Conversion of 2-chloromaleylacetate in Alcaligenes eutrophus JMP134

2,4-Dichlorophenoxyacetate (2,4-D) in Alcaligenes eutrophus JMP134 (pJP4) is degraded via 2-chloromaleylacetate as an intermediate. The latter compound was found to be reduced by NADH in a maleylacetate reductase catalyzed reaction. Maleylacetate and chloride were formed as products of 2-chloromaleylacetate reduction, the former being funnelled into the 3-oxoadipate pathway by a second reductive step. There was no indication for an involvement of a pJP4-encoded enzyme in either the reduction or the dechlorination reaction.Abbreviations 2,4-D 2,4-dichlorophenoxyacetate     

Catabolism of 2,6-dinitrophenol by Alcaligenes eutrophus JMP 134 and JMP 222

Both Alcaligenes eutrophus JMP 134 and its plasmid-free derivative Alcaligenes eutrophus JMP 222 utilize 2,6-dinitrophenol as sole source of carbon, energy, and nitrogen. In the presence of ammonia resting cells of these strains release two mol of nitrite per mol of 2,6-dinitrophenol. Alcaligenes eutrophus JMP 222-1D, a mutant of strain JMP 222 obtained by transposon (Tn5) mutagenesis, is able to use 2,6-dinitrophenol as nitrogen source but not as source of carbon and energy. Resting cells of this mutant liberate only one mol of nitrite per mol of 2,6-dinitrophenol. A single metabolite was detected by high-pressure liquid chromatography and identified as 2-hydroxy-5-nitropenta-2,4-dienoic acid from the mass spectrum, the ¹H-, and ¹³C-NMR spectra. Strain JMP 222-1S, a spontaneous mutant of strain JMP 222-1D, accumulates 4-nitropyrogallol which was identified as the initial metabolite of 2,6-dinitrophenol degradation.Non-standard abbreviations 2,4-D 2,4-dichlorophenoxyacetic acid - 2,6-DNP 2,6-dinitrophenol - HNMA 2-hydroxy-5-nitromuconic acid - HNPA 2-hydroxy-5-nitropenta-2,4-dienoic acid - NB nutrient broth - NMR nuclear magnetic resonance - NPG 4-nitropyrogallol - O.D. optical density - t_R retention time - UV/Vis ultraviolet/visible     

Metabolization of 3,5-dichlorocatechol by Alcaligenes eutrophus JMP 134

2,4-Dichloro-cis,cis-muconate is established as ringcleavage product in the degradation of 3,5-dichlorocatechol by Alcaligenes eutrophus JMP 134. The formerly described isomerization of 2-chloro-trans- to 2-chlorocis-4-carboxymethylenebut-2-en-4-olide as an essential catabolic step could not be certified.     

Formation of Dimethylmuconolactones from Dimethylphenols by Alcaligenes eutrophus JMP 134

2,3-, 2,4-, 2,5-, 3,4-, and 3,5-dimethylphenols were cometabolized by 2,4-dichlorophenoxyacetate-grown Alcaligenes eutrophus JMP 134 or the constitutive derivative JMP 134-1 via the ortho pathway into dimethylmuconolactones as dead-end products. Formation of two distinct lactones from 3,4-dimethylphenol is indicative of 2- as well as 6-hydroxylation. Induction of the meta-cleavage pathway by 2,3- and 3,4-dimethylphenols resulted in growth and no accumulation of products. In contrast, 3,5-dimethylphenol is not metabolized by the meta-cleavage pathway.     

Metabolism of 2-chloro-4-methylphenoxyacetate by Alcaligenes eutrophus JMP 134

2-Chloro-4-methylphenoxyacetate is not a growth substrate for Alcaligenes eutrophus JMP 134 and JMP 1341. It is, however, being transformed by enzymes of 2,4-dichlorophenoxyacetic acid metabolism to 2-chloro-4-methyl-cis, cis-muconate, which is converted by enzymatic 1,4-cycloisomerization to 4-carboxymethyl-2-chloro-4-methylmuconolactone as a dead end metabolite. Chemically, only 3,6-cycloisomerization occurs, giving rise to both diastereomers of 4-carboxychloromethyl-3-methylbut-2-en-4-olide. Those lactones harbonring a chlorosubstituent on the 4-carboxymethyl side chain were surprisingly stable under physiological as well as acidic conditions.     

Trichloroethylene degradation by two independent aromatic-degrading pathways in Alcaligenes eutrophus JMP134

The bacterium Alcaligenes eutrophus JMP134(pJP4) degrades trichloroethylene (TCE) by a chromosomal phenol-dependent pathway and by the plasmid-encoded 2,4-dichlorophenoxyacetic acid pathway. The two pathways were independent and exhibited different rates of removal and capacities for quantity of TCE removed. The phenol-dependent pathway was more rapid (0.2 versus 0.06 nmol of TCE removed per min per mg of protein) and consumed all detectable TCE. The 2,4-dichlorophenoxyacetic acid-dependent pathway removed 40 to 60% of detectable TCE.     

Purification and characterization of dichloromuconate cycloisomerase from Alcaligenes eutrophus JMP 134.

Dichloromuconate cycloisomerase from Alcaligenes eutrophus JMP 134 was purified to homogeneity. The enzyme has an Mr of about 270,000 as determined by gel filtration and consists of six to eight subunits of identical Mr 40,000 as determined by SDS/PAGE. Mn2+ ions as well as thiol groups are required for activity. A high Km value of about 4 mM for cis,cis-muconate explains the reported low activity with this compound. Relatively high Km values were also calculated for monochloro-substituted cis,cis-muconates (300-500 microM), in contrast with the low Km value of 20 microM for 2,4-dichloro-cis,cis-muconate. The catalytic constant of the pure enzyme was 3820 min-1 when measured with 2,4-dichloro-cis,cis-muconate.     

Degradation of Chlorophenols by Alcaligenes eutrophus JMP134(pJP4) in Bleached Kraft Mill Effluent

The ability of Alcaligenes eutrophus JMP134(pJP4) to degrade 2,4-dichlorophenoxyacetic acid, 2,4,6-trichlorophenol, and other chlorophenols in a bleached kraft mill effluent was studied. The efficiency of degradation and the survival of strain JMP134 and indigenous microorganisms in short-term batch or long-term semicontinuous incubations performed in microcosms were assessed. After 6 days of incubation, 2,4-dichlorophenoxyacetate (400 ppm) or 2,4,6-trichlorophenol (40 to 100 ppm) were extensively degraded (70 to 100%). In short-term batch incubations, indigenous microorganisms were unable to degrade such of compounds. Degradation of 2,4,6-trichlorophenol by strain JMP134 was significantly lower at 200 to 400 ppm of compound. This strain was also able to degrade 2,4-dichlorophenoxyacetate, 2,4,6-trichlorophenol, 4-chlorophenol, and 2,4,5-trichlorophenol when bleached Kraft mill effluent was amended with mixtures of these compounds. On the other hand, the chlorophenol concentration and the indigenous microorganisms inhibited the growth and survival of the strain in short-term incubations. In long-term (>1-month) incubations, strain JMP134 was unable to maintain a large, stable population, although extensive 2,4,6-trichlorophenol degradation was still observed. The latter is probably due to acclimation of the indigenous microorganisms to degrade 2,4,6-trichlorophenol. Acclimation was observed only in long-term, semicontinuous microcosms.     

Competition between Pseudomonas fluorescens Ag1 and Alcaligenes eutrophus JMP134 (pJP4) during colonization of barley roots

Abstract: To use deliberately released beneficial microorganisms in the rhizosphere, we need a better understanding of the process of root colonization by seed-borne or soil-borne inocula. In this study, we determine the survival of Pseudomonas fluorescens Ag1 and Alcaligenes eutrophus JMP134, their colonization ability as affected by substrates, and the relative importance of migration versus competition for colonization of the root. Ag1 and the 2,4-dichlorophenoxy-acetic acid (2,4-D) degrader JMP134 were inoculated in sterile barley rhizosphere systems. After inoculation of seeds with individual strains, comparable population sizes were established in the rhizosphere as determined by immunofluorescence microscopic total cell counts. Both strains were motile and able to colonize the entire root system without percolating water to stimulate passive transport. Comparing immunofluorescence microscopic cell counts with colony-forming units demonstrated that a subpopulation of A. eutrophus JMP134 closely associated with the root was non-culturable in contrast to the population in rhizosphere soil. Hence, the sole use of culture-dependent methods may give misleading information about the distribution of bacteria in the rhizosphere. Colonization studies with both strains showed that co-inoculation of Ag1 and JMP134 caused a decrease of the population size of JMP134 if 2,4-D was not added to the soil as a specific carbon source for this strain. Thus, competition for limited carbon sources might influence the composition of the bacterial community in the rhizosphere. We also found that the presence of an established inoculum in the soil reduced subsequent root colonization by a seed-inoculated strain, probably by filling available niches, also indicating that competition from other bacteria may be an important factor determining the distribution of seed-borne inocula. This factor may be just as important for the distribution of bacteria as migration.     

Purification and characterization of maleylacetate reductase from Alcaligenes eutrophus JMP134(pJP4).

Maleylacetate reductase (EC 1.3.1.32) plays a major role in the degradation of chloroaromatic compounds by channeling maleylacetate and some of its substituted derivatives into the 3-oxoadipate pathway. The enzyme was purified to apparent homogeneity from an extract of 2,4-dichlorophenoxyacetate (2,4-D)-grown cells of Alcaligenes eutrophus JMP134. Maleylacetate reductase appears to be a dimer of two identical subunits of 35 kDa. The pI was determined to be at pH 5.4. There was no indication of a flavin prosthetic group. The enzyme was inactivated by p-chloromercuribenzoate but not by EDTA, 1,10-phenanthroline, or dithiothreitol. Maleylacetate and 2-chloromaleylacetate were converted with similar efficiencies (with NADH as cosubstrate, Km = 31 microM for each substrate and kcat = 8,785 and 7,280/min, respectively). NADH was preferred to NADPH as the cosubstrate. Upon reduction of 2-chloramaleylacetate by the purified enzyme, chloride was liberated and the resulting maleylacetate was further reduced by a second NADH. These results and the kinetic parameters suggest that the maleylacetate reductase is sufficient to channel the 2,4-D degradation intermediate 2-chloromaleylacetate into the 3-oxoadipate pathway. In a data base search the NH2-terminal sequence of maleylacetate reductase was found to be most similar to that of TfdF, a pJP4-encoded protein of as-yet-unknown function in 2,4-D degradation.     

Trichloroethylene degradation by two independent aromatic-degrading pathways in Alcaligenes eutrophus JMP134.

The bacterium Alcaligenes eutrophus JMP134(pJP4) degrades trichloroethylene (TCE) by a chromosomal phenol-dependent pathway and by the plasmid-encoded 2,4-dichlorophenoxyacetic acid pathway. The two pathways were independent and exhibited different rates of removal and capacities for quantity of TCE removed. The phenol-dependent pathway was more rapid (0.2 versus 0.06 nmol of TCE removed per min per mg of protein) and consumed all detectable TCE. The 2,4-dichlorophenoxyacetic acid-dependent pathway removed 40 to 60% of detectable TCE.     

Modified ortho-cleavage pathway in Alcaligenes eutrophus JMP134 for the degradation of 4-methylcatechol

Abstract 2,4-Dichlorophenoxyacetate-grown cells of Alcaligenes eutrophus JMP134 [1] metabolized 4-methylphenoxyacetate via a modified ortho -cleavage pathway. 4-Carboxymethyl-4-methylbut-2-en-1,4-olide (4-methyl-2-enelactone), 4-carboxymethyl-3-methylbut-2-en-1,4-olide (3-methyl-2-enelactone) and 4-methyl-3-oxoadipate, were identified as intermediates.     

Accumulation of 2-chloromuconate during metabolism of 3-chlorobenzoate by Alcaligenes eutrophus JMP134

Alcaligenes eutrophus JMP134 metabolizes 3-chlorobenzoate via 3- (3CC) and 4-chlorocatechol (4CC) as central metabolites. Whereas 4CC was efficiently degraded without a build-up of significant quantities of intermediates, substantial amounts of 2-chloro-cis,cis-muconate (2CM) formed from 3CC were excreted as a result of the poor activity of dichloromuconate cycloisomerase for this compound. This pathway bottleneck can, using appropriate fermentation conditions, be exploited in the production of 2CM. Correspondence to: D. H. Pieper     

Duplication of a 2,4-dichlorophenoxyacetic acid monooxygenase gene in Alcaligenes eutrophus JMP134(pJP4).

The Alcaligenes eutrophus JMP134 plasmid pJP4 contains genes necessary for the complete degradation of 2,4-dichlorophenoxyacetic acid (2,4-D) and 3-chlorobenzoic acid. tfdA encodes 2,4-D monooxygenase, the initial enzyme in the 2,4-D catabolic pathway. The tfdA locus has recently been localized to a region on pJP4 13 kilobases away from a cluster of five genes, tfdB to tfdF, which encode the enzymes responsible for the further degradation of 2,4-D to chloromaleylacetic acid (W.R. Streber, K. N. Timmis, and M. H. Zenk, J. Bacteriol. 169:2950-2955, 1987). A second, dissimilar locus on pJP4, tfdAII, has been observed which encodes 2,4-D monooxygenase activity. Gas chromatographic analysis of the 2,4-D metabolites of A. eutrophus harboring pJP4 or subclones thereof localized tfdAII to within a 9-kilobase SstI fragment of pJP4 which also carries the genes tfdBCDEF. This fragment was further characterized in Escherichia coli by deletion and subcloning analysis. A region of 2.5 kilobases, adjacent to tfdC, enabled E. coli extracts to degrade 2,4-D to 2,4-dichlorophenol. Hybridization under low-stringency conditions was observed between tfdA and tfdAII, signifying that the 2,4-D monooxygenase gene was present as two related copies on pJP4.     

Analysis of duplicated gene sequences associated with tfdR and tfdS in Alcaligenes eutrophus JMP134.

Plasmid pJP4 of Alcaligenes eutrophus JMP134 encodes the degradation of 2,4-dichlorophenoxyacetic acid. A 1.2-kb BamHI-XhoI region of the restriction fragment BamHI-E has been proposed to contain the regulatory gene tfdR (A. R. Harker, R. H. Olsen, and R. J. Seidler, J. Bacteriol. 171:314-320, 1989; B. Kaphammer, J. J. Kukor, and R. H. Olsen, J. Bacteriol. 172:2280-2286, 1990). When sequenced and analyzed, the region is shown to contain two incomplete open reading frames (ORFs) positioned divergently. The complete DNA sequence for one of the two ORFs was obtained by sequencing the adjacent restriction fragment BamHI-F. The DNA sequence reveals 100% identify with the regulatory gene tfdS of pJP4. An XbaI-PstI fragment, containing the complete ORF, encodes a 32,000-Da protein which binds to the promoter regions upstream from tfdA and tfdDII. The deduced amino acid sequence of the complete ORF shows similarity with sequences of activator proteins TcbR, CatM, and CatR of the LysR family. The complete ORF represents the regulatory gene tfdR. The deduced amino acid sequence of the incomplete ORF, situated divergently from tfdR, indicates similarity to chloromuconate cycloisomerases produced by genes tfdD and tcbD of plasmids pJP4 and pP51, respectively. This ORF is identified as part of a putative isofunctional gene, tfdDII.     

Gene transfer of Alcaligenes eutrophus JMP134 plasmid pJP4 to indigenous soil recipients.

This study evaluated the potential for gene transfer of a large catabolic plasmid from an introduced organism to indigenous soil recipients. The donor organism Alcaligenes eutrophus JMP134 contained the 80-kb plasmid pJP4, which contains genes that code for mercury resistance. Genes on this plasmid plus chromosomal genes also allow degradation of 2,4-dichloruphenoxyacetic acid (2,4-D). When JMP134 was inoculated into a nonsterile soil microcosm amended with 1,000 micrograms of 2,4-D g-1, significant (10(6) g of soil-1) populations of indigenous recipients or transconjugants arose. These transconjugants all contained an 80-kb plasmid similar in size to pJP4, and all degraded 2,4-D. In addition, all transconjugants were resistant to mercury and contained the tfdB gene of pJP4 as detected by PCR. No mercury-resistant, 2,4-D-degrading organisms with large plasmids or the tfdB gene were found in the 2,4-D-amended but uninoculated control microcosm. These data clearly show that the plasmid pJP4 was transferred to indigenous soil recipients. Even more striking is the fact that not only did the indigenous transconjugant population survive and proliferate but also enhanced rates of 2,4-D degradation occurred relative to microcosms in which no such gene transfer occurred. Overall, these data indicate that gene transfer from introduced organisms is an effective means of bioaugmentation and that survival of the introduced organism is not a prerequisite for biodegradation that utilizes introduced biodegradative genes.     

Growth and viability of Alcaligenes eutrophus JMP134 in seawater as affected by substrate and nutrient amendment

O. NYBROE, K. EINARSON AND T. AHL. 1996. Growth and viability of Alcaligenes eutrophus JMP134 was studied in laboratory microcosms with 0.2 μ-filtered seawater prior to release in field-based mesocosms. In unamended systems JMP134 did not grow and viability, measured as direct viable counts combined with immunofluorescence microscopy, was 40–50%. Addition of a nitrogen+phosphorus nutrient mixture caused a greater growth response than amendment with a carbon substrate. Amendment with substrate and/or nutrients caused an increase in viability to ca 100% but only for a brief period coinciding with cell proliferation. Hence, Alc. eutrophus JMP134 has a limited survival potential in seawater unless it is supplied with additional nutrients.     

Constitutive expression of the cloned phenol hydroxylase gene(s) from Alcaligenes eutrophus JMP134 and concomitant trichloroethylene oxidation.

Given the demonstrated phenol-dependent trichloroethylene (TCE) degradation in Alcaligenes eutrophus JMP134 (A. R. Harker and Y. Kim, Appl. Environ. Microbiol. 56:1179-1181, 1990), this work represents a purposeful effort to create a constitutive degrader of TCE. Genes responsible for phenol hydroxylase activity were identified by Tn5 transposon mutagenesis. Mutants lacked both phenol hydroxylase and catechol 2,3-dioxygenase activities. Southern blot analysis of total DNA showed that all mutants contained a single copy of Tn5 inserted in the same 11.5-kb EcoRI fragment. Complementation with a cosmid-based gene bank constructed from A. eutrophus AEK101 allowed the isolation of three recombinant cosmids carrying a common 16.8-kb HindIII fragment. Deletion and subcloning analysis localized the genes involved in phenol hydroxylase and catechol 2,3-dioxygenase activities. Partial sequence analysis of regions within the cloned phenol hydroxylase-expressing fragment shows significant homology to the oxygenase and oxidoreductase subunits of toluene-3-monooxygenase from Pseudomonas pickettii. The Tn5-induced phl mutant, carrying a recombinant plasmid expressing the phenol hydroxylase activity, degrades TCE in the absence of induction. Complete removal of TCE (50 microM) within 24 h was observed in minimal medium containing only 0.05% ethanol as a carbon source. The bacterium removed 200 microM TCE to below detectable levels within 2 days under noninducing and nonselective conditions.     

Filtration rates of Daphnia cucullata on Alcaligenes eutrophus JMP134 estimated by a fluorescent antibody method

Abstract The fluorescent antibody (FA) technique was employed to estimate the filtration rates of Daphnia cucullata on the Alcaligenes eutrophus JMP134 strain introduced into lake water. We investigated the effect of animal density and food concentration on the filtration rates in 0.2-μm filtered and autoclaved lake water. The individual filtration rates were 0.08–1.12 ml animal⁻¹ h⁻¹. Filtration rates decreased with increasing grazer density and with increasing food concentrations. The grazing impact on indigenous and introduced bacteria was compared in experiments with 2-μm filtered lake water. Filtration rates of D. cucullata on A. eutrophus were greater than on indigenous bacteria. These differences were explained by size-selective grazing, implying that this mechanism is important in the elimination of introduced bacteria from lake water when the introduced bacteria are in the larger size-range of the indigeneuos bacterial flora.