The dehalogenase gene dehI from Pseudomonas putida PP3 is carried on an unusual mobile genetic element designated DEH

Transport of haloacids across biological membranes

Haloacids are considered to be environmental pollutants, but some of them have also been tested in clinical research. The way that haloacids are transported across biological membranes is important for both biodegradation and drug delivery purposes. In this review, we will first summarize putative haloacids transporters and the information about haloacids transport when studying carboxylates transporters. We will then introduce MCT1 and SLC5A8, which are respective transporter for antitumor agent 3-bromopyruvic acid and dichloroacetic acid, and monochloroacetic acid transporters Deh4p and Dehp2 from a haloacids-degrading bacterium. Phylogenetic analysis of these haloacids transporters and other monocarboxylate transporters reveals their evolutionary relationships. Haloacids transporters are not studied to the extent that they deserve compared with their great application potentials, thus future inter-discipline research are desired to better characterize their transport mechanisms for potential applications in both environmental and clinical fields.

Interactions between populations ofPseudomonas putida leading to the expression of a cryptic dehalogenase gene (dehll)

In appropriate environments containing 2-monochloropropionic acid (2MCPA), mutations in a population of nondehalogenatingPseudomonas putida, strain PP40-040 (parent population), resulted in the formation of 2mcpa(+) papillae as a result of the decryptification of adehII gene. Increasing the size of the parent population, for example by increasing the availability of a metabolizable substrate such as succinate or lactate, increased the number of 2mcpa(+) papillae formed because there were more parent cells available for mutation to the 2mcpa(+) phenotype. The presence of a dehalogenating population, such asP. putida strain PP3, in close proximity to the non-dehalogenating population, also increased the number of 2mcpa(+) papillae formed. This was due to the excretion of dehalogenases into the growth medium, which caused localized dehalogenation of the available 2MCPA, yielding a metabolizable substrate. This substrate stimulated the growth of the non-dehalogenating population, in turn increasing the number of 2mcpa(+) papillae formed. Barriers, such as dialysis membranes, which prevented the excretion of the dehalogenases into the growth medium, prevented the stimulation of 2mcpa(+) papillae formation by preventing release of metabolizable substrates from 2MCPA breakdown. Cell-free extracts (CFE) from dehalogenase-producing populations had a similar effect for the same reason. CFE without dehalogenase activity or in which the dehalogenase activity had been destroyed by heating failed to stimulate parent population growth and 2mcpa(+) papillae formation. In the case ofPseudomonas putida strain PP3, which carries an easily transposed dehalogenase-encoding transposon, treatment of CFE with DNAase eliminated an additional factor involved in the formation of 2mcpa(+) papillae.

Facilitation of bacterial adaptation to chlorothalonil-contaminated sites by horizontal transfer of the chlorothalonil hydrolytic dehalogenase gene

Horizontal transfer of the chlorothalonil hydrolytic dehalogenase gene (chd) is proposed based on the high conservation of the chd gene and its close association with a novel insertion sequence, ISOcsp1, in 16 isolated chlorothalonil-dechlorinating strains belonging to eight different genera. The ecological role of horizontal gene transfer is assumed to facilitate bacterial adaptation to chlorothalonil-contaminated sites, through detoxification of chlorothalonil to less toxic 2,4,5-trichloro-6-hydroxybenzene-1,3-dicarbonitrile.

Detection and enumeration of haloacetic acid-degrading bacteria in drinking water distribution systems using dehalogenase genes

AIMS

To develop a PCR-based tracking method for the detection of a subset of bacteria in drinking water distribution systems capable of degrading haloacetic acids (HAAs).

METHODS AND RESULTS

Published degenerate PCR primers were used to determine that 54% of tap water samples (7/13) were positive for a deh gene, indicating that drinking water distribution systems may harbour bacteria capable of HAA degradation. As the published primer sets were not sufficiently specific for quantitative PCR, new primers were designed to amplify dehII genes from selected indicator strains. The developed primer sets were effective in directly amplifying dehII genes from enriched consortia samples, and the DNA extracted from tap water provided that an additional nested PCR step for detection of the dehII gene was used.

CONCLUSIONS

This study demonstrates that drinking water distribution systems harbour microbes capable of degrading HAAs. In addition, a quantitative PCR method was developed to detect and quantify dehII genes in drinking water systems.

SIGNIFICANCE AND IMPACT OF THE STUDY

The development of a technique to rapidly screen for the presence of dehalogenase genes in drinking water distribution systems could help water utilities determine if HAA biodegradation is occurring in the distribution system.

Purification, crystallization and preliminary crystallographic analysis of DehI, a group I alpha-haloacid dehalogenase from Pseudomonas putida strain PP3

Pseudomonas putida strain PP3 produces two dehalogenases, DehI and DehII, which belong to the group I and II alpha-haloacid dehalogenases, respectively. Group I dehalogenases catalyse the removal of halides from D-haloalkanoic acids and in some cases also the L-enantiomers, both substituted at their chiral centres. Studies of members of this group have resulted in the proposal of general catalytic mechanisms, although no structural information is available in order to better characterize their function. This work presents the initial stages of the structural investigation of the group I alpha-haloacid dehalogenase DehI. The DehI gene was cloned into a pET15b vector with an N-terminal His tag and expressed in Escherichia coli Nova Blue strain. Purified protein was crystallized in 25% PEG 3350, 0.4 M lithium sulfate and 0.1 M bis-tris buffer pH 6.0. The crystals were primitive monoclinic (space group P2(1)), with unit-cell parameters a = 68.32, b = 111.86, c = 75.13 A, alpha = 90, beta = 93.7, gamma = 90 degrees , and a complete native data set was collected. Molecular replacement is not an option for structure determination, so further experimental phasing methods will be necessary.

Plasmid-encoded gamma-hexachlorocyclohexane degradation genes and insertion sequences in Sphingobium francense (ex-Sphingomonas paucimobilis Sp+)

The lin genes encode the gamma-hexachlorocyclohexane (gamma-HCH or lindane) catabolic pathway in lindane-degrading strains. The location and stability of these genes have been explored in the lindane-degrading Sphingobium francense strain Sp+, and in two non-lindane-degrading mutants (Sp1- and Sp2-). The lin genes, linA, linB, linE and linX were localized by hybridization on three of the six plasmids of the S. francense strain Sp+ showing dispersal within the genome. The linC gene was detected by PCR, but was not detected by hybridization on any of the plasmids. The hybridization of the linA and linX genes was negative with the two non-lindane-degrading mutants S. francense strains, Sp1- and Sp2-. The dynamic of this genome associated with gene loss and acquisition, and plasmid rearrangement was explored by a search for associated insertion sequences. A new insertion sequence, ISSppa4, belonging to the IS21 family was detected and compared with IS6100 and ISsp1. Insertion sequence localization was explored on different hybridization patterns (plasmid, total genome) with the lindane-degrading Sp+ strain and the two non-degrading derivatives (Sp1-, Sp2-). Insertion sequence movement and plasmid rearrangement could explain the emergence of the non-lindane-degrading mutants.

Bacterial degradation of xenobiotic compounds: evolution and distribution of novel enzyme activities

Bacterial dehalogenases catalyse the cleavage of carbon-halogen bonds, which is a key step in aerobic mineralization pathways of many halogenated compounds that occur as environmental pollutants. There is a broad range of dehalogenases, which can be classified in different protein superfamilies and have fundamentally different catalytic mechanisms. Identical dehalogenases have repeatedly been detected in organisms that were isolated at different geographical locations, indicating that only a restricted number of sequences are used for a certain dehalogenation reaction in organohalogen-utilizing organisms. At the same time, massive random sequencing of environmental DNA, and microbial genome sequencing projects have shown that there is a large diversity of dehalogenase sequences that is not employed by known catabolic pathways. The corresponding proteins may have novel functions and selectivities that could be valuable for biotransformations in the future. Apparently, traditional enrichment and metagenome approaches explore different segments of sequence space. This is also observed with alkane hydroxylases, a category of proteins that can be detected on basis of conserved sequence motifs and for which a large number of sequences has been found in isolated bacterial cultures and genomic databases. It is likely that ongoing genetic adaptation, with the recruitment of silent sequences into functional catabolic routes and evolution of substrate range by mutations in structural genes, will further enhance the catabolic potential of bacteria toward synthetic organohalogens and ultimately contribute to cleansing the environment of these toxic and recalcitrant chemicals.

Horizontal transfer of dehalogenase genes on IncP1beta plasmids during bacterial adaptation to degrade alpha-halocarboxylic acids

The diversity of bacterial alpha-halocarboxylic acid (alphaHA) dehalogenases from a polluted soil was investigated. Polymerase chain reaction (PCR) primers designed to amplify group I and group II dehalogenase (deh) gene sequences were used to screen bacterial isolates, nine beta-Proteobacteria and one gamma-Proteobacterium, from soil enrichments. Primers successfully amplified deh sequences from all 10 alphaHA-utilising isolates. Bacteria isolated at 15 or 30 degrees C on chloroacetic acid or 2-chloropropionic acid from the same polluted soil were shown to contain up to four plasmids, some of these common between isolates. Analysis of deletion mutants and Southern hybridisation showed that each isolate contained an apparently identical IncP1beta plasmid c. 80 kb in size, carrying group I deh genes in addition to an associated insertion sequence element. Moreover, an identical conjugative catabolic plasmid was isolated exogenously in several transconjugants independently selected from biparental matings between Ralstonia eutropha JMP222 and enrichment samples. PCR cloning and sequencing of deh genes directly from enrichment cultures inoculated with the same soil revealed that an identical deh gene was present in both primary, secondary and tertiary enrichment cultures, although this deh could not be amplified directly from soil. Two alphaHA-utilising bacteria isolated at lower temperature were found also to contain group II deh genes. Transfer of the deh catabolic phenotype to R. eutropha strain JMP222 occurred at high frequencies for four strains tested, a result that was consistent with assignment of the plasmids to the IncP1 incompatibility group. The promiscuous nature and broad host range of IncP plasmids make them likely to be involved in horizontal gene transfer during adaptation of bacteria to degrade organohalogens.

Diversity of alpha-halocarboxylic acid dehalogenases in bacteria isolated from a pristine soil after enrichment and selection on the herbicide 2,2-dichloropropionic acid (Dalapon)

Five pure cultures of bacteria (strains DA1-5) able to degrade 2,2-dichloropropionic acid (22DCPA) were isolated for the first time from pristine bulk soil samples. From 16S rDNA analysis, it was concluded that strains DA2, DA3 and DA4 were members of the Bradyrhizobium subgroup (alpha-Proteobacteria), strain DA5 clustered in the Brucella assemblage (alpha-Proteobacteria) and strain DA1 clustered in the beta-Proteobacteria. Biochemical and molecular analysis of the dehalogenases from the isolates showed that these enzymes were quite diverse. Several dehalogenases were closely related to group I and II alpha-halocarboxylic acid dehalogenases, and partial polymerase chain reaction (PCR) products were obtained from isolates DA1, 2, 3 and 4 using degenerate dehalogenase primers. However, no PCR products were obtained from isolate DA5 using either of the group I or II alpha-halocarboxylic acid dehalogenase primers. Isolates DA2 and DA4 contained putative silent dehalogenases. The investigation highlighted the endemic nature of these genes in pristine environments and how diverse these were even from spatially close samples.

Complete sequence of the IncP-9 TOL plasmid pWW0 from Pseudomonas putida

The TOL plasmid pWW0 (117 kb) is the best studied catabolic plasmid and the archetype of the IncP-9 plasmid incompatibility group from Pseudomonas. It carries the degradative (xyl) genes for toluenes and xylenes within catabolic transposons Tn4651 and Tn4653. Analysis of the complete pWW0 nucleotide sequence revealed 148 putative open reading frames. Of these, 77 showed similarity to published sequences in the available databases predicting functions for: plasmid replication, stable maintenance and transfer; phenotypic determinants; gene regulation and expression; and transposition. All identifiable transposition functions lay within the boundaries of the 70 kb transposon Tn4653, leaving a 46 kb sector containing all the IncP-9 core functions. The replicon and stable inheritance region was very similar to the mini-replicon from IncP-9 antibiotic resistance plasmid pM3, with their Rep proteins forming a novel group of initiation proteins. pWW0 transfer functions exist as two blocks encoding putative DNA processing and mating pair formation genes, with organizational and sequence similarity to IncW plasmids. In addition to the known Tn4651 and IS1246 elements, two additional transposable elements were identified as well as several putative transposition functions, which are probably genetic remnants from previous transposition events. Genes likely to be responsible for known resistance to ultraviolet light and free radicals were identified. Other putative phenotypic functions identified included resistance to mercury and other metal ions, as well as to quaternary ammonium compounds. The complexity and size of pWW0 is largely the result of the mosaic organization of the transposable elements that it carries, rather than the backbone functions of IncP-9 plasmids.

Transposition of DEH, a broad-host-range transposon flanked by ISPpu12, in Pseudomonas putida is associated with genomic rearrangements and dehalogenase gene silencing

Pseudomonas putida strain PP3 produces two hydrolytic dehalogenases encoded by dehI and dehII, which are members of different deh gene families. The 9.74-kb DEH transposon containing dehI and its cognate regulatory gene, dehR(I), was isolated from strain PP3 by using the TOL plasmid pWW0. DEH was fully sequenced and shown to have a composite transposon structure, within which dehI and dehR(I) were divergently transcribed and were flanked on either side by 3.73-kb identical direct repeats. The flanking repeat unit, designated ISPpu12, had the structure of an insertion sequence in that it was bordered by 24-bp near-perfect inverted repeats and contained four open reading frames (ORFs), one of which was identified as tnpA, putatively encoding an ISL3 family transposase. A putative lipoprotein signal peptidase was encoded by an adjacent ORF, lspA, and the others, ISPpu12 orf1 and orf2, were tentatively identified as a truncated cation efflux transporter gene and a PbrR family regulator gene, respectively. The orf1-orf2 intergenic region contained an exact match with a previously described active, outward-orientated promoter, Pout. Transposition of DEH-ISPpu12 was investigated by cloning the whole transposon into a suicide plasmid donor, pAWT34, and transferring the construct to various recipients. In this way DEH-ISPpu12 was shown to transpose in a broad range of Proteobacteria. Transposition of ISPpu12 independently from DEH, and inverse transposition, whereby the vector DNA and ISPpu12 inserted into the target genome without the deh genes, were also observed to occur at high frequencies in P. putida PaW340. Transposition of a second DEH-ISPpu12 derivative introduced exogenously into P. putida PP3 via the suicide donor pAWT50 resulted in silencing of resident dehI and dehII genes in about 10% of transposition transconjugants and provided a genetic link between transposition of ISPpu12 and dehalogenase gene silencing. Database searches identified ISPpu12-related sequences in several bacterial species, predominantly associated with plasmids and xenobiotic degradative genes. The potential role of ISPpu12 in gene silencing and activation, as well as the adaptation of bacteria to degrade xenobiotic compounds, is discussed.

Occurrence of Tn4371-related mobile elements and sequences in (chloro)biphenyl-degrading bacteria

Tn4371, a 55-kb transposable element involved in the degradation and biphenyl or 4-chlorobiphenyl identified in Ralstonia eutropha A5, displays a modular structure including a phage-like integrase gene (int), a Pseudomonas-like (chloro)biphenyl catabolic gene cluster (bph), and RP4- and Ti-plasmid-like transfer genes (trb) (C. Merlin, D. Springael, and A. Toussaint, Plasmid 41:40-54, 1999). Southern blot hybridization was used to examine the presence of different regions of Tn4371 in a collection of (chloro)biphenyl-degrading bacteria originating from different habitats and belonging to different bacterial genera. Tn4371-related sequences were never detected on endogenous plasmids. Although the gene probes containing only bph sequences hybridized to genomic DNA from most strains tested, a limited selection of strains, all beta-proteobacteria, displayed hybridization patterns similar to the Tn4371 bph cluster. Homology between Tn4371 and DNA of two of those strains, originating from the same area as strain A5, extended outside the catabolic genes and covered the putative transfer region of Tn4371. On the other hand, none of the (chloro)biphenyl degraders hybridized with the outer left part of Tn4371 containing the int gene. The bph catabolic determinant of the two strains displaying homology to the Tn4371 transfer genes and a third strain isolated from the A5 area could be mobilized to a R. eutropha recipient, after insertion into an endogenous or introduced IncP1 plasmid. The mobilized DNA of those strains included all Tn4371 homologous sequences previously identified in their genome. Our observations show that the bph genes present on Tn4371 are highly conserved between different (chloro)biphenyl-degrading hosts, isolated globally but belonging mainly to the beta-proteobacteria. On the other hand, Tn4371-related mobile elements carrying bph genes are apparently only found in isolates from the environment that provided the Tn4371-bearing isolate A5.

Investigation of two evolutionarily unrelated halocarboxylic acid dehalogenase gene families

Dehalogenases are key enzymes in the metabolism of halo-organic compounds. This paper describes a systematic approach to the isolation and molecular analysis of two families of bacterial alpha-halocarboxylic acid (alphaHA) dehalogenase genes, called group I and group II deh genes. The two families are evolutionarily unrelated and together represent almost all of the alphaHA deh genes described to date. We report the design and evaluation of degenerate PCR primer pairs for the separate amplification and isolation of group I and II deh genes. Amino acid sequences derived from 10 of 11 group I deh partial gene products of new and previously reported bacterial isolates showed conservation of five residues previously identified as essential for activity. The exception, DehD from a Rhizobium sp., had only two of these five residues. Group II deh gene sequences were amplified from 54 newly isolated strains, and seven of these sequences were cloned and fully characterized. Group II dehalogenases were stereoselective, dechlorinating L- but not D-2-chloropropionic acid, and derived amino acid sequences for all of the genes except dehII degrees P11 showed conservation of previously identified essential residues. Molecular analysis of the two deh families highlighted four subdivisions in each, which were supported by high bootstrap values in phylogenetic trees and by enzyme structure-function considerations. Group I deh genes included two putative cryptic or silent genes, dehI degrees PP3 and dehI degrees 17a, produced by different organisms. Group II deh genes included two cryptic genes and an active gene, dehIIPP3, that can be switched off and on. All alphaHA-degrading bacteria so far described were Proteobacteria, a result that may be explained by limitations either in the host range for deh genes or in isolation methods.

Mobile catabolic genes in bacteria

The recent findings of various mobile catabolic genes have provided some insight into the evolution of microbial degradation systems for xenobiotic compounds. The catabolic genes undergo marked genetic rearrangements due to their presence on transposons or association with mobile genetic elements. Bacterial catabolic transposons fall into three defined structural classes. Class I elements include catabolic genes flanked by two copies of insertion sequences. Class II elements carry short terminal inverted repeats and transpose by the replicative mode in which transposase and resolvase are involved. Conjugative catabolic transposons represent the third class of mobile genetic elements. They carry all the genes required for excision, conjugal transfer to a new host, and integration. This review focuses on the structures, functions and roles of the recently characterized catabolic transposons in bacteria. Also described are the mobile catabolic elements that share structural similarity with the pathogenicity and symbiosis islands.

Association of newly discovered IS elements with the dichloromethane utilization genes of methylotrophic bacteria

Dichloromethane (DCM) dehalogenases enable facultative methylotrophic bacteria to utilize DCM as sole carbon and energy source. DCM-degrading aerobic methylotrophic bacteria expressing a type A DCM dehalogenase were previously shown to share a conserved 4.2 kb BamHI DNA fragment containing the dehalogenase structural gene, dcmA, and dcmR, the gene encoding a putative regulatory protein. Sequence analysis of a 10 kb DNA fragment including this region led to the identification of three types of insertion sequences identified as IS1354, IS1355 and IS1357, and also two ORFs, orf353 and orf192, of unknown function. Two identical copies of element IS1354 flank the conserved 4.2 kb fragment as a direct repeat. The occurrence of these newly identified IS elements was shown to be limited to DCM-utilizing methylotrophs containing a type A DCM dehalogenase. The organization of the corresponding dcm regions in 12 DCM-utilizing strains was examined by hybridization analysis using IS-specific probes. Six different groups could be defined on the basis of the occurrence, position and copy number of IS sequences. All groups shared a conserved 5.6 kb core region with dcmA, dcmR, orf353 and orf192 as well as IS1357. One group of strains including Pseudomonas sp. DM1 contained two copies of this conserved core region. The high degree of sequence conservation observed within the genomic region responsible for DCM utilization and the occurrence of clusters of insertion sequences in the vicinity of the dcm genes suggest that a transposon is involved in the horizontal transfer of the DCM-utilization character among methylotrophic bacteria.

The plasmid-located haloalkane dehalogenase gene from Rhodococcus rhodochrous NCIMB 13064

The haloalkane dehalogenase (dhaA) gene from Rhodococcus rhodochrous NCIMB 13064 was cloned and sequenced. Its comparison with the previously studied dhlA gene from Xanthobacter autotrophicus GJ10 did not show homology. However, the amino acid sequences of the products of these genes showed approximately 30% identity and several of the catalytic amino acid residues were conserved in the NCIMB 13,064 dehalogenase. A high level of dhaA expression was demonstrated in Escherichia coli cells and this gene was shown to encode a dehalogenase with the activity against chloroalkanes of chain length C3-C10. Also, some dehalogenase activity against 1,2-dichloroethane encoded by the cloned dhaA gene was detected. The analysis of NCIMB 13,064 derivatives lacking dehalogenase activity showed that the dhaA gene was located on the 100 kbp pRTL1 plasmid. It was also found that reversible rearrangements of DNA in the dhaA region may be responsible for the control of expression of haloalkane dehalogenase in R. rhodochrous NCIMB 13064. A number of repeated and inverted sequences which may cause genetic instability at the locus were found in the haloalkane dehalogenase gene region.

Cloning and nucleotide sequence of a D,L-haloalkanoic acid dehalogenase encoding gene from Alcaligenes xylosoxidans ssp. denitrificans ABIV

We have cloned DNA fragments of plasmid pFL40 from Alcaligenes xylosoxidans ssp. denitrificans ABIV encoding a D,L-2-haloalkanoic acid halidohydrolase (DhlIV). A 6.5-kb EcoRI/SalI-fragment with inducible expression of the halidohydrolase was cloned in Pseudomonas fluorescens and Escherichia coli. A 1.9-kb HindII-fragment demonstrated expression of the dehalogenase only due to the presence of the promoter from the pUC vector in Escherichia coli. The nucleotide sequence of this DNA-fragment was determined. It had an open reading frame coding for 296 amino acid residues (molecular weight of 32783 D). The dhlIV gene showed sequence homology to a short segment of a D-specific dehalogenase (hadD) from Pseudomonas putida AJ1, but not to any other known DNA sequences. Restriction enzyme patterns indicated similarity between dhlIV and the D,L- isomer specific dehl dehalogenase gene from Pseudomonas putida PP3. There are some indications from restriction enzyme patterns and initial sequencing data, that a gene encoding a sigma 54-dependent activator protein, similar to the dehRI regulatory gene from Pseudomonas putida PP3 is located upstream of dhlIV. In contrast to DehI, dehalogenation of D- or L-chloropropionic acid by the DhlIV-protein leads to lactic acid of inverted configuration.

The nucleotide sequence of a transposable haloalkanoic acid dehalogenase regulatory gene (dehRI) from Pseudomonas putida strain PP3 and its relationship with sigma 54-dependent activators

The mobile genetic element, DEH found in Pseudomonas putida PP3 carries a 2-haloalkanoic acid dehalogenase structural gene, dehI, and its associated regulatory gene, dehRI. The nucleotide sequence of dehRI was determined. The gene had an open reading frame putatively encoding for a 64 kDa protein containing 571 amino acid residues. The protein was similar to previously published sequences of several other sigma 54-dependent activator proteins. Amino acid sequence analysis showed that the deduced DehRI protein clustered with the NifA nitrogenase regulatory activator family, and was most closely related, with 47.7% similarity, to a 'NifA-like' deduced partial sequence from a plasmid-encoded ORF in Pseudomonas sp. strain NS671, associated with L-amino acid production. The domain structure of DehRI was analysed by alignment with other NifA-like and NtrC-like sequences and showed a highly conserved central region of approximately 230 amino acids, and a potential DNA-binding domain. No homology was detected between the deduced DehRI and other sigma 54-dependent activator sequences at the N-terminus, a result which was consistent with that region being the domain which recognised inducer.

Overexpression and feasible purification of thermostable L-2-halo acid dehalogenase of Pseudomonas sp. YL

The gene encoding thermostable L-2-halo acid dehalogenase of Pseudomonas sp. YL was isolated, and its overexpression system was constructed. Gene library was prepared from Sau3AI fragments of total DNA from Ps. sp. YL, pUC118 as a vector and Escherichia coli JM109 as a host. The recombinant cells resistant to bromoacetate, a germicide, were isolated and shown to produce L-2-halo acid dehalogenase. Subsequently, subcloning was carried out with pKK223-3 as a vector, and the length of DNA inserted was reduced to 1.1 kbp. One of the subclones showed very high activity, and the amount of the dehalogenase produced corresponded to about 30% of the soluble protein. From 5 g (wet weight) of cells, 105 mg of dehalogenase was efficiently purified by heat treatment and DEAE-Toyopearl chromatography. This overexpression system provides a large amount of the thermostable enzyme to enable us to study the properties, structure and application of the enzyme.

Adaptation of Xanthobacter autotrophicus GJ10 to bromoacetate due to activation and mobilization of the haloacetate dehalogenase gene by insertion element IS1247

Monobromoacetate (MBA) is toxic for the 1,2-dichloroethane-degrading bacterium Xanthobacter autotrophicus GJ10 at concentrations higher than 5 mM. Mutants which are able to grow on higher concentrations of MBA were isolated and found to overexpress haloacid dehalogenase, which is encoded by the dhlB gene. In mutant GJ10M50, a DNA fragment (designated IS1247) had copied itself from a position on the chromosome that was not linked to the dhlB region to a site immediately upstream of dhlB, resulting in a 1,672-bp insertion. IS1247 was found to encode an open reading frame corresponding to 464 amino acids which showed similarity to putative transposases from two other insertion elements. In most of the other MBA-resistant mutants of GJ10, IS1247 was also present in one more copy than in the wild type, which had two copies located within 20 kb. After insertion to a site proximal to dhlB, IS1247 was able to transpose itself together with the dhlB gene to a plasmid, without the requirement of a second insertion element being present downstream of dhlB. The results show that IS1247 causes bromoacetate resistance by overexpression and mobilization of the haloacid dehalogenase gene, which mimics steps during the evolution of a catabolic transposon and plasmid during adaptation to a toxic growth substrate.

Cryptic dehalogenase and chloroamidase genes in Pseudomonas putida and the influence of environmental conditions on their expression

Mutants of two strains of Pseudomonas putida expressed two cryptic chloroamidases (C-amidase and H-amidase) and one cryptic dehalogenase (DehII). The mutants were selected on either 2-chloropropionamide (2CPA) or 2-monochloropropionate (2MCPA), developing as papillae in parental colonies growing on a metabolisable support substrate. Mutants expressing C-amidase were selected if 2CPA was utilised as either a carbon or a nitrogen source. H-amidase mutants were selected only if 2CPA was used as a nitrogen source. Growth temperature and pH affected the frequency of papillae production, although different temperatures and pHs did not affect the overall growth characteristics of the parental colonies. Decreasing growth temperature increased the frequency of 2cpa+ papillae formation, but decreased the frequency of 2mcpa+ papillae formation. Low pH (6.0) prevented the formation of 2mcpa+ and 2cpa+ papillae. However, in the case of the 2cpa+ papillae, decreasing the growth temperature also allowed papillae formation at pH 6.0.

Catabolic transposons

The structure and function of transposable elements that code for catabolic pathways involved in the biodegradation of organic compounds are reviewed. Seven of these catabolic transposons have structural features that place them in the Class I (composite) or Class II (Tn3-family) bacterial elements. One is a conjugative transposon. Another three have been found to have properties of transposable elements but have not been characterized sufficiently to assign to a known class. Structural features of the toluene (Tn4651/Tn4653) and naphthalene (Tn4655) elements that illustrate the enormous potential for acquisition, deletion and rearrangement of DNA within catabolic transposons are discussed. The recently characterized chlorobenzoate (Tn5271) and chlorobenzene (Tn5280) catabolic transposons encode different aromatic ring dioxygenases, however they both illustrate the constraints that must be overcome when recipients of catabolic transposons assemble and regulate complete metabolic pathways for environmental pollutants. The structures of the chlorobenzoate catabolic transposon Tn5271 and the related haloacetate dehalogenase catabolic element of plasmid pUO1 are compared and a hypothesis for their formation is discussed. The structures and activities of catabolic transposons of unknown class coding for the catabolism of halogenated alkanoic acids (DEH) and chlorobiphenyl (Tn4371) are also reviewed.

The evolution of pathways for aromatic hydrocarbon oxidation in Pseudomonas

The organisation and nucleotide sequences coding for the catabolism of benzene, toluene (and xylenes), naphthalene and biphenyl via catechol and the extradiol (meta) cleavage pathway in Pseudomonas are reviewed and the various factors which may have played a part in their evolution are considered. The data suggests that the complete pathways have evolved in a modular way probably from at least three elements. The common meta pathway operons, downstream from the ferredoxin-like protein adjacent to the gene for catechol 2,3-dioxygenase, are highly homologous and clearly share a common ancestry. This common module may have become fused to a gene or genes the product(s) of which could convert a stable chemical (benzoate, salicylate, toluene, benzene, phenol) to catechol, thus forming the lower pathway operons found in modern strains. The upper pathway operons might then have been acquired as a third module at a later stage thus increasing the catabolic versatility of the host strains.

Bacterial dehalogenases: biochemistry, genetics, and biotechnological applications

This review is a survey of bacterial dehalogenases that catalyze the cleavage of halogen substituents from haloaromatics, haloalkanes, haloalcohols, and haloalkanoic acids. Concerning the enzymatic cleavage of the carbon-halogen bond, seven mechanisms of dehalogenation are known, namely, reductive, oxygenolytic, hydrolytic, and thiolytic dehalogenation; intramolecular nucleophilic displacement; dehydrohalogenation; and hydration. Spontaneous dehalogenation reactions may occur as a result of chemical decomposition of unstable primary products of an unassociated enzyme reaction, and fortuitous dehalogenation can result from the action of broad-specificity enzymes converting halogenated analogs of their natural substrate. Reductive dehalogenation either is catalyzed by a specific dehalogenase or may be mediated by free or enzyme-bound transition metal cofactors (porphyrins, corrins). Desulfomonile tiedjei DCB-1 couples energy conservation to a reductive dechlorination reaction. The biochemistry and genetics of oxygenolytic and hydrolytic haloaromatic dehalogenases are discussed. Concerning the haloalkanes, oxygenases, glutathione S-transferases, halidohydrolases, and dehydrohalogenases are involved in the dehalogenation of different haloalkane compounds. The epoxide-forming halohydrin hydrogen halide lyases form a distinct class of dehalogenases. The dehalogenation of alpha-halosubstituted alkanoic acids is catalyzed by halidohydrolases, which, according to their substrate and inhibitor specificity and mode of product formation, are placed into distinct mechanistic groups. beta-Halosubstituted alkanoic acids are dehalogenated by halidohydrolases acting on the coenzyme A ester of the beta-haloalkanoic acid. Microbial systems offer a versatile potential for biotechnological applications. Because of their enantiomer selectivity, some dehalogenases are used as industrial biocatalysts for the synthesis of chiral compounds. The application of dehalogenases or bacterial strains in environmental protection technologies is discussed in detail.

Transfer and expression of PCB-degradative genes into heavy metal resistant Alcaligenes eutrophus strains

Sites polluted with organic compounds frequently contain inorganic pollutants such as heavy metals. The latter might inhibit the biodegradation of the organics and impair bioremediation. Chromosomally located polychlorinated biphenyl (PCB) catabolic genes of Alcaligenes eutrophus A5, Achromobacter sp. LBS1C1 and Alcaligenes denitrificans JB1 were introduced into the heavy metal resistant Alcaligenes eutrophus strain CH34 and related strains by means of natural conjugation. Mobile elements containing the PCB catabolic genes were transferred from A. eutrophus A5 and Achromobacter sp. LB51C1 into A. eutrophus CH34 after transposition onto their endogenous IncP plasmids pSS50 and pSS60, respectively. The PCB catabolic genes of A. denitrificans JB1 were transferred into A. eutrophus CH34 by means of RP4::Mu3A mediated prime plasmid formation. The A. eutrophus CH34 transconjugant strains expressed both catabolic and metal resistance markers. Such constructs may be useful for the decontamination of sites polluted by both organics and heavy metals.

Genetic adaptation of bacteria to chlorinated aromatic compounds

Genetic mechanisms in bacteria provide a continuous source of alterations in DNA sequences that may lead to favourable adaptations. Bacteria that use chlorinated aromatics as sole carbon and energy sources show evidence of these different genetic alterations. The distinct effects of single base-pair mutations on adaptation of bacterial strains (e.g. by changing the substrate specificity of a key metabolic enzyme or regulator protein) have been demonstrated in various studies. In addition to these small sequence modifications, intermolecular or intercellular gene exchange mechanisms can result in new strains with altered metabolic capabilities. The details of these evolutionary processes with respect to the metabolism of chlorobenzenes and chlorocatechols are reviewed in this manuscript.

Degradation of halogenated aliphatic compounds: the role of adaptation

A limited number of halogenated aliphatic compounds can serve as a growth substrate for aerobic microorganisms. Such cultures have (specifically) developed a variety of enzyme systems to degrade these compounds. Dehalogenations are of critical importance. Various heavily chlorinated compounds are not easily biodegraded, although there are no obvious biochemical or thermodynamic reasons why microorganisms should not be able to grow with any halogenated compound. The very diversity of catabolic enzymes present in cultures that degrade halogenated aliphatics and the occurrence of molecular mechanisms for genetic adaptation serve as good starting points for the evolution of catabolic pathways for compounds that are currently still resistant to biodegradation.

Molecular mechanisms of genetic adaptation to xenobiotic compounds

Microorganisms in the environment can often adapt to use xenobiotic chemicals as novel growth and energy substrates. Specialized enzyme systems and metabolic pathways for the degradation of man-made compounds such as chlorobiphenyls and chlorobenzenes have been found in microorganisms isolated from geographically separated areas of the world. The genetic characterization of an increasing number of aerobic pathways for degradation of (substituted) aromatic compounds in different bacteria has made it possible to compare the similarities in genetic organization and in sequence which exist between genes and proteins of these specialized catabolic routes and more common pathways. These data suggest that discrete modules containing clusters of genes have been combined in different ways in the various catabolic pathways. Sequence information further suggests divergence of catabolic genes coding for specialized enzymes in the degradation of xenobiotic chemicals. An important question will be to find whether these specialized enzymes evolved from more common isozymes only after the introduction of xenobiotic chemicals into the environment. Evidence is presented that a range of genetic mechanisms, such as gene transfer, mutational drift, and genetic recombination and transposition, can accelerate the evolution of catabolic pathways in bacteria. However, there is virtually no information concerning the rates at which these mechanisms are operating in bacteria living in nature and the response of such rates to the presence of potential (xenobiotic) substrates. Quantitative data on the genetic processes in the natural environment and on the effect of environmental parameters on the rate of evolution are needed.

A plant selectable marker gene based on the detoxification of the herbicide dalapon

A gene from Pseudomonas putida coding for a dehalogenase capable of degrading 2,2 dichloropropionic acid (2,2DCPA), the active ingredient of the herbicide dalapon, has been isolated and characterised. In plant transformation experiments the gene was shown to confer resistance to 2,2DCPA at a tissue culture level where 2,2DCPA could be used to select for transformants. At the whole plant level, transformed plants showed resistance to 2,2DCPA at concentrations up to 5 times the recommended dose rate of dalapon when it was sprayed on their leaves. At lower concentrations, the herbicide caused a non-lethal yellowing of sensitive plants which clearly distinguished them from resistant plants. The mode of action of chlorinated aliphatic acids is not known but they probably affect many enzyme pathways. The results described here are the first example of engineering a plant resistant to a herbicide that does not have one specific enzyme as its target site. This gene has several advantages as a marker in plant breeding and genetic studies. For example, the herbicide is readily available and has low toxicity, transformants can be selected at both the tissue culture and the whole plant level, a large number of transformed plants can easily be screened even in the field, and there is a very low probability of selecting spontaneous mutants.

Environmentally directed mutations in the dehalogenase system of Pseudomonas putida strain PP3

Favourable mutations involving the two dehalogenases (DehI and DehII) of Pseudomonas putida PP3 and derivative strains containing the cloned gene for DehI (dehI) occurred in response to specific environmental conditions, namely: starvation conditions; the presence of dehalogenase substrates (halogenated alkanoic acids--HAAs) which were toxic to P. putida; and/or the presence of a potential growth substrate. Fluctuation tests showed that these mutations were environmentally directed by the presence of HAAs. The mutations were associated with complex DNA rearrangements involving the movement of dehI located on a transposon DEH. Some mutations resulted in switching off the expression of either one or both of the dehalogenases, events which were effective in protecting P. putida from toxic compounds in its growth environment. Other mutations partially restored P. putida's dehalogenating capability under conditions where toxic substrates were absent. Restoration of the capability to untilize HAAs was favoured when normal growth substrates were present in the environment.

Localization and functional analysis of structural and regulatory dehalogenase genes carried on DEH from Pseudomonas putida PP3

Pseudomonas putida PP3 expressed two dehalogenases, DehI and DehII. The DehI gene (dehI) was located on a mobile DNA element (DEH) which inserted at high frequencies into target plasmids from its chromosomal location. From a recombinant TOL plasmid (pWW0) containing a 6.0-kb DEH element inserted into the plasmid's 5.6-kb EcoRI-G restriction endonuclease fragment, an 11.6-kb EcoRI fragment was cloned. Subcloning analysis and insertion mutagenesis produced a structural map of the DEH element and located the dehalogenase functions. The gene dehI was transcribed from a regulated promoter on DEH which was expressed in P. putida and Escherichia coli. The direction of transcription of dehI was determined, and it was also found to be under positive control, activated by an adjacent regulatory gene (dehRI). Expression of dehI in clones containing the intact DEH supported good growth on 2-monochloropropionate (2MCPA). Subclones lacking dehRI expressed dehI at levels which allowed only slow growth on 2MCPA, even when dehI expression was initiated from vector promoters. Expression of dehI in P. putida containing the intact DEH element required rpoN, suggesting that it was omega 54 dependent. The intact DEH element transferred to P. putida on a suicide plasmid donor pAWT34 (pBR325 replicon), and dehI was stably inherited, without vector DNA sequences, in transformants selected on 2MCPA. This indicated that the cloned DEH element contained functions associated with recombination.