clay bulk soil and in rhizosphere and rhizoplane of maize suggested that the introduced bacteria competed well with the native bacteria, and colonized the roots at about 10⁶ cfu g⁻¹ dry root at 25°C, over 20 days. However, rhizoplane colonization was lower at environmental temperature. The decay rate of both strains was slower in planted than in unplanted sandy soil. The population densities in the rhizosphere and rhizoplane in the sandy soil were significantly lower than those in the clay soil. Both introduced strains colonized the maize roots in both soils, using seeds coated with bacteria in 1% carboxymethyl cellulose. Introduced cells were localized at different sites along the roots of plants developing in clay soil, with higher densities in the original (near the seeds) and root hair zones as compared to the intermediate zones. No significant difference was observed between the extent of root colonization of the genetically modified strain and its parent.     

Survival of and plasmid stability in Pseudomonas and Klebsiella spp. introduced into agricultural drainage water

Cell survival and plasmid stability in Pseudomonas fluorescens R2f and Pseudomonas putida CYM 318 containing respectively, plasmid RP4 and pRK2501, and Klebsiella aerogenes NCTC 418 harboring plasmid pBR322 were studied in sterile and nonsterile agricultural drainage water under both aerobic and anaerobic conditions and in the absence and presence of added nutrients. Both Pseudomonas strains survived well in sterile drainage water incubated aerobically, with or without added nutrients. However, Klebsiella aerogenes NCTC 418 (pBR322) only survived in the presence of added nutrients. Pseudomonas fluorescens R2f (RP4) and K. aerogenes NCTC 418 (pBR322) did not survive under anerobic conditions without added nutrients, but showed good survival in the presence of nutrients. Survival of all three strains was negatively affected in nonsterile agricultural drainage water when compared with survival in sterile water. Maintenance of the three plasmids was host, plasmid, and environment dependent. Plasmid pBR322 was not stably maintained in K. aerogenes NCTC 418 under all conditions used in the study, and pRK2501 was readily lost from P. putida CYM 318. Maintenance of RP4 by P. fluorescens R2f was markedly influenced by added nutrients, which caused a loss of the plasmid from cells. The results of the present study demonstrate the influence of nutrients, O2, and native microorganisms on the survival of introduced bacterial strains and plasmid stability in agricultural drainage water.     

Polyphosphate-degrading enzymes in Acinetobacter spp. and activated sludge

Polyphosphate-degrading enzymes were studied in Acinetobacter spp. and activated sludge. Polyphosphate: AMP phosphotransferase activity in Acinetobacter strain 210A decreased with increasing growth rates. The activity of this enzyme in cell extracts of Acinetobacter strain 210A was maximal at a pH of 8.5 and a temperature of 40 degrees C and was stimulated by (NH4)2SO4. The Km for AMP was 0.6 mM, and the Vmax was 60 nmol/min per mg of protein. Cell extracts of this strain also contained polyphosphatase, which was able to degrade native polyphosphate and synthetic magnesium polyphosphate and was strongly stimulated by 300 to 400 mM NH4Cl. A positive correlation was found between polyphosphate:AMP phosphotransferase activity, adenylate kinase activity, and phosphorus accumulation in six Acinetobacter strains. Significant activities of polyphosphate kinase were detected only in strain P, which contained no polyphosphate:AMP phosphotransferase. In samples of activated sludge from different plants, the activity of adenylate kinase correlated well with the ability of the sludge to remove phosphate biologically from wastewater.     

Polyphosphate-degrading enzymes in Acinetobacter spp. and activated sludge.

Polyphosphate-degrading enzymes were studied in Acinetobacter spp. and activated sludge. Polyphosphate: AMP phosphotransferase activity in Acinetobacter strain 210A decreased with increasing growth rates. The activity of this enzyme in cell extracts of Acinetobacter strain 210A was maximal at a pH of 8.5 and a temperature of 40 degrees C and was stimulated by (NH4)2SO4. The Km for AMP was 0.6 mM, and the Vmax was 60 nmol/min per mg of protein. Cell extracts of this strain also contained polyphosphatase, which was able to degrade native polyphosphate and synthetic magnesium polyphosphate and was strongly stimulated by 300 to 400 mM NH4Cl. A positive correlation was found between polyphosphate:AMP phosphotransferase activity, adenylate kinase activity, and phosphorus accumulation in six Acinetobacter strains. Significant activities of polyphosphate kinase were detected only in strain P, which contained no polyphosphate:AMP phosphotransferase. In samples of activated sludge from different plants, the activity of adenylate kinase correlated well with the ability of the sludge to remove phosphate biologically from wastewater.     

Recombinant and wild-type Pseudomonas aureofaciens strains introduced into soil microcosms: effect on decomposition of cellulose and straw

The effect of a genetically engineered Pseudomonas aureofaciens (Ps3732RNL11) strain (GEM) and the parental wild-type (Ps3732RN) on decomposition of cellulose paper, straw and calico cloth was assessed after 18 weeks incubation in laboratory soil microcosms. Effect(s) of inoculum density (10³, 10⁵, and 10⁸ cells/ g dry soil) and single versus multiple bacterial inoculations were also investigated. Cellulose paper was completely decomposed after 18 weeks in all treatments. There were no significant differences (95% level), between treatments, in percentage decomposition of either straw or calico cloth. Recovery of the GEM at 18 weeks, using viable plating, was limited to treatments originally receiving 10⁸ cells/g dry soil. Log 1.8 CFU/g dry soil were recovered from the single dose treatment while log 4.2 CFU/g dry soil were recovered from the multiple dose treatment Biolog metabolic tests were used to determine if the GEM or parental wild-type had any effect on overall carbon utilization in soil. Results suggested they did not. Detection of the recombinant lacZY gene sequence in soil using PCR suggested the possibility of viable but nonculturable cells and/or persistence of chromosomal DNA.     

Cloning and nucleotide sequence of carbazole catabolic genes from Pseudomonas stutzeri strain OM1, isolated from activated sludge

A new carbazole (CAR)-degrading bacterium, called strain OM1, was isolated from activated sludge obtained from sewage disposal plants in Fukuoka Prefecture, and it was identified as Pseudomonas stutzeri. Anthranilic acid (AN), 2'-aminobiphenyl-2,3-diol and its meta-cleavage product, 2-hydroxy-6-oxo-6-(2'-aminophenyl)-hexa-2,4-dienoic acid, were identified as metabolic intermediates of CAR in the ethyl acetate extract of the culture broth. Therefore, the CAR catabolic pathway to AN in strain OM1 was indicated to be identical to those found in the Pseudomonas sp. strains CA06 and CA10. The strain OM1 degraded catechol (CAT) via a meta-cleavage pathway in contrast to strains CA06 and CA10, which transform catechol into cis, cis-munonic acid. Clones containing a 6.9-kb EcoRI fragment and a 3-kb PstI-SphI fragment were isolated from colonies, forming a clear zone of CAR and a yellow ring-cleavage product from CAT, respectively. Recombinant E. coli carrying the 6.9-kb fragment degraded CAR in the L-broth and produced AN. Cell-free extract from the clone carrying a 3-kb PstI-SphI fragment had high meta-ring-cleavage dioxygenase activity for CAT. The nucleotide sequences of these fragments were determined. The 6.9-kb fragment showed a very high degree of homology with the CAR catabolic genes of strain CA10. The amino acid and nucleotide sequences of the 3-kb fragment were found to exhibit significant homology with the genes for the CAT-catabolic enzymes of TOL plasmid pWW0, plasmid NAH7, and plasmid pVI150.     

Survival and catabolic performance of introduced Pseudomonas strains during phytoremediation and bioaugmentation field experiment

A long-term field experiment was carried out to estimate the efficiency of bioaugmentation in combination with phytoremediation for oil shale chemical industry solid waste dump area remediation. Soil samples for microbiological and chemical analysis were collected during 3 years after bacterial biomass application. Microbial communities in soil samples were analysed using both culture-based and molecular methods. The survival of the introduced bacterial strains was confirmed by cultivation-based Box-PCR genomic fingerprints and denaturing gradient gel electrophoresis fingerprinting of the 16S rRNA and lmPH genes. The introduced bacterial strains as well as corresponding catabolic genes were recovered several years after biomass application, predominantly from the rhizosphere of birches. Soil samples from bioaugmented plots showed an elevated potential for degradation of phenolic compounds even 40 months after treatment. Based on our results we can conclude that the introduced Pseudomonas strains both survived, and their metabolic traits have persisted at the contaminated site over a long period of time.     

Evolution of catabolic pathways and metabolic versatility in Pseudomonas stutzeri OX1

Pseudomonas stutzeri OX1 is able to degrade toluene and ortho-xylene via the direct oxygenation of the aromatic ring. The genetic studies carried out suggest that the genes coding for the monooxygenase involved in the early steps of this catabolic route have been acquired by gene transfer. P. stutzeri OX1 is also potentially able to utilize meta- and para-xylene as growth substrates. These two isomers are metabolized through a different pathway (TOL pathway). Both catabolic routes can be activated or inactivated by means of genomic rearrangements. The relevance of such recombination mechanisms in the evolution and the adaptability of P. stutzeri is discussed.     

The genetics of bile acid degradation in Pseudomonas spp.: location and cloning of catabolic genes

Four Pseudomonas spp. capable of utilizing bile acids as sole carbon source were examined for the presence of plasmids. One plasmid was found in Pseudomonas sp. RAL8, but no plasmids could be detected in the other three strains. Mitomycin C curing of RAL8 did not affect the ability of the strain to grow on bile acids. This suggested that the genetic information for bile acid catabolism in all four strains was chromosomally located. To isolate bile acid catabolic genes. DNA from RAL8 was partially digested with Sau3A, then the DNA fragments cloned into the broad-host-range cosmid vector pMMB33. The resulting gene bank was screened by plate-mating with two stable RAL8 mutants. Four of the gene bank clones were found to give a positive complementation with one or both mutants. Examination of the plasmids in the four clones revealed that they were unstable, but detailed mapping enabled a 52 kb restriction map to be derived. Further complementation work showed that two of the bile acid catabolic genes are located close together on the map, and may be contiguous.     

Biodegradaon of phenanthrene in soil microcosms stimulated by an introduced Alcaligenes sp.

Abstract A phenanthrene degrading strain of Alcaligenes sp. was isolated from oil polluted soil. Addition of Alcaligenes sp. to soil microcosms supplemented with phenanthrene (1 mg/g dry soil) resulted in degradation of the added phenanthrene within 11 days. The phenanthrene concentration declined only 12% in uninoculated soil during 42 days. The total phenanthrene degradation potential of Alcaligenes sp. was 2.3 mg/g dry soil during a period of 22 days. The amount of CO₂ evolved during 22 days corresponded to the conversion of 91% of the degraded phenanthrene to CO₂. The Alcaligenes sp. were not able to degrade phenanthrene in sterile soil.     

Production of poly-\-hydroxybutyrate in Acinetobacter spp. isolated from activated sludge

Two strains of Acinetobacter sp. isolated from activated sludge actively removing phosphate were examined for their abilities to produce poly-\-hydroxybutyrate (PHB). When yield-limited by phosphate, strain RA3117 contained material that stained with Sudan Black, but contained only 0.9% PHB on a dry weight basis. This strain contained no sudanophilic material or PHB when limited by ammonia or sulphate. When strain RA3757 was limited by phosphate, ammonia or sulphate it produced 2.0, 7.8 and 11.5% PHB, respectively, on a dry weight basis. \-Ketothiolase and acetoacetyl-coenzyme A (CoA) reductase were only observed in RA3757 cell-free extracts. \-Ketothiolase was produced both in cells with and without PHB whereas acetoacetyl-CoA reductase was found only in cells accumulating PHB. When RA3757 was grown in ammonia-limiting medium with acetate, butyrate, caproate or ethanol as carbon source, similar levels of PHB were produced. When cells were grown on valerate, RA3757 produced 5.6 poly-\-hydroxyvalerate and 0.9% PHB on a dry weight basis. Correspondence to: J. W. May     

Cytokinin production by Agrobacterium and Pseudomonas spp.

The production of cytokinins by plant-associated bacteria was examined by radioimmunoassay. Strains producing trans-zeatin were identified in the genera Agrobacterium and Pseudomonas. Agrobacterium tumefaciens strains containing nopaline tumor-inducing plasmids, A. tumefaciens Lippia isolates, and Agrobacterium rhizogenes strains produced trans-zeatin in culture at 0.5 to 44 micrograms/liter. Pseudomonas solanacearum and Pseudomonas syringae pv. savastanoi produced trans-zeatin at levels of up to 1 mg/liter. In vitro cytokinin biosynthetic activity was measured for representative strains and was found to correlate with trans-zeatin production. The genetic locus for trans-zeatin secretion (tzs) was cloned from four strains: A. tumefaciens T37, A. rhizogenes A4, P. solanacearum K60, and P. syringae pv. savastanoi 1006. Southern blot analysis showed substantial homology of the Agrobacterium tzs genes to each other but not to the two Pseudomonas genes.