Direct phenotypic and genotypic detection of a recombinant pseudomonad population released into lake water.

As a system for studying the fate of genetically engineered microorganisms in the environment, we have previously constructed recombinant plasmids encoding a xylE marker gene (C. Winstanley, J. A. W. Morgan, R. W. Pickup, J. G. Jones, and J. R. Saunders, Appl. Environ. Microbiol. 55:771-777, 1989). A series of direct membrane filter methods have been developed which facilitate the detection of bacterial cells harboring the xylE gene, its product, catechol 2,3-dioxygenase, and catechol 2,3-dioxygenase enzyme activity directly from water samples. These methods enable detection of recombinant populations at concentrations as low as 10(3) to 10(4) cells ml of lake water-1. Direct detection facilitates ecological studies of a range of bacterial strains containing the marker system in aquatic environments. The fate of a recombinant pseudomonad population in lake water was assessed by a combination of colony-forming ability, direct counts, and direct detection of the xylE gene and phenotypic expression of its product.     

Differential regulation of lambda pL and pR promoters by a cI repressor in a broad-host-range thermoregulated plasmid marker system.

Plasmid systems with unique markers were constructed to assess the fate of recombinant DNA and genetically manipulated bacteria in soil and freshwater model environments. On such constructs the marker gene, xylE (for catechol 2,3-dioxygenase), is expressed from the lambda promoter pL or pR, each of which is controlled by the temperature-sensitive lambda repressor c1857. Combinations of these elements were cloned into the broad-host-range plasmid pKT230 to form pLV1010 (pL-xylE), pLV1011 (pL-xylE-c1857), and pLV1013 (pR-xylE-c1857). The recombinant plasmids were introduced into different gram-negative bacteria. The thermoregulated system of pLV1013 functioned well in a range of species, with xylE induction being readily achieved by elevation of the temperature from 28 to 37 degrees C. There was a difference in the induction of catechol 2,3-dioxygenase activity, depending on whether xylE was expressed from pL (pLV1011) or pR (pLV1013). Our observations on testing the different systems in a number of hosts suggest that genes carried by the DNA of genetically engineered microorganisms may not be expressed in a predictable manner following transfer from the release host to other species.     

Differential regulation of lambda pL and pR promoters by a cI repressor in a broad-host-range thermoregulated plasmid marker system

Plasmid systems with unique markers were constructed to assess the fate of recombinant DNA and genetically manipulated bacteria in soil and freshwater model environments. On such constructs the marker gene, xylE (for catechol 2,3-dioxygenase), is expressed from the lambda promoter pL or pR, each of which is controlled by the temperature-sensitive lambda repressor c1857. Combinations of these elements were cloned into the broad-host-range plasmid pKT230 to form pLV1010 (pL-xylE), pLV1011 (pL-xylE-c1857), and pLV1013 (pR-xylE-c1857). The recombinant plasmids were introduced into different gram-negative bacteria. The thermoregulated system of pLV1013 functioned well in a range of species, with xylE induction being readily achieved by elevation of the temperature from 28 to 37 degrees C. There was a difference in the induction of catechol 2,3-dioxygenase activity, depending on whether xylE was expressed from pL (pLV1011) or pR (pLV1013). Our observations on testing the different systems in a number of hosts suggest that genes carried by the DNA of genetically engineered microorganisms may not be expressed in a predictable manner following transfer from the release host to other species.     

Green fluorescent protein as a molecular marker in microbiology

Molecular markers such as: lacZ (b-galactosidase), xylE (catechol 2,3-dioxygenase), lux (bacterial luciferase), luc (insect luciferase), phoA (alkaline phosphatase), gusA and gurA (beta-glucuronidase), gfp (green fluorescent protein), bla (beta-lactamase) and other antibiotic resistance markers, heavy metals resistance genes are commonly used in environmental microorganisms research (Errampaii et al., 1998; Kohler et al., 1999). Most of these markers require one or more substrates, complex media and/or expensive equipment for detection. The gfp gene is widely used as a marker because of its very useful properties such as high stability, minimal toxicity, non-invasive detection and the ability to generate the green light without addition of external cofactors and without application of expensive equipment. Various applications of that reporter gene were showed starting from monitoring of microorganism's survival in complex biological systems such as activated sludge to biodegradation of chemical compounds in soil. GFP allowed the detection, determination of spatial location and enumeration of bacterial cells from diverse environmental samples such as biofilm and water. The gfp as a biomarker was very useful in monitoring of gene expression and protein localisation in bacterial cells, too. The techniques with using gfp marker promise to supply a better understanding of environmental processes. It can make possible to use that knowledge in designing more effective and more efficient methods of biodegradation of toxic compounds from different environments.     

Streptomyces marker plasmids for monitoring survival and spread of streptomycetes in soil.

Plasmid constructs pNW1 through pNW6 containing a controllable xylE gene (for catechol 2,3-dioxygenase) were introduced into Streptomyces lividans strains to provide a selectable marker system. xylE functions in S. lividans under the control of bacteriophage lambda promoters lambda pL and lambda pR. Thermoregulated expression of xylE is provided through the lambda repressor cI857. Catechol 2,3-dioxygenase activity was increased 2.8-fold from plasmid construct pNW2 (lambda pL, xylE, cI857) and 9.5- and 7.4-fold from constructs pNW3 (lambda pR, xylE, cI857) and pNW5 (lambda pR, xylE, cI857), respectively, when the temperature was shifted from 28 degrees C to 37 degrees C. The stability of the constructs varied from 4.7% for pNW2 to 99.4% for pNW4 (lambda pL, xylE) over two rounds of sporulation. Marked S. lividans strains released into soil systems retained the XylE phenotype for more than 80 days, depending on the marker plasmid, when examined by a selective plating method. Furthermore, S. lividans harboring plasmid pNW5 was detectable by nucleic acid hybridization at less than 10 CFU g-1 (dry weight) of soil as mycelium and 10(3) CFU g-1 (dry weight) of soil as spores with the xylE marker DNA extracted from soil and amplified by using the polymerase chain reaction.     

Streptomyces marker plasmids for monitoring survival and spread of streptomycetes in soil.

Plasmid constructs pNW1 through pNW6 containing a controllable xylE gene (for catechol 2,3-dioxygenase) were introduced into Streptomyces lividans strains to provide a selectable marker system. xylE functions in S. lividans under the control of bacteriophage lambda promoters lambda pL and lambda pR. Thermoregulated expression of xylE is provided through the lambda repressor cI857. Catechol 2,3-dioxygenase activity was increased 2.8-fold from plasmid construct pNW2 (lambda pL, xylE, cI857) and 9.5- and 7.4-fold from constructs pNW3 (lambda pR, xylE, cI857) and pNW5 (lambda pR, xylE, cI857), respectively, when the temperature was shifted from 28 degrees C to 37 degrees C. The stability of the constructs varied from 4.7% for pNW2 to 99.4% for pNW4 (lambda pL, xylE) over two rounds of sporulation. Marked S. lividans strains released into soil systems retained the XylE phenotype for more than 80 days, depending on the marker plasmid, when examined by a selective plating method. Furthermore, S. lividans harboring plasmid pNW5 was detectable by nucleic acid hybridization at less than 10 CFU g-1 (dry weight) of soil as mycelium and 10(3) CFU g-1 (dry weight) of soil as spores with the xylE marker DNA extracted from soil and amplified by using the polymerase chain reaction.     

A vital staining method for measuring the efficiency of transfection of eucaryotic cells

The xylE gene encodes catechol 2,3-dioxygenase, which catalyzes the conversion of catechol to 2-hydroxymuconic semialdehyde. The expression of this gene in eucaryotic cells can be detected simply by addition of catechol to the growth medium of the cells: cells that have a sufficient level of expression of the xylE gene stain yellow because of the accumulation of 2-hydroxymuconic semialdehyde. The number of stained cells is thus dependent upon the transfection efficiency as well as the level of expression of the xylE gene and is a measure of the combined transfection/expression efficiency in a particular cell type. Since the staining procedure does not affect the viability of the culture, the cells can be harvested afterward and analyzed for the expression of other, cotransfected, genes. This system for measuring transfection efficiency is especially useful when only small amounts of tissue are available.     

Detection and quantification of degradative genes in soils contaminated by toluene

Abstract: A method based on the polymerase chain reaction (PCR) was developed for a rapid and specific detection of toluene degradative genes in soil. The xylE gene coding for catechol 2,3-dioxygenase was chosen as a target gene. The detection threshold was evaluated in microcosms using a sterilized standard soil inoculated with various amounts of a degradative strain of Pseudomonas putida (mX). The extracted DNA was used as a template to amplify the xylE gene. PCR followed by hybridization with an internal probe allowed us to detect 10² bacteria per g of soil. In polluted soils, quantification of target DNA by competitive PCR was compared with enumeration of degradative microflora. This molecular method appeared to be rapid, sensitive and more suitable than the microbiological approach to estimate the biodegradative potential of a polluted soil.     

Use of a xylE marker gene to monitor survival of recombinant Pseudomonas putida populations in lake water by culture on nonselective media

IncQ marker plasmids were previously constructed to enable the analysis of the survival of populations of Pseudomonas putida released into lake water (C. Winstanley, J. A. W. Morgan, R. W. Pickup, J. G. Jones, and J. R. Saunders, Appl. Environ. Microbiol. 55:771-777, 1989). We constructed equivalent IncP plasmids, pLV1016 and pLV1017, to provide conjugative alternative systems. Detection of the xylE gene carried by marker plasmids was found to be a valid indicator to use for studying the survival of released populations by culturing on nonselective media. These plasmids were used to study the survival of populations of Pseudomonas putida in both sterile and untreated lake water. The effects of inoculum size, the metabolic burden imposed on the cell by the unregulated expression of xylE, and an auxotrophic mutation carried by the host strain were studied. We also assessed the reproducibility and hence the predictability of the survival of released populations. Model systems with a single lake water sample and model systems with three different lake water samples, taken from the same site in consecutive months, were used to analyze variability between replicates and to assess differences caused by host strain or water sample. A large variability was found depending on which water sample was used. These findings imply that it will be difficult to predict accurately the survival of released populations in the natural environment.     

Use of a xylE marker gene to monitor survival of recombinant Pseudomonas putida populations in lake water by culture on nonselective media.

IncQ marker plasmids were previously constructed to enable the analysis of the survival of populations of Pseudomonas putida released into lake water (C. Winstanley, J. A. W. Morgan, R. W. Pickup, J. G. Jones, and J. R. Saunders, Appl. Environ. Microbiol. 55:771-777, 1989). We constructed equivalent IncP plasmids, pLV1016 and pLV1017, to provide conjugative alternative systems. Detection of the xylE gene carried by marker plasmids was found to be a valid indicator to use for studying the survival of released populations by culturing on nonselective media. These plasmids were used to study the survival of populations of Pseudomonas putida in both sterile and untreated lake water. The effects of inoculum size, the metabolic burden imposed on the cell by the unregulated expression of xylE, and an auxotrophic mutation carried by the host strain were studied. We also assessed the reproducibility and hence the predictability of the survival of released populations. Model systems with a single lake water sample and model systems with three different lake water samples, taken from the same site in consecutive months, were used to analyze variability between replicates and to assess differences caused by host strain or water sample. A large variability was found depending on which water sample was used. These findings imply that it will be difficult to predict accurately the survival of released populations in the natural environment.     

Chloroplast-type ferredoxin involved in reactivation of catechol 2,3-dioxygenase from Pseudomonas sp. S 47

Pseudomonas sp. S-47 is capable of degrading catechol and 4-chlorocatechol via the meta-cleavage pathway. XylTE products catalyze the dioxygenation of the aromatics. The xylT of the strain S-47 is located just upstream of the xylE gene. XylT is a typical chloroplast-type ferredoxin, which is characterized by 4 cystein residues that are located at positions 41, 46, 49, and 81. The chloroplast-type ferredoxin of Pseudomonas sp. S-47 exhibited a 98% identity with that of P. putida mt-2 (TOL plasmid) in the amino acid sequence, but only about a 40 to 60% identity with the corresponding enzymes from other organisms. We constructed two recombinant plasmids (pRES1 containing xylTE and pRES101 containing xylE without xylT) in order to examine the function of XylT for the reactivation of the catechol 2,3-dioxygenase (XylE) that is oxidized with hydrogen peroxide. The pRES1 that was treated with hydrogen peroxide was recovered in the catechol 2,3-dioxygenase (C23O) activity about 4 minutes after incubation, but the pRES101 showed no recovery. That means that the typical chloroplast-type ferredoxin (XylT) of Pseudomonas sp. S-47 is involved in the reactivation of the oxidized C23O in the dioxygenolytic cleavage of aromatic compounds.     

Alternative primer sets for PCR detection of genotypes involved in bacterial aerobic BTEX degradation: distribution of the genes in BTEX degrading isolates and in subsurface soils of a BTEX contaminated industrial site

Eight new primer sets were designed for PCR detection of (i) mono-oxygenase and dioxygenase gene sequences involved in initial attack of bacterial aerobic BTEX degradation and of (ii) catechol 2,3-dioxygenase gene sequences responsible for meta-cleavage of the aromatic ring. The new primer sets allowed detection of the corresponding genotypes in soil with a detection limit of 10(3)-10(4) or 10(5)-10(6) gene copies g(-1) soil, assuming one copy of the gene per cell. The primer sets were used in PCR to assess the distribution of the catabolic genes in BTEX degrading bacterial strains and DNA extracts isolated from soils sampled from different locations and depths (vadose, capillary fringe and saturated zone) within a BTEX contaminated site. In both soil DNA and the isolates, tmoA-, xylM- and xylE1-like genes were the most frequently recovered BTEX catabolic genes. xylM and xylE1 were only recovered from material from the contaminated samples while tmoA was detected in material from both the contaminated and non-contaminated samples. The isolates, mainly obtained from the contaminated locations, belonged to the Actinobacteria or Proteobacteria (mainly Pseudomonas). The ability to degrade benzene was the most common BTEX degradation phenotype among them and its distribution was largely congruent with the distribution of the tmoA-like genotype. The presence of tmoA and xylM genes in phylogenetically distant strains indicated the occurrence of horizontal transfer of BTEX catabolic genes in the aquifer. Overall, these results show spatial variation in the composition of the BTEX degradation genes and hence in the type of BTEX degradation activity and pathway, at the examined site. They indicate that bacteria carrying specific pathways and primarily carrying tmoA/xylM/xylE1 genotypes, are being selected upon BTEX contamination.     

Effect of environmental growth conditions on plasmid stability, plasmid copy number, and catechol 2,3-dioxygenase activity in free and immobilized Escherichia coli cells

In order to better understand the high plasmid stability in immobilized recombinant E. coli cells, the effects of dilution rate on the pTG201 plasmid stability, the copy number, and the catechol 2,3-dioxygenase (encoded by XyIE gene) production were, at first, studied in free E. coli W3101 continuous cultures in minimal media. It was found that decreasing specific growth rate increased the plasmid copy number and the catechol 2,3-dioxygenase activity but the stability decreased. In continuous culture with immobilized cells, an increase was shown in plasmid copy number and catechol 2,3-dioxygenase activity probably due to the distribution of growth in the gel beads. Besides mechanical properties of gel beads which may allow limited cell divisions, the increase in plasmid copy number is involved in enhanced plasmid stability in immobilized cells. In the same way, an experiment conducted in LB medium dealing with competition between pTG201-free and pTG201-containing E. coli B cells was described. It was shown that the competition was not more pronounced in gel bead compared to a free system. The effects of nutritional limitations on pTG201 plasmid stability and catechol 2,3-dioxygenase activity during chemostat cultivations in free and immobilized E. coli B cells were also investigated. It was found that immobilization of cells increased the stability of pTG201 even under glucose, nitrogen, or phosphate limited cultures. However in the case of magnesium depleted culture, pTG201 was shown to be relatively instable and a decrease in viable cell number during the immobilized continuous culture was observed. By contrast to the free system, the catechol 2,3-dioxygenase activity increased in immobilized cells under all culture conditions used.     

An effective family shuffling method using single-stranded DNA

Family shuffling, which is one of the most powerful techniques for in vitro protein evolution, always involves the problem of reassembling the gene fragments into parental gene sequences, because such a process prevents the formation of chimeric sequences. In order to improve the efficiency of hybrid formation in family shuffling, single-stranded DNAs (ssDNAs) were used as templates. The ssDNAs of two catechol 2,3-dioxygenase genes, nahH and xylE, were prepared, the xylE strand being complementary to the nahH strand. When these ssDNAs were digested by DNase I and reassembled, chimeric genes were obtained at a rate of 14%, which was much higher than the rate of less than 1% obtained by shuffling with double-stranded DNAs. Chimeric catechol 2,3-dioxygenases that were more thermally stable than the parental enzymes, XylE and NahH, were obtained by this ssDNA-based DNA shuffling.     

Aromatic hydrocarbon degradation patterns and catechol 2,3-dioxygenase genes in microbial cultures from deep anoxic hypersaline lakes in the eastern Mediterranean sea

Several mixed cultures able to grow on different aromatic hydrocarbons were obtained from different depths (between 3500 and 3660 m under the sea surface) of water/brine interfaces (1 to 5 m over the estimated brine surface) of three deep hypersaline anoxic basins (Urania, Discovery and Atalante) in the eastern Mediterranean sea. Eight strains which completely removed toluene from the medium in six to 10 days were isolated from one of the mixed cultures obtained from the Urania basin. The strains grew on toluene and yeast extract in the presence of NaCl concentrations of up to 50 and 100 g l(-1), respectively, indicating that they are halotolerant rather than halophilic. Even though DNA fingerprinting methods showed that the strains were strictly related, two groups could be found on the basis of the plasmid profile. Metabolic profiling and partial sequencing (350 bp) of the 16S rDNA showed that the strains were related to Pseudomonas mendocina. A 320 bp fragment of the catechol 2,3-dioxygenase gene from all the strains was aimplified by PCR. The sequence of the fragment showed 100% identity with xylE from pWW53 of Pseudomonas putida MT53 isolated from soil. Southern hybridisation experiments showed that catechol 2,3-dioxygenase is plasmid encoded.     

Development of Catechol 2,3-Dioxygenase-Specific Primers for Monitoring Bioremediation by Competitive Quantitative PCR

Benzene, toluene, xylenes, phenol, naphthalene, and biphenyl are among a group of compounds that have at least one reported pathway for biodegradation involving catechol 2,3-dioxygenase enzymes. Thus, detection of the corresponding catechol 2,3-dioxygenase genes can serve as a basis for identifying and quantifying bacteria that have these catabolic abilities. Primers that can successfully amplify a 238-bp catechol 2,3-dioxygenase gene fragment from eight different bacteria are described. The identities of the amplicons were confirmed by hybridization with a 238-bp catechol 2,3-dioxygenase probe. The detection limit was 10² to 10³ gene copies, which was lowered to 10⁰ to 10¹ gene copies by hybridization. Using the dioxygenase-specific primers, an increase in catechol 2,3-dioxygenase genes was detected in petroleum-amended soils. The dioxygenase genes were enumerated by competitive quantitative PCR with a 163-bp competitor that was amplified using the same primers. Target and competitor sequences had identical amplification kinetics. Potential PCR inhibitors that could coextract with DNA, nonamplifying DNA, soil factors (humics), and soil pollutants (toluene) did not impact enumeration. Therefore, this technique can be used to accurately and reproducibly quantify catechol 2,3-dioxygenase genes in complex environments such as petroleum-contaminated soil. Direct, non-cultivation-based molecular techniques for detecting and enumerating microbial pollutant-biodegrading genes in environmental samples are powerful tools for monitoring bioremediation and developing field evidence in support of natural attenuation.     

Development of catechol 2,3-dioxygenase-specific primers for monitoring bioremediation by competitive quantitative PCR

Benzene, toluene, xylenes, phenol, naphthalene, and biphenyl are among a group of compounds that have at least one reported pathway for biodegradation involving catechol 2,3-dioxygenase enzymes. Thus, detection of the corresponding catechol 2,3-dioxygenase genes can serve as a basis for identifying and quantifying bacteria that have these catabolic abilities. Primers that can successfully amplify a 238-bp catechol 2,3-dioxygenase gene fragment from eight different bacteria are described. The identities of the amplicons were confirmed by hybridization with a 238-bp catechol 2,3-dioxygenase probe. The detection limit was 10(2) to 10(3) gene copies, which was lowered to 10(0) to 10(1) gene copies by hybridization. Using the dioxygenase-specific primers, an increase in catechol 2, 3-dioxygenase genes was detected in petroleum-amended soils. The dioxygenase genes were enumerated by competitive quantitative PCR with a 163-bp competitor that was amplified using the same primers. Target and competitor sequences had identical amplification kinetics. Potential PCR inhibitors that could coextract with DNA, nonamplifying DNA, soil factors (humics), and soil pollutants (toluene) did not impact enumeration. Therefore, this technique can be used to accurately and reproducibly quantify catechol 2, 3-dioxygenase genes in complex environments such as petroleum-contaminated soil. Direct, non-cultivation-based molecular techniques for detecting and enumerating microbial pollutant-biodegrading genes in environmental samples are powerful tools for monitoring bioremediation and developing field evidence in support of natural attenuation.