Survival of Pseudomonas putida UWC1 containing cloned catabolic genes in a model activated-sludge unit

Description of a novel plasmid replicative origin from a genetically distinct family of conjugative plasmids associated with phytosphere microflora

A novel replicative origin (oriV) from a conjugative, mercury resistance plasmid (pQBR11, 304 kbp) has been cloned and sequenced. Homology to the pQBR11 oriV-containing 3.55 kbp BamHI fragment (pCV1200) was restricted to one of five genetically distinct classes (group I) of narrow host range, mega-plasmids that persist as a genetic component of the pseudomonad community indigenous to the microflora of sugar beet. The oriV of pQBR11 was located within a unique sequence of 300 bp which initiated the replication of pUC derived suicide vectors in Pseudomonas putida UWC1. The limited size of the DNA sequence required to initiate replication, and the presence of two 15/16 bp directly repeated motifs, indicate that this group of mega-plasmids contain a single origin of replication, which initiates replication via a host-polymerase dependent rolling circle mechanism.

Construction of GFP vectors for use in gram-negative bacteria other than Escherichia coli

A set of vectors containing a mutated gfp gene was constructed for use with Gram-negative bacteria other than Escherichia coli. These constructs were: pTn3gfp for making random promoter probe gfp insertions into cloned DNA in E. coli for subsequent introduction into host strains; pUTmini-Tn5gfp for making random promoter probe gfp insertions directly into host strains; p519gfp and p519nfp, broad host range mob+ plasmids containing gfp expressed from a lac and an npt2 promoter, respectively.

Fate of genetically modified Rhizobium leguminosarum biovar viciae during long-term storage of commercial inoculants

A study was carried out to assess the behaviour, in terms of strain survival and genetic stability, of genetically modified micro-organisms (GEMs) during their storage in commercial-type agricultural inoculants. Three genetically modified Rhizobium leguminosarum biovar viciae strains were constructed, using a gene cassette containing an inducible lacZ gene from Escherichia coli and mercury resistance determinants from transposon Tn 1831. In the first case the genes have been integrated into the chromosome, the second strain contains the inducible cassette on a plasmid, in the third case the cassette is carried by the same plasmid, but the lacZ is constitutively expressed at high levels, due to the removal of the regulatory structure (lac operator) between the gene and its promoter. Three inoculum formulations, based on liquid, vermiculite and peat carriers, were prepared using the genetically modified strains, and were monitored during a period of up to 16 months. Results indicate a high stability of the chromosomally integrated markers. The plasmid-borne modification also was very stable, though the presence of the plasmid affected the strain growth kinetics. In contrast, the strain containing the highly expressed lacZ showed dramatic marker instability. Strain behaviour in stored inoculant packages reflected that observed in batch cultures; moreover, prolonged storage appeared to magnify differences found in in vitro cultures.

Antibiotic resistance of biofilms

Microbial biofilms are notably recalcitrant towards treatment with antibiotics, biocides or disinfectants that would adequately control the same organisms growing in planktonic mode. Much of this resistance has been attributed to an organisation of the biofilm cells within exopolymer matrices. Whilst such exopolymers are unlikely to hinder the diffusion and access of antimicrobial agents to the underlying cells, they will chemically quench reactive biocides such as chlorine and peroxygens, and bind highly charged antibiotics, such as tobramycin and gentamycin, thereby providing some protection to the more deep lying cells. Extracellular enzymes, bound within the glycocalyx and able to degrade the treatment agents, will further reduce the access of susceptible compounds. Diffusion limitation however, is unlikely to be the sole moderator of the resistance properties of microbial biofilms. In addition, gradients of oxygen and nutrients established across the biofilm community will cause growth rates to be much reduced at points remoted from the accessible nutrient. Slow growth rates, and the associated induction of stringent responses further contribute towards this resistance. Finally, there have been recent demonstrations that attachment of microorganisms to surfaces promotes the expression of genes that are not normally expressed in planktonic culture. Whether or not the expression of such genes alters the phenotype in a manner which alters the response of the cells to antimicrobial agents remains to be demonstrated.

Use of a novel plasmid to monitor the fate of a genetically engineered Pseudomonas putida strain

Plasmid pSI30 was constructed to increase the sensitivity of detection of a genetically engineered micro-organism (GEM) and its recombinant DNA in environmental samples. This broad host-range, mobilizable plasmid contained chlorocatechol (clc) degradative genes, antibiotic resistance genes (ampicillin and kanamycin) and a fragment of eukaryotic DNA. The clc genes encode enzymes that convert 3-chlorocatechol to maleylacetic acid permitting the host, Pseudomonas putida RC-4, to grow on 3-chlorobenzoate. This catabolic phenotype was exploited using enrichment procedures to detect RC-4(pSI30) cells, free-living in the water column or when irreversibly bound to surfaces. The eukaryotic DNA sequence provided a unique target allowing positive identification by DNA:DNA hybridization. Using the eukaryotic DNA sequence as a probe, no transfer of the plasmid to indigenous bacteria was detected. Persistence of RC-4(pSI30) and its ability to multiply upon addition of 3-chlorobenzoate were demonstrated 78 days after its addition to natural freshwater. In flow-through microcosms RC-4(pSI30), undetectable as free-living cells, was found by enrichment as irreversibly bound sessile forms. These experiments revealed the stability of pSI30 and its utility in a 'combination' detection system for tracking the survival of a GEM and its DNA in environmental samples.

Exogenous Isolation of Mobilizing Plasmids from Polluted Soils and Sludges

Exogenous plasmid isolation was used to assess the presence of mobilizing plasmids in several soils and activated sludges. Triparental matings were performed with Escherichia coli (a member of the γ subgroup of the Proteobacteria ) as the donor of an IncQ plasmid (pMOL155, containing the heavy metal resistance genes czc : Co r , Zn r , and Cd r ), Alcaligenes eutrophus (a member of the β subgroup of the Proteobacteria ) as the recipient, and indigenous microorganisms from soil and sludge samples as helper strains. We developed an assay to assess the plasmid mobilization potential of a soil ecosystem on the basis of the number of transconjugants obtained after exogenous isolations. After inoculation into soil of several concentrations of a helper strain ( E. coli CM120 harboring IncP [IncP1] mobilizing plasmid RP4), the log numbers of transconjugants obtained from exogenous isolations with different soil samples were a linear function of the log numbers of helper strain CM120(RP4) present in the soils. Four soils were analyzed for the presence of mobilizing elements, and mobilizing plasmids were isolated from two of these soils. Several sludge samples from different wastewater treatment plants yielded much higher numbers of transconjugants than the soil samples, indicating that higher numbers of mobilizing strains were present. The mobilizing plasmids isolated from Gent-O sludge and one plasmid isolated from Eislingen soil hybridized to the repP probe, whereas the plasmids isolated from Essen soil did not hybridize to a large number of rep probes (repFIC, repHI1, repH12, repL/M, repN, repP, repT, repU, repW, repX). This indicates that in Essen soil, broad-host-range mobilizing plasmids belonging to other incompatibility groups may be present.

The behavior of bacteria designed for biodegradation

Mineralization of organic molecules by microbes is essential for the carbon cycle to operate. The massive mobilization of compounds stored in natural resources, or the introduction of xenobiotics into the biosphere, leads to unidirectional fluxes, which result in the persistance of a number of chemicals in the biosphere, and thus constitute a source of pollution. Molecular biology offers the tools to optimize the biodegradative capacities of microorganisms, accelerate the evolution of "new" activities, and construct totally "new" pathways through the assemblage of catabolic segments from different microbes. Although the number of genetically engineered microbes (GEMs) for potential use in biodegradation is not large, these recombinant microbes function in microcosms according to their design. The survival and fate of recombinant microbes in different ecological niches under laboratory conditions is similar to what has been observed for the unmodified parental strains. rDNA, both on plasmids and on the host chromosome, is usually stably inherited by GEMs. The potential lateral transfer of rDNA from the GEMs to other microbes is significantly diminished, though not totally inhibited, when rDNA is incorporated on the host chromosome. The behavior and fate of GEMs can be predicted more accurately through the coupling of regulatory circuits that control the expression of catabolic pathways to killing genes, so that the GEMs survive in polluted environments, but die when the target chemical is eliminated.

Distribution of the catabolic transposon Tn5271 in a groundwater bioremediation system

The distribution of Tn5271-related DNA sequences in samples of groundwater and a groundwater bioremediation system at the Hyde Park (Niagara Falls, N.Y.) chemical landfill site was investigated. PCR amplification of target sequences within the cha genes of Tn5271 revealed similar sequences in the groundwater community and in samples from the sequencing batch reactors treating that groundwater. Cell dilution combined with PCR amplification indicated that cha sequences were carried in about 1 of 10 culturable bacteria from the treatment system. Characterization of isolates involved in chlorobenzoate and toluene biodegradation in the treatment system indicated that two phenotypic clusters, Alcaligenes faecalis type 2 and CDC group IVC-2, contained all of the Tn5271 probe-positive isolates from the community. These two groups differed phenotypically from recipient groups isolated following horizontal transfer of pBRC60 (Tn5271) in pristine freshwater microcosms. A genetic rearrangement in Tn5271 attributable to the intramolecular transposition of the flanking element IS1071R was detected in an isolate from the treatment system. Comparison of the structure of the intramolecular transposition derivative from groundwater isolate OCC13(pBRC13) with a laboratory-derived intramolecular transposition derivative of pBRC60 revealed similarities. The rearrangement was shown to increase the stability of the plasmid under starvation conditions.

Survival of 2,4-dichlorophenoxyacetic acid degrading Alcaligenes eutrophus AE0106(pR0101) in lake water microcosms

Survival of the 2,4-dichlorophenoxyacetic acid (2,4-D) degrading Alcaligenes eutrophus strain AEO 106 harboring the catabolic plasmid pRO101 was studied in lake water from the eutrophic lake Frederiksborg Slotssø. Survival experiments were performed for periods of 7 days in laboratory microcosms containing filtered (0.2-µm pore size) or natural lake water amended with increasing concentrations of 2,4-D. A. eutrophus AE0106 was detected by combining the fluorescent antibody method with selective and nonselective plating followed by colony blotting and colony hybridization. Comparison of colony blotting and colony hybridization demonstrated that the A. eutrophus AE0106 host organism and the catabolic plasmid pRO101 had similar fates in the model system employed. In all experiments culturable counts of A. eutrophus AE0106 were lower than fluorescent antibody counts and frequently a decline in culturable counts occurred at times when the fluorescent antibody method showed an increasing population size. Amendment with 2,4-D increased survival of A. eutrophus AE0106 both in filtered and in natural lake water. Survival was always poorer in model systems with natural water than in 0.2 µm-filtered water.

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

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

Evaluation of aquatic sediment microcosms and their use in assessing possible effects of introduced microorganisms on ecosystem parameters

In this paper we describe a sediment microcosm system consisting of 20 undisturbed, layered sediment cores with overlying site water which are incubated under identical conditions of temperature, light, stirring rate of overlying water, and water exchange rate. Ecosystem parameters (nutrient level, photosynthetic potential, community structure of heterotrophic bacteria, thymidine incorporation rate, and oxygen microgradients) of the laboratory microcosms and the source ecosystem were compared and shown to be indistinguishable for the first 2 weeks. In weeks 3 and 4, small differences were detectable in the nutrient level, community structure of heterotrophic bacteria, and thymidine incorporation rate. However, the photosynthetic potential, depth profiles of heterotrophic bacterial community structure, and oxygen microgradients were maintained throughout the incubation period and did not differ between laboratory microcosms and the source ecosystem. The microcosm system described here would thus appear to be a valid model of aquatic sediments for up to 4 weeks; the actual period would depend on the sediment source and incubation temperature. The validated systems were used with Rhine river sediment to assess possible effects on ecosystem parameters of Pseudomonas sp. strain B13 FR1(pFRC20P), a genetically engineered microorganism (GEM) that had been constructed to degrade mixtures of halo- and alkylbenzoates and -phenols. The GEM survived in the surface sediment at densities of 5 x 10(4) to 5 x 10(5)/g (dry weight) for 4 weeks and degraded added chloro- and methylaromatics. The GEM did not measurably influence ecosystem parameters such as photosynthesis, densities of selected heterotrophic bacteria, thymidine incorporation rate, and oxygen microgradients. Thus, the microcosm system described here would seem to be useful for the study of the ecology of biodegradation and the fate and effect of microorganisms introduced into the environment.

Survival and function of a genetically engineered Pseudomonad in aquatic sediment microcosms

Pseudomonas sp. strain B13 FR1(pFRC20P) is a genetically engineered microorganism (GEM) which is able to degrade chloro- and methylaromatics through a constructed ortho cleavage pathway. The fate of the GEM and its ability to degrade substituted aromatic compounds in two different aquatic sediments was investigated by using a microcosm system which consisted of intact layered sediment cores with an overlying water column. The GEM survived in Lake Plussee and in Rhine river sediments at densities of approximately 10(5) bacteria per g (dry weight) (1 to 5% of the total CFU) throughout a 4-week period of investigation. According to several criteria, the microcosm system was stable and healthy throughout the experiment and the addition of the GEM did not affect the total number of extractable CFU (I. Wagner-Döbler, R. Pipke, K. N. Timmis, and D. F. Dwyer, Appl. Environ. Microbiol. 58:1249-1258, 1992). When compared with uninoculated controls, the presence of the GEM enhanced the rate of degradation of a mixture of 3-chlorobenzoate and 4-methylbenzoate (25 microns each) which had been added to the water column of the sediment cores.

Isolation and screening of plasmids from the epilithon which mobilize recombinant plasmid pD10

This study examined the potential of bacteria from river epilithon to mobilize a recombinant catabolic plasmid, pD10, encoding 3-chlorobenzoate degradation and kanamycin resistance. Fifty-four mobilizing plasmids were exogenously isolated by triparental matings between strains of Pseudomonas putida and epilithic bacteria from the River Taff (South Wales, United Kingdom). Frequencies for mobilization ranged from 1.7 x 10(-8) to 4.5 x 10(-3) per recipient at 20 degrees C. The sizes of the mobilizing plasmids isolated ranged from 40 kb to over 200 kb, and 19 of 54 were found to encode mercury resistance. Plasmid-encoded resistance to tetracycline and streptomycin was also found but not resistance to UV light or various heavy metals. Eight plasmids of epilithic bacteria, analyzed by comparing restriction fragmentation patterns, showed significant differences between those isolated from different independent matings. Optimal temperatures for mobilization of pD10 were between 15 and 25 degrees C. Four mercury resistance plasmids were found to be broad host range, transferring mercury resistance and mobilizing pD10 readily to representative species of beta- and gamma-purple bacteria. In general, frequencies of pD10 mobilization by plasmids of epilithic bacteria were 2 to 3 orders of magnitude lower than conjugal transfer frequencies. Thus, there is a high potential for exchange of recombinant genes introduced into the epilithon by mobilization between a variety of bacterial species.

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.

Involvement of a chlorobenzoate-catabolic transposon, Tn5271, in community adaptation to chlorobiphenyl, chloroaniline, and 2,4-dichlorophenoxyacetic acid in a freshwater ecosystem

A chlorobenzoate-catabolic transposon (Tn5271) was introduced on a conjugative plasmid (pBRC60) in the natural host, Alcaligenes sp. strain BR60, into lake water and sediment flowthrough microcosms. Experimental microcosms were exposed to micromolar levels of 3-chlorobenzoate, 4-chloroaniline, 2,4-dichlorophenoxyacetate, or 3-chlorobiphenyl. The populations of the host, BR60, and organisms carrying Tn5271 were monitored over a 100-day period by use of selective plate counts and the most-probable-number-DNA hybridization method. Populations of Tn5271-carrying bacteria were significantly higher in microcosms dosed with 3-chlorobenzoate, 4-chloroaniline, and 3-chlorobiphenyl than in the control microcosms, indicating that each of these chemicals exerts a selective force on this particular genotype in natural systems. The rates of 3-chlorobenzoate uptake and respiration correlated with Tn5271-carrying populations, as did the rates of 4-chloroaniline uptake and respiration. Plasmid transfer in the 3-chlorobenzoate- and 3-chlorobiphenyl-dosed microcosms resulted in the selection of three phenotypic clusters of chlorobenzoate degraders, only one of which was closely related to the original pBRC60 (Tn5271) donor, Alcaligenes sp. strain BR60. Bacteria dominating 4-chloroaniline-dosed microcosms carried IS1071, the class II insertion sequence that brackets Tn5271, on a plasmid unrelated to pBRC60. The importance of plasmid transfer and transposition during chemical adaptation is discussed.

Conjugational transfer of recombinant DNA in cultures and in soils: host range of Pseudomonas putida TOL plasmids

Recombinant TOL plasmid pWWO-EB62 allows Pseudomonas putida to grow on p-ethylbenzoate. This plasmid can be transferred to other microorganisms, and its catabolic functions for the metabolism of alkylbenzoates are expressed in a limited number of gram-negative bacteria, including members of pseudomonad rRNA group I and Escherichia coli. Transfer of the recombinant plasmid to Erwinia chrysanthemi was observed, but transconjugants failed to grow on alkylbenzoates because they lost catabolic functions. Pseudomonads belonging to rRNA groups II, III, and IV, Acinetobacter calcoaceticus, and Alcaligenes sp. could not act as recipients for TOL, either because the plasmid was not transferred or because it was not stably maintained. The frequency of transfer of pWWO-EB62 from P. putida as a donor to pseudomonads belonging to rRNA group I was on the order of 1 to 10(-2) transconjugant per recipient, while the frequency of intergeneric transfer ranged from 10(-3) to 10(-7) transconjugant per recipient. The profile of potential hosts was conserved when the donor bacterium was Escherichia coli or Erwinia chrysanthemi instead of P. putida. No intergeneric gene transfer of the recombinant TOL plasmid was observed in soils; however, intraspecies transfer did take place. Intraspecies transfer of TOL in soils was affected by the type of soil used, the initial inoculum size, and the presence of chemicals that could affect the survival of the donor or recipient bacteria.

Survival and catabolic activity of natural and genetically engineered bacteria in a laboratory-scale activated-sludge unit

The survival of selected naturally occurring and genetically engineered bacteria in a fully functional laboratory-scale activated-sludge unit (ASU) was investigated. The effect of the presence of 3-chlorobenzoate (3CB) on the survival of Pseudomonas putida UWC1, with or without a chimeric plasmid, pD10, which encodes 3CB catabolism, was determined. P. putida UWC1(pD10) did not enhance 3CB breakdown in the ASU, even following inoculation at a high concentration (3 x 10(8) CFU/ml). The emergence of a natural, 3CB-degrading population appeared to have a detrimental effect on the survival of strain UWC1 in the ASU. The fate of two 3CB-utilizing bacteria, derived from activated-sludge microflora, was studied in experiments in which these strains were inoculated into the ASU. Both strains, AS2, an unmanipulated natural isolate which flocculated readily in liquid media, and P. putida ASR2.8, a transconjugant containing the recombinant plasmid pD10, survived for long periods in the ASU and enhanced 3CB breakdown at 15 degrees C. The results reported in this paper illustrate the importance of choosing strains which are well adapted to environmental conditions if the use of microbial inoculants for the breakdown of target pollutants is to be successful.

Mobilization of the genetically engineered plasmid pHSV106 from Escherichia coli HB101(pHSV106) to Enterobacter cloacae in drinking water

We have used triparental matings to demonstrate transfer (mobilization) of the nonconjugative genetically engineered plasmid pHSV106, which contains the thymidine kinase gene of herpes simplex virus cloned into pBR322, from Escherichia coli HB101 to an environmental isolate of Enterobacter cloacae in sterile drinking water. This is the first demonstration of a two-step mobilization of a genetically engineered plasmid in any type of fresh water, including drinking water. Transfer was mediated by R plasmid R100-1 of E. coli ED2149(R100-1). Matings in drinking water at 15, 25, and 35 degrees C yielded recombinants, the number of which increased with increasing temperature. Numbers of recombinants obtained were 2 orders of magnitude lower than those obtained from matings in Trypticase soy broth. High concentrations of parental organisms (2.6 x 10(8) to 2.0 x 10(9) CFU/ml) were required. During 1 week of incubation in drinking water, number of parental organisms and recombinants resulting from mobilization remained constant in the absence of indigenous organisms and declined in their presence. Using oligonucleotide probes for the cloned foreign DNA (thymidine kinase gene) and plasmid vector DNA (ampicillin resistance gene), we demonstrated that both genes were transferred to E. cloacae in the mobilization process. In one recombinant selected for detailed study, the plasmids containing these genes differed in size from all forms of pHSV106 present in E. coli HB101(pHSV106), indicating that DNA rearrangement had occurred. This recombinant maintained its plasmids in unchanged form for 15 days in drinking water. A second rearrangement occurred during serial passage of this recombinant on selective media.(ABSTRACT TRUNCATED AT 250 WORDS)

Survival in soils of an herbicide-resistant Pseudomonas putida strain bearing a recombinant TOL plasmid

Pseudomonas putida EEZ15(pWW0-EB62) is a phosphinothricin (PPT)-resistant strain with a recombinant TOL plasmid which allows the strain to grow on p-ethylbenzoate. The survival of this strain in sterile agricultural soils depends on the physicochemical properties of the soil. The recombinant pWW0-EB62 plasmid and its catabolic functions were stable for periods of up to 1 month in bacteria introduced in unamended soils and only conferred selective advantage to the host bacteria without the plasmid or with the natural pWW0 plasmid when the soils were amended with low amounts of p-ethylbenzoate. The addition to soils of aromatics that are cometabolized by P. putida EEZ15(pWW0-EB62) had a detrimental effect on the survival of the bacteria, whereas low amounts of aromatics that are not metabolized by this bacterium had no effect on their survival. Survival of P. putida EEZ15(pWW0-EB62) was better at 4 and 25 degrees C than at 37 degrees C. The host bacterium carrying the recombinant pWW0-EB62 plasmid was established in unsterile soils.