Prevalence of nptII and Tn5 in kanamycin-resistant bacteria from different environments

Abstract Kanamycin (Km)-resistant bacterial populations in different soil, river water, sewage and pig manure slurry samples were enumerated and their prevalence in the total populations determined. About 350 Km-resistant Gram-negative colonies grown in the presence of kanamycin were identified using a rapid presumptive identification scheme. They were then screened for the presence of Tn5 and npt II sequences using hybridization of cells in dot blots, of Southern-blotted genomic DNA extracts and of PCR amplification products. Colonies reacting positively with a 2.7 kb probe of the central region of Tn5, or with a 925 bp npt II specific probe were primarily obtained from sewage samples, whereas fewer were obtained from pig manure slurry, river water and soil. However, in soil samples bacteria containing Tn5 or npt II were not found. Transposon Tn5 carrying the npt II gene could be unequivocally demonstrated in 3 isolates from sewage, identified as Aeromonas spp. (2x) and Escherichia coli . Hin dIII digests of chromosomal DNA obtained from these strains were cloned and shown to confer Km resistance to a sensitive E. coli strain. Further, various strains revealed the presence of npt II homologous sequences in a non-Tn5 background. The occurence of Tn5 and npt II in the samples was also assessed via PCR analysis of total community DNA extracts obtained from the aforementioned environmental samples. Evidence for the occurence of npt II was obtained for sewage, pig manure slurry, for 2 (out of 3) river water (Avon, Rhine) and 3 (out of 6) soil (Flevo silt loam, Westmaas silt loam, Ahlum rhizosphere) samples. Tn5 was not detectable via PCR in any of these environmental DNA extracts but it was found in Ede loamy sand and Flevo silt loam samples taken from a field microplot 2 and 4 weeks after release of a Tn5-containing genetically modified organism.     

DNA recovery and direct detection of Tn5 sequences from soil

Specific Tn5 sequences inserted in the genome of Enterobacter agglomerans were detected in EcoRI digested DNA directly recovered from soil 70 d after its inoculation with the bacteria, when these were no longer culturable on agar medium. A new method of DNA extraction from soil was used. No amplification of DNA sequences by PCR was needed.     

Enumeration of Tn5 mutant bacteria in soil by using a most- probable-number-DNA hybridization procedure and antibiotic resistance

Investigations were made into the utility of DNA hybridization in conjunction with a microdilution most-probable-number procedure for the enumeration of Rhizobium spp. and Pseudomonas putida in soil. Isolates of Rhizobium spp. and P. putida carrying the transposon Tn5 were added to sterile and nonsterile Burbank sandy loam soil and enumerated over time. Soil populations of rhizobia were enumerated by colony hybridization, most-probable-number-DNA hybridization procedure, plate counts, plant infectivity most probable number, and fluorescent antibody counts. Population values compared well for all methods at 5 and 30 days after the addition of cells, although the fluorescent antibody method tended to overestimate the viable population. In nonsterile soil, most-probable-number-DNA hybridization procedure enumerated as few as 10 P. putida Tn5 cells g of soil-1 and 100 R. leguminosarum bv. phaseoli Tn5 cells g of soil-1 and should have utility for following the fate of genetically engineered microorganisms released to the environment. Among the Kmr isolates containing Tn5, approximately 5% gave a dark, more intense autoradiograph when probed with 32P-labeled pGS9 DNA, which facilitated their detection in soil. Hybridization with a pCU101 probe (pGS9 without Tn5) indicated that donor plasmid sequences were being maintained in the bacterial chromosome. Transposon-associated antibiotic resistance was also utilized as a phenotypic marker. Tn5 vector-integrate mutants were successfully enumerated at low populations (10 to 100 cells g of soil-1) in soil by both phenotypic (Kmr) and genotypic (DNA probe) analysis. However, determination of the stability of Tn5 or Tn5 and vector sequences in the bacteria is necessary.     

Enumeration of Tn5 mutant bacteria in soil by using a most- probable-number-DNA hybridization procedure and antibiotic resistance.

Investigations were made into the utility of DNA hybridization in conjunction with a microdilution most-probable-number procedure for the enumeration of Rhizobium spp. and Pseudomonas putida in soil. Isolates of Rhizobium spp. and P. putida carrying the transposon Tn5 were added to sterile and nonsterile Burbank sandy loam soil and enumerated over time. Soil populations of rhizobia were enumerated by colony hybridization, most-probable-number-DNA hybridization procedure, plate counts, plant infectivity most probable number, and fluorescent antibody counts. Population values compared well for all methods at 5 and 30 days after the addition of cells, although the fluorescent antibody method tended to overestimate the viable population. In nonsterile soil, most-probable-number-DNA hybridization procedure enumerated as few as 10 P. putida Tn5 cells g of soil-1 and 100 R. leguminosarum bv. phaseoli Tn5 cells g of soil-1 and should have utility for following the fate of genetically engineered microorganisms released to the environment. Among the Kmr isolates containing Tn5, approximately 5% gave a dark, more intense autoradiograph when probed with 32P-labeled pGS9 DNA, which facilitated their detection in soil. Hybridization with a pCU101 probe (pGS9 without Tn5) indicated that donor plasmid sequences were being maintained in the bacterial chromosome. Transposon-associated antibiotic resistance was also utilized as a phenotypic marker. Tn5 vector-integrate mutants were successfully enumerated at low populations (10 to 100 cells g of soil-1) in soil by both phenotypic (Kmr) and genotypic (DNA probe) analysis. However, determination of the stability of Tn5 or Tn5 and vector sequences in the bacteria is necessary.     

Survival of enterococci and Tn916-like conjugative transposons in soil

The persistence of Enterococcus faecalis, fecal enterococci from swine waste, and Tn916-like elements was determined following inoculation into autoclaved and native soil microcosms. When cells of E. faecalis CG110 (Tn916) were inoculated into native microcosms, enterococcal viability in the soil decreased approximately 5 orders of magnitude (4.8 x 10(5) CFU/g soil to < 10 CFU/g) after 5 weeks. In autoclaved microcosms, the viability of E. faecalis decreased by only 20% in 5 weeks. In contrast, the content of Tn916, based on PCR of DNA extracts from soil microcosms, decreased by about 20% in both native and autoclaved microcosms. Similar results were obtained when the source of fecal enterococci and Tn916-like elements was swine waste. Because the concentration of Tn916-independent E. faecalis DNA (the D-alanine D-alanine ligase gene), based on PCR, decreased to nearly undetectable levels (at least 3 orders of magnitude) after 5 weeks in the native microcosms, the evidence suggests Tn916 stability in the soil results from en masse transfer of the transposon to the normal soil microflora and not survival of E. faecalis DNA in the soil system. Results from denaturing gradient gel electrophoresis suggest that multiple forms of Tn916 occur in swine waste, but only forms most like Tn916 exhibit stability in the soil.     

Tn 5 to assess soil fate of genetically marked bacteria: screening for aminoglycoside-resistance advantage and labelling specificity

Abstract The reliability of Tn 5 as labelling tool was investigated in soil microcosm. The occurence of a selective in soil microcosm. The occurence of resistances encoded by Tn 5 nptII gene was assesed by kanamycin and neomycin amendment. The bioassay developed to monitor the persistence of the soil-added kanamycin did not detect the antibiotic activity in soil extract. A nptII -engineered Escherichia coli strain showed no enhanced survival in aminoglycoside amended soil. Tn 5-marker properties were investigated within indigenous bacteria to determine the specificity of labelling to follow the fate of recombinant DNA. Kanamycin and neomycin resistant population levels made Tn 5 aminoglycoside-resistance phenotype non-sensitive enough to select a soil dissemination of the labelled DNA. The unexpected occurrence of homologous sequences among soil organisms also prevented Tn 5 from being a specific DNA marker. By contrast, colony hybridization did not reveal homology to nptII suggesting its use as a reliable gene transfer indicator.     

Transport of a genetically engineered Pseudomonas fluorescens strain through a soil microcosm

Vertical soil microcosms flushed with groundwater were used to study the influence of water movement on survival and transport of a genetically engineered Pseudomonas fluorescens C5t strain through a loamy sand and a loam soil. Transport of cells introduced into the top 1 cm of the vertical soil microcosms was dependent on the flow rate of water and the number of times microcosms were flushed with groundwater. The presence of wheat roots growing downward in the microcosms contributed only slightly to the movement of P. fluorescens C5t cells to lower soil regions of the loamy sand microcosms, but enhanced downward transport in the loam microcosms. Furthermore, the introduced P. fluorescens C5t cells were detected in the effluent water samples even after three flushes of groundwater and 10 days of incubation. As evidenced by a comparison of counts from immunofluorescence and selective plating, nonculturable C5t cells occurred in day 10 soil and percolated water samples, primarily of the loamy sand microcosms. Vertical soil microcosms that use water movement may be useful in studying the survival and transport of genetically engineered bacteria in soil under a variety of conditions prior to field testing.     

Transport of a genetically engineered Pseudomonas fluorescens strain through a soil microcosm.

Vertical soil microcosms flushed with groundwater were used to study the influence of water movement on survival and transport of a genetically engineered Pseudomonas fluorescens C5t strain through a loamy sand and a loam soil. Transport of cells introduced into the top 1 cm of the vertical soil microcosms was dependent on the flow rate of water and the number of times microcosms were flushed with groundwater. The presence of wheat roots growing downward in the microcosms contributed only slightly to the movement of P. fluorescens C5t cells to lower soil regions of the loamy sand microcosms, but enhanced downward transport in the loam microcosms. Furthermore, the introduced P. fluorescens C5t cells were detected in the effluent water samples even after three flushes of groundwater and 10 days of incubation. As evidenced by a comparison of counts from immunofluorescence and selective plating, nonculturable C5t cells occurred in day 10 soil and percolated water samples, primarily of the loamy sand microcosms. Vertical soil microcosms that use water movement may be useful in studying the survival and transport of genetically engineered bacteria in soil under a variety of conditions prior to field testing.     

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.     

Monitoring the fate of genetically engineered bacteria sprayed on the phylloplane of bush beans and grass

Abstract The fate of a Bacillus amyloliquefaciens with the recombinant plasmid pSB20 sprayed on the phyllosphere of grass, and of a Tn 5 marked Pseudomonas syringae sprayed on the phyllosphere of bush beans was studied in planted soil microcosms. B. amyloliquefaciens showed a decline from 1.5×10⁸ to 3.1×10² cfu g⁻¹ on the phylloplane of grass in the course of the experiment. B. amyloliquefaciens was easy to follow by selective cultivation due to the complete absence of bacterial background growth. Southern blot hybridization of Hin dIII digested genomic DNA showed plasmid restriction patterns identical with pSB20 indicating high plasmid stability. In total DNA extracts from phyllosphere bacteria the recombinant plasmid was detectable by Southern blot hybridization up to 6×10⁴ cfu g⁻¹ (wet weight). Counts of hybridizing colonies showed that P. syringae established on the phyllosphere of bush beans at between 5×10³ and 4×10⁶ cfu g⁻¹ fresh weight. During senescence of the bean plants the strain was no longer detectable by selective cultivation and subsequent colony hybridization. In contrast, Tn5 marked DNA was detected after PCR amplification over the whole period of the experiment.     

Survival of free and alginate-encapsulated Pseudomonas aeruginosa UG2Lr in soil treated with disinfectants

Pseudomonas aeruginosa UG2Lr, a rifampicin-resistant strain possessing the luxAB on a chromosomal Tn5 insert, was inoculated into soil microcosms as either free cells or encapsulated in dry alginate beads. A 100-fold increase in cell number g^-1 dry soil was observed in microcosms inoculated with alginate-encapsulated UG2Lr after 3 weeks incubation at 22°C compared to microcosms inoculated with free cells. After 98 d, microcosms inoculated with free UG2Lr cells contained 10⁴ cfu g^-1 dry soil compared to 10⁷ cfu g^-1 dry soil in microcosms inoculated with alginate-encapsulated UG2Lr cells. The effects of disinfectants on both the free and alginate-encapsulated UG2Lr cells were also examined. 1·0% (w/g dry soil) calcium hypochlorite, formaldehyde and Spectrum Clear Bath, were added to microcosms each week for 4 weeks. Formaldehyde killed both free and alginate-encapsulated UG2Lr cells within 14 d after only two amendments. Calcium hypochlorite reduced free UG2Lr cell numbers 10-fold 2 d after initial application; however, the introduced population recovered and was unaffected by subsequent treatments at 7, 14 and 21 d. Alginate-encapsulated UG2Lr cells were not affected by calcium hypochlorite treatment. Spectrum Clear Bath did not kill either free or alginate-encapsulated UG2Lr cells in soil. Alginate encapsulation improved survival of introduced bacteria in soil except in the presence of formaldehyde. Killing genetically-engineered bacteria in soil may be difficult unless a powerful disinfectant such as formaldehyde is used or the genetically-engineered micro-organism is allowed to become non-viable over time.     

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.     

Plasmid Transfer between Spatially Separated Donor and Recipient Bacteria in Earthworm-Containing Soil Microcosms

Most gene transfer studies have been performed with relatively homogeneous soil systems in the absence of soil macrobiota, including invertebrates. In this study we examined the influence of earthworm activity (burrowing, casting, and feeding) on transfer of plasmid pJP4 between spatially separated donor (Alcaligenes eutrophus) and recipient (Pseudomonas fluorescens) bacteria in nonsterile soil columns. A model system was designed such that the activity of earthworms would act to mediate cell contact and gene transfer. Three different earthworm species (Aporrectodea trapezoides, Lumbricus rubellus, and Lumbricus terrestris), representing each of the major ecological categories (endogeic, epigeic, and anecic), were evaluated. Inoculated soil microcosms, with and without added earthworms, were analyzed for donor, recipient, and transconjugant bacteria at 5-cm-depth intervals by using selective plating techniques. Transconjugants were confirmed by colony hybridization with a mer gene probe. The presence of earthworms significantly increased dispersal of the donor and recipient strains. In situ gene transfer of plasmid pJP4 from A. eutrophus to P. fluorescens was detected only in earthworm-containing microcosms, at a frequency of (symbl)10(sup2) transconjugants per g of soil. The depth of recovery was dependent on the burrowing behavior of each earthworm species; however, there was no significant difference in the total number of transconjugants among the earthworm species. Donor and recipient bacteria were recovered from earthworm feces (casts) of all three earthworm species, with numbers up to 10(sup6) and 10(sup4) bacteria per g of cast, respectively. A. trapezoides egg capsules (cocoons) formed in the inoculated soil microcosms contained up to 10(sup7) donor and 10(sup6) recipient bacteria per g of cocoon. No transconjugant bacteria, however, were recovered from these microhabitats. To our knowledge, this is the first report of gene transfer between physically isolated bacteria in nonsterile soil, using burrowing earthworms as a biological factor to facilitate cell-to-cell contact.     

Rapid amplification and cloning of Tn5 flanking fragments by inverse PCR

A simple approach is described to efficiently amplify DNA sequences flanking transposon Tn5 insertions. The method involves: (i) digestion with a restriction enzyme that cuts within Tn5; (ii) self-ligation under conditions favouring the production of monomeric circles; (iii) four parallel PCR reactions using primers designed to amplify left or right flanking sequences, and to distinguish target amplicons from non-specific products. This reveals the number of Tn5 insertions and the size of flanking genomic restriction fragments, without Southern blot analysis. The amplified product contains restriction sites that facilitate cohesive-end cloning. This rapid method is demonstrated using Tn5 and Tn5-Mob tagged DNA sequences involved in albicidin biosynthesis in Xanthomonas albilineans. It is generally applicable for efficient recovery of DNA sequences flanking transposon Tn5 derivatives in insertional mutagenesis studies.     

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.     

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.     

Distribution of streptothricin acetyltransferase encodi determinants among environmental bacteria

In this paper we report about a screening for streptothricin- (St)-resistant phenotypes and genotypes among environmental bacteria from a St virgin area. St-resistant bacteria were isolated from river water, sewage, manure and soil by selective plating. The resistance quotient was typical of an area without selective pressure. The occurrence of streptothricin acetyltransferase-encoding determinants and their localization on a Tn7-like transposon was tested by the application of a set of gene probes. Sat genes could be detected in 22.5% of the tested St-resistant bacteria but in 100% of the checked Enterobacteriaceae. However, we could not detect sat genes in St-resistant bacteria from soil samples. Surprisingly the sat genes were found to be located on conjugative or mobilizable plasmids for a rather high number of strains. The determined plasmid species and their restriction patterns showed a high degree of similarities to those observed from an area of strong selective pressure.     

Cloning, characterization, and complementation of lesions causing acid sensitivity in Tn5-induced mutants of Rhizobium meliloti WSM419.

Four Tn5-induced mutants of Rhizobium meliloti WSM419 were unable to grow or maintain intracellular pH at an external pH of 5.6. Restriction analysis of DNA fragments carrying Tn5 and flanking sequences cloned from these mutants indicated that all four cloned mutations are unique and that the two strains (TG1-6 and TG1-11) carry Tn5 insertions which are within 4.4 kilobases of each other on a single EcoRI fragment. Southern analysis of total mutant DNA indicated a single copy of Tn5 in each mutant. A limited cosmid gene bank of wild-type WSM419 DNA was probed for homology to mutant DNA cloned from the acid-sensitive mutants. Dot hybridization experiments identified one cosmid element within this bank carrying wild-type DNA sequences corresponding to DNA implicated in acid tolerance. This cosmid was able to complement defects in growth and intracellular pH maintenance in TG1-11 but not TG1-6.     

COMPARISON OF THREE PROBE LABELLING METHODS TO DETECT PCR AMPLIFICATION PRODUCTS

Polymerase chain reaction amplifications are finding increased applications in environmental microbiology. The development of sensitive and specific methods to detect amplified products is necessary especially when these amplifications are conducted in the presence of the environmental matrix. Gene probes specific to the npt11 locus were prepared by nick translation, 5'end labelling and by a PCR driven amplification. These probes were tested against a 300 bp PCR amplified segment of the npt11 region of the transposable element Tn5. The nick translated probe was the most sensitive, though not as specific as the other two types of probes. Sensitivity and specificity were found to be dependent on the hybridization format (Southern blots versus dot blots), the number of amplification cycles and on the purity of the target sequence.     

Influence of soil variables on in situ plasmid transfer from Escherichia coli to Rhizobium fredii.

A model system was established to determine whether intergeneric plasmid transfer occurs in soil and how various soil variables affect the rate of plasmid transfer. The donor bacterium, Escherichia coli HB101 carrying plasmid pBLK1-2 (pRK2073::Tn5), and the recipient bacterium, Rhizobium fredii USDA 201, were inoculated into a sterile Adelphia fine-sandy-loam soil. Transconjugants were enumerated by direct plating on antibiotic-amended HM [N-2-hydroxyethylpiperazine-N'-2-ethanesulfonic acid; 2-(N-morpholino) ethanesulfonic acid] salts medium. Randomly chosen transconjugants were verified by serological typing and Southern hybridization with a Tn5 gene probe. The maximum transfer frequency was observed after 5 days of incubation (1.8 x 10(-4) per recipient). The influences of clay (0 to 50% addition), organic matter (0 to 15% addition), soil pH (4.3 to 7.25), soil moisture (2 to 40%), and soil incubation temperature (5 to 40 degrees C) on plasmid transfer were examined. Maximum transfer frequencies were noted at a clay addition of 15%, an organic matter addition of 5%, a soil pH of 7.25, a soil moisture content of 8%, and a soil incubation temperature of 28 degrees C. These results indicate that intergeneric plasmid transfer may occur in soil and that soil variables may significantly affect the rate of transfer.