Regulation of tfdCDEF by tfdR of the 2,4-dichlorophenoxyacetic acid degradation plasmid pJP4.

The closely linked structural genes tfdCDEF borne on the 2,4-dichlorophenoxyacetic acid (TFD) catabolic plasmid, pRO101, were cloned into vector pRO2321 as a 12.6-kilobase-pair BamHI C fragment and designated pRO2334. The first gene in this cluster, tfdC, encodes chlorocatechol 1,2-dioxygenase and was expressed constitutively. Chlorocatechol 1,2-dioxygenase expression by pRO2334 was repressed in trans by the negative regulatory element, tfdR, on plasmid pRO1949. Derepression of tfdC was achieved when Pseudomonas aeruginosa PAO4032 containing both plasmids pRO2334 and pRO1949 was grown in minimal glucose medium containing TFD, 2,4-dichlorophenol, or 4-chlorocatechol, suggesting that TFD and other pathway intermediates can act as inducing compounds. Genetic organization of the tfdCDEF cluster was established by deletion of the tfdC gene, which resulted in the loss of tfdD and tfdE activity, suggesting that genes tfdCDEF are organized in an operon transcribed from the negatively regulated promoter of tfdC. Deletion subcloning of pRO1949 was used to localize tfdR to a 1.2-kilobase-pair BamHI-XhoI region of the BamHI E fragment of plasmid pRO101. The tfdR gene product was shown not to regulate the expression of tfdB, which encodes 2,4-dichlorophenol hydroxylase.     

Analysis of the 2,4-dichlorophenoxyacetic acid-degradative plasmid pEST4011 of Achromobacter xylosoxidans subsp. denitrificans strain EST4002

The 2,4-dichlorophenoxyacetic acid (2,4-D)-degradative bacterium Achromobacter xylosoxidans subsp. denitrificans strain EST4002, isolated in Estonia more than 10years ago, was found to contain the 70kb plasmid pEST4011 that is responsible for the bacterium having had obtained a stable 2,4-D(+) phenotype. The tfd-like genes for 2, 4-D degradation of the strain EST4002 were located on a 10.5kb region of pEST4011, but without functional genes coding for chloromuconate cycloisomerase and chlorodienelactone hydrolase. The latter two genes are probably encoded by homologous, tcb-like genes, located elsewhere on pEST4011. We also present evidence of two copies of insertion element IS1071-like sequences on pEST4011. IS1071 is a class II (Tn3 family) insertion element, associated with different catabolic genes and operons and globally distributed in the recent past. We speculate that this insertion element might have had a role in the formation of plasmid pEST4011. The 28kb plasmid pEST4012 is generated by deletion from pEST4011 when cells of A. xylosoxidans EST4002 are grown in the absence of 2,4-D in growth medium. We propose that this is the result of homologous recombination between the two putative copies of IS1071-like sequences on pEST4011.     

The completely sequenced plasmid pEST4011 contains a novel IncP1 backbone and a catabolic transposon harboring tfd genes for 2,4-dichlorophenoxyacetic acid degradation

The herbicide 2,4-dichlorophenoxyacetic acid (2,4-D)-degrading bacterium Achromobacter xylosoxidans subsp. denitrificans strain EST4002 contains plasmid pEST4011. This plasmid ensures its host a stable 2,4-D(+) phenotype. We determined the complete 76,958-bp nucleotide sequence of pEST4011. This plasmid is a deletion and duplication derivative of pD2M4, the 95-kb highly unstable laboratory ancestor of pEST4011, and was self-generated during different laboratory manipulations performed to increase the stability of the 2,4-D(+) phenotype of the original strain, strain D2M4(pD2M4). The 47,935-bp catabolic region of pEST4011 forms a transposon-like structure with identical copies of the hybrid insertion element IS1071::IS1471 at the two ends. The catabolic regions of pEST4011 and pJP4, the best-studied 2,4-D-degradative plasmid, both contain homologous, tfd-like genes for complete 2,4-D degradation, but they have little sequence similarity other than that. The backbone genes of pEST4011 are most similar to the corresponding genes of broad-host-range self-transmissible IncP1 plasmids. The backbones of the other three IncP1 catabolic plasmids that have been sequenced (the 2,4-D-degradative plasmid pJP4, the haloacetate-catabolic plasmid pUO1, and the atrazine-catabolic plasmid pADP-1) are nearly identical to the backbone of R751, the archetype plasmid of the IncP1 beta subgroup. We show that despite the overall similarity in plasmid organization, the pEST4011 backbone is sufficiently different (51 to 86% amino acid sequence identity between individual backbone genes) from the backbones of members of the three IncP1 subgroups (the alpha, beta, and gamma subgroups) that it belongs to a new IncP1subgroup, the delta subgroup. This conclusion was also supported by a phylogenetic analysis of the trfA2, korA, and traG gene products of different IncP1 plasmids.     

Sequence of the gene (pheA) encoding phenol monooxygenase from Pseudomonas sp. EST1001: expression in Escherichia coli and Pseudomonas putida.

The plasmid pEST1412 contains the genes, pheA and pheB, encoding phenol monooxygenase (PMO) and catechol 1,2-dioxygenase (C12]), respectively. Thse were originally cloned from the plasmid DNA of Pseudomonas sp. EST1001 [Kivisaar et al., Plasmid 24 (1990) 25-36]. Although pheA and pheB are cotranscribed using the promoter sequences derived from Tn4652 and the level of expression of C120 activities from pEST1412 was equal both in Escherichia coli and in Pseudomonas putida, the level of PMO activity measured in the cell-free extracts of E. coli was lower than that in P. putida. The nucleotide sequence of the 2.0-kb PstI-HindIII fragment of pEST1412 carrying pheA was determined. A 1821-bp ORF was found in this DNA. The structural gene (tfdB) encoding 2,4-dichlorophenol hydroxylase from pJP4 has been sequenced [Perkins et al., J. Bacteriol. 172 (1990) 2351-2359]. Comparison of the deduced amino acid sequences of tfdB and pheA revealed highly conserved regions in the protein products of these genes.     

Operon structure and nucleotide homology of the chlorocatechol oxidation genes of plasmids pJP4 and pAC27

Alcaligenes eutrophus harboring plasmid pJP4 (strain JMP134) is capable of growing on both 2,4-dichlorophenoxyacetate (2,4-D) and 3-chlorobenzoate (3-Cba), while Pseudomonas putida carrying plasmid pAC27 (strain AC867) can utilize only 3-Cba as the sole carbon source. The tfdCDEF operon of the pJP4 plasmid and the clcABD operon of plasmid pAC27 each encode enzymes for the degradation of chlorocatechols (Clc), key intermediates in the catabolism of 2,4-D and 3-Cba. Similarities in the nucleotide (nt) sequences of genes tfdC and clcA, encoding pyrocatechases, were reported earlier [Ghosal and You, Mol. Gen. Genet. 211 (1988a) 113-120]. Genes tfdD and clcB, encoding Clc-specific cycloisomerases, have been completely sequenced. The tfdD gene (1107 bp) is slightly smaller than gene clcB (1113 bp). Comparison of the two cycloisomerase-encoding genes reveals that the nt sequences are 63% homologous with 62% homology in the deduced amino acid (aa) sequences of the polypeptides they encode. Genes tfdD and tfdE are contiguous in the tfdCDEF operon, whereas the corresponding genes, clcB and clcD, of the clcABD operon, are known to be separated by a long open reading frame of unknown function. The predicted N-terminal aa sequences of the two hydrolase-encoding genes, tfdE and clcD, also show homology. The structural and nt homologies between the two Clc operons, tfdCDEF and clcABD, suggest their relatedness.     

Cloning and characterization of tfdS, the repressor-activator gene of tfdB, from the 2,4-dichlorophenoxyacetic acid catabolic plasmid pJP4.

Plasmid pRO101, a derivative of plasmid pJP4 which contains Tn1721 inserted into a nonessential region, is inducible for 2,4-dichlorophenol hydroxylase (DCPH) encoded by tfdB. Plasmid pRO103, which has a deletion in the BamHI-F--BamHI-E region of plasmid pRO101, has elevated basal levels of DCPH but is uninducible. The regulatory gene for tfdB, designated tfdS, was cloned as an 8.3-kilobase-pair EcoRI-E fragment. When the cloned tfdS gene was in trans with plasmid pRO103, the baseline DCPH levels were repressed to normal uninduced levels and were fully induced when this strain was grown in the presence of 2,4-dichlorophenoxyacetic acid, 2,4-dichlorophenol, or 4-chlorocatechol. However, when tfdS was in trans with tfdB in the absence of tfdCDEF, tfdB was repressed but could not be induced. When tfdS and tfdC1, which encodes chlorocatechol 1,2-dioxygenase, are in trans with tfdB, tfdB remained uninduced, indicating that a downstream metabolite of chloro-cis,cis-muconate, either 2-cis-chlorodiene lactone or chloromaleylacetic acid, is the effector. Collectively, these data demonstrate that the gene product of tfdS acts as a repressor of tfdB in the absence of an effector and as an activator of tfdB when an effector is present.     

New plasmids of herbicide 2,4-dichlorophenoxyacetic acid biodegradation

Three herbicide 2,4-D metabolizing bacterial strains were isolated from three independent soil samples of Estonia. The strains, although belonging to various species, contain 2,4-D degradative plasmids with identical restriction patterns. pEST4001 is a 78 kb conjugative plasmid. All Pseudomonas putida PaW340 2,4-D+ transconjugants obtained a 70 kb plasmid pEST4011 - a deletion derivative of the pEST4001. The restriction patterns of the plasmids mentioned above are considerably different from those of the other 2,4-D plasmids pJP4 and pRC10 reported previously.     

Isolation and characterization of a stable 2,4-dichlorophenoxyacetic acid degrading bacterium, Variovorax paradoxus, using chemostat culture

A strain of Variovorax paradoxus degrading 2,4-dichlorophenoxyacetic acid (2,4-D) was isolated from the Dijon area (France) using continuous chemostat culture. This strain, designated TV1, grew on up to 5 mM 2,4-D and efficiently degraded the herbicide as sole carbon source as well as in presence of soil extracts. It also degraded phenol and 2-methyl, 4-chlorophenoxyacetic acid at 3 mM and 2,4-dichlorophenol at 1 mM. This organism contained a stable 200 kb plasmid, designated pTV1, which showed no similarity in its restriction pattern with the archetypal 2,4-D catabolic plasmid pJP4. However, pTV1 contained an 11 kb BamHI fragment which hybridized at low stringency with the 2,4-D degradative genes tfdA, tfdB and tfdR from pJP4. PTV1 partial tfdA sequence showed 77 % similarity with the archetypal tfdA gene sequence from Ralstonia eutropha JMP134. Tn5 mutagenesis confirmed the involvement of this gene in the 2,4-D catabolic pathway. © Rapid Science Ltd. 1998     

Characterization of diverse 2,4-dichlorophenoxyacetic acid-degradative plasmids isolated from soil by complementation.

The diversity of 2,4-dichlorophenoxyacetic acid (2,4-D)-degradative plasmids in the microbial community of an agricultural soil was examined by complementation. This technique involved mixing a suitable Alcaligenes eutrophus (Rifr) recipient strain with the indigenous microbial populations extracted from soil. After incubation of this mixture, Rifr recipient strains which grow with 2,4-D as the only C source were selected. Two A. eutrophus strains were used as recipients: JMP228 (2,4-D-), which was previously derived from A. eutrophus JMP134 by curing of the 2,4-D-degradative plasmid pJP4, and JMP228 carrying pBH501aE (a plasmid derived from pJP4 by deletion of a large part of the tfdA gene which encodes the first step in the mineralization of 2,4-D). By using agricultural soil that had been treated with 2,4-D for several years, transconjugants were obtained with both recipients. However, when untreated control soil was used, no transconjugants were isolated. The various transconjugants had plasmids with seven different EcoRI restriction patterns. The corresponding plasmids are designated pEMT1 to pEMT7. Unlike pJP4, pEMT1 appeared not to be an IncP1 plasmid, but all the others (pEMT2 to pEMT7) belong to the IncP1 group. Hybridization with individual probes for the tfdA to tfdF genes of pJP4 demonstrated that all plasmids showed high degrees of homology to the tfdA gene. Only pEMT1 showed a high degree of homology to tfdB, tfdC, tfdD, tfdE, and tfdF, while the others showed only moderate degrees of homology to tfdB and low degrees of homology to tfdC.(ABSTRACT TRUNCATED AT 250 WORDS)     

Organization and sequence analysis of the 2,4-dichlorophenol hydroxylase and dichlorocatechol oxidative operons of plasmid pJP4.

Growth of Alcaligenes eutrophus JMP134 on 2,4-dichlorophenoxyacetate requires a 2,4-dichlorphenol hydroxylase encoded by gene tfdB. Catabolism of either 2,4-dichlorophenoxyacetate or 3-chlorobenzoate involves enzymes encoded by the chlorocatechol oxidative operon consisting of tfdCDEF, which converts 3-chloro- and 3,5-dichlorocatechol to maleylacetate and chloromaleylacetate, respectively. Transposon mutagenesis has localized tfdB and tfdCDEF to EcoRI fragment B of plasmid pJP4 (R. H. Don, A. J. Wieghtman, H.-J. Knackmuss, and K. N. Timmis, J. Bacteriol. 161:85-90, 1985). We present the complete nucleotide sequence of tfdB and tfdCDEF contained within a 7,954-base-pair HindIII-SstI fragment from EcoRI fragment B. Sequence and expression analysis of tfdB in Escherichia coli suggested that 2,4-dichlorophenol hydroxylase consists of a single subunit of 65 kilodaltons. The amino acid sequences of proteins encoded by tfdD and tfdE were found to be 63 and 53% identical to those of functionally similar enzymes encoded by clcB and clcD, respectively, from plasmid pAC27 of Pseudomonas putida. P. putida(pAC27) can utilize 3-chlorocatechol but not dichlorinated catechols. A region of DNA adjacent to clcD in pAC27 was found to be 47% identical in amino acid sequence to tfdF, a gene important in catabolizing dichlorocatechols. The region in pAC27 does not appear to encode a protein, suggesting that the absence of a functional trans-chlorodienelactone isomerase may prevent P. putida(pAC27) from utilizing 3,5-dichlorocatechol.     

Transposon mutagenesis and cloning analysis of the pathways for degradation of 2,4-dichlorophenoxyacetic acid and 3-chlorobenzoate in Alcaligenes eutrophus JMP134(pJP4).

Plasmid pJP4 permits its host bacterium, strain JMP134, to degrade and utilize as sole sources of carbon and energy 3-chlorobenzoate and 2,4-dichlorophenoxyacetic acid (R. H. Don and J. M. Pemberton, J. Bacteriol. 145:681-686, 1981). Mutagenesis of pJP4 by transposons Tn5 and Tn1771 enabled localization of five genes for enzymes involved in these catabolic pathways. Four of the genes, tfdB, tfdC, tfdD, and tfdE, encoded 2,4-dichlorophenol hydroxylase, dichlorocatechol 1,2-dioxygenase, chloromuconate cycloisomerase, and chlorodienelactone hydrolase, respectively. No function has been assigned to the fifth gene, tfdF, although it may encode a trans-chlorodiene-lactone isomerase. Inactivation of genes tfdC, tfdD, and tfdE, which encode the transformation of dichlorocatechol to chloromaleylacetic acid, prevented host strain JMP134 from degrading both 3-chlorobenzoate and 2,4-dichlorophenoxyacetic acid, which indicates that the pathways for these two substrates utilize common enzymes for the dissimilation of chlorocatechols. Studies with cloned catabolic genes from pJP4 indicated that whereas all essential steps in the degradation of 2,4-dichlorophenoxyacetic acid are plasmid encoded, the conversion of 3-chlorobenzoate to chlorocatechol is specified by chromosomal genes.     

The metabolic pathway of 2,4-dichlorophenoxyacetic acid degradation involves different families of tfdA and tfdB genes according to PCR-RFLP analysis

Abstract: Twenty-five 2,4-dichlorophenoxyacetic acid (2,4-D) degrading bacteria from geographically diverse locations and presenting various degrees of similarity or no similarity to the tfdA and tfdB genes from Alcaligenes eutrophus JMP134 were analysed by PCR-RFLP (restriction length fragment polymorphism). Primers for the 2,4-D etherase gene were derived by sequence alignment of the tfdA genes from A. eutrophus JMP134 and Burkholderia sp. RASC. Primers for the 2,4-dichlorophenolhydroxylase gene were based on the tfdB gene sequence from A. eutrophus JMP134 by taking codon degeneration and variations in amino acid residue sequences into consideration. PCR amplification using the tfdA primer set produced fragments of 0.3 kb from 17 strains which showed varying degrees of similarity to the tfdA gene probe from A. eutrophus JMP134. Significant variations in the gene sequences were confirmed by PCR-RFLP analysis. DNA amplification using the tfdB primer set produced a 1.1 kb fragment from 19 strains. Amongst them, two did not show any similarity to the tfdB gene probe. The size and restriction pattern of the products obtained from A. eutrophus JMP134 were in accordance with the expected size calculated from the A. eutrophus tfdA and tfdB gene sequence and their theoretical PCR-RFLP patterns. Some strains which did not amplify using the tfdA primer set did however amplify with the tfdB primer set. These results suggest the independent evolution of these two genes in the construction of the 2,4-D metabolic pathway. Our tfdA and tfdB primer sets could be used for the detection of similar sequences in bacteria and soils. Moreover, PCR-RFLP patterns could also be used to select subsets of strains for sequencing to study the phylogeny of the tfdA and tfdB genes.     

Chlorophenol hydroxylases encoded by plasmid pJP4 differentially contribute to chlorophenoxyacetic acid degradation

Phenoxyalkanoic compounds are used worldwide as herbicides. Cupriavidus necator JMP134(pJP4) catabolizes 2,4-dichlorophenoxyacetate (2,4-D) and 4-chloro-2-methylphenoxyacetate (MCPA), using tfd functions carried on plasmid pJP4. TfdA cleaves the ether bonds of these herbicides to produce 2,4-dichlorophenol (2,4-DCP) and 4-chloro-2-methylphenol (MCP), respectively. These intermediates can be degraded by two chlorophenol hydroxylases encoded by the tfdB(I) and tfdB(II) genes to produce the respective chlorocatechols. We studied the specific contribution of each of the TfdB enzymes to the 2,4-D/MCPA degradation pathway. To accomplish this, the tfdB(I) and tfdB(II) genes were independently inactivated, and growth on each chlorophenoxyacetate and total chlorophenol hydroxylase activity were measured for the mutant strains. The phenotype of these mutants shows that both TfdB enzymes are used for growth on 2,4-D or MCPA but that TfdB(I) contributes to a significantly higher extent than TfdB(II). Both enzymes showed similar specificity profiles, with 2,4-DCP, MCP, and 4-chlorophenol being the best substrates. An accumulation of chlorophenol was found to inhibit chlorophenoxyacetate degradation, and inactivation of the tfdB genes enhanced the toxic effect of 2,4-DCP on C. necator cells. Furthermore, increased chlorophenol production by overexpression of TfdA also had a negative effect on 2,4-D degradation by C. necator JMP134 and by a different host, Burkholderia xenovorans LB400, harboring plasmid pJP4. The results of this work indicate that codification and expression of the two tfdB genes in pJP4 are important to avoid toxic accumulations of chlorophenols during phenoxyacetic acid degradation and that a balance between chlorophenol-producing and chlorophenol-consuming reactions is necessary for growth on these compounds.     

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.     

Characterization of (R/S)-mecoprop [2-(2-methyl-4-chlorophenoxy) propionic acid]-degrading Alcaligenes sp.CS1 and Ralstonia sp. CS2 isolated from agricultural soils

The herbicide mecoprop [2-(2-methyl-4-chlorophenoxy) propionic acid] is widely applied to corn fields in order to control broad-leaved weeds. However, it is often detected in groundwater where it can be a persistent contaminant. Two mecoprop-degrading bacterial strains were isolated from agricultural soils through their capability to degrade ( R/S )-mecoprop rapidly. 16S rDNA sequencing of the isolates demonstrated that one was closely related to the genera Alcaligenes sp. (designated CS1) and the other to Ralstonia sp. (designated CS2). Additionally, these isolates demonstrated ability to grow on other related herbicides, including 2,4- D (2,4-dichlorophenoxyacetic acid), MCPA [4-chloro-2-methyl phenoxy acetic acid] and ( R/S )-2,4-DP [2-(2,4-dichlorophenoxy)propionic acid] as sole carbon sources. tfdABC gene-specific probes derived from the 2,4- D -degrading Variovorax paradoxus TV1 were used in hybridization analyses to establish whether tfd -like genes are present in mecoprop-degrading bacteria. Hybridization analysis demonstrated that both Alcaligenes sp. CS1 and Ralstonia sp. CS2 harboured tfdA , tfdB and tfdC genes on plasmids that have approximately > 60% sequence similarity to the tfdA , tfdB and tfdC genes of V. paradoxus . It is therefore likely that tfd -like genes may be involved in the degradation of mecoprop, and we are currently investigating this further.     

Capture of a catabolic plasmid that encodes only 2,4-dichlorophenoxyacetic acid:alpha-ketoglutaric acid dioxygenase (TfdA) by genetic complementation.

The modular pathway for the metabolism of 2,4-dichlorophenoxyacetic acid (2,4-D) encoded on plasmid pJP4 of Alcaligenes eutrophus JMP134 appears to be an example in which two genes, tfdA and tfdB, have been recruited during the evolution of a catabolic pathway. The products of these genes act to convert 2,4-D to a chloro-substituted catechol that can be further metabolized by enzymes of a modified ortho-cleavage pathway encoded by tfdCDEF. Given that modified ortho-cleavage pathways are comparatively common and widely distributed among bacteria, we sought to determine if microbial populations in soil carry tfdA on plasmid vectors that lack tfdCDEF or tfdB. To capture such plasmids from soil populations, we used a recipient strain of A. eutrophus that was rifampin resistant and carried a derivative of plasmid pJP4 (called pBH501aE) in which the tfdA had been deleted. Upon mating with mixed bacterial populations from soil treated with 2,4-D, transconjugants that were resistant to rifampin yet able to grow on 2,4-D were obtained. Among the transconjugants obtained were clones that contained a ca. 75-kb plasmid, pEMT8. Bacterial hosts that carried this plasmid in addition to pBH501aE metabolized 2,4-D, whereas strains with only pEMT8 did not. Southern hybridization showed that pEMT8 encoded a gene with a low level of similarity to the tfdA gene from plasmid pJP4. Using oligonucleotide primers based on known tfdA sequences, we amplified a 330-bp fragment of the gene and determined that it was 77% similar to the tfdA gene of plasmid pJP4 and 94% similar to tfdA from Burkholderia sp. strain RASC. Plasmid pEMT8 lacked genes that exhibited significant levels of homology to tfdB and tfdCDEF. Moreover, cell extracts from A. eutrophus(pEMT8) cultures did not exhibit TfdB, TfdC, TfdD, and TfdE activities, whereas cell extracts from A. eutrophus(pEMT8)(pBH501aE) cultures did. These data suggest that pEMT8 encodes only tfdA and that this gene can effectively complement the tfdA deletion mutation of pBH501aE.