Survival of Vibrio cholerae and Escherichia coli in estuarine waters and sediments.

In in vitro estuarine water and sediment chambers, the survival of Vibrio cholerae and Escherichia coli was determined by plate counting and direct counting techniques. V. cholerae strains included environmental, clinical, and serotype O1 and non-O1 isolates, whereas E. coli strains included ATCC 25922 and a freshly cultured human isolate. Recovery of V. cholerae varied significantly with incubation temperature. Growth and extended periods of survival occurred in sterile sediments, sterile waters, and nonsterile waters, but not in nonsterile sediments. In contrast to V. cholerae, viable cells of E. coli decreased rapidly in both sterile and nonsterile estuarine waters. Direct counts revealed that E. coli cells were intact in the estuarine water, but attempts to resuscitate them were unsuccessful. The data suggest that V. cholerae survives better in estuarine waters than E. coli. The results may explain the recent observations that V. cholerae levels do not correlate well with fecal coliform concentrations in estuarine waters. Furthermore, the results add increasing evidence to support the theory that V. cholerae is an autochthonous bacterium in estuaries.     

Retention of virulence in a viable but nonculturable Edwardsiella tarda isolate

Edwardsiella tarda is pathogen of fish and other animals. The aim of this study was to investigate the viable but nonculturable (VBNC) state and virulence retention of this bacterium. Edwardsiella tarda CW7 was cultured in sterilized aged seawater at 4 degrees C. Total cell counts remained constant throughout the 28-day period by acridine orange direct counting, while plate counts declined to undetectable levels (<0.1 CFU/ml) within 28 days by plate counting. The direct viable counts, on the other hand, declined to ca. 10(9) CFU/ml active cells and remained fairly constant at this level by direct viable counting. These results indicated that a large population of cells existed in a viable but nonculturable state. VBNC E. tarda CW7 could resuscitate in experimental chick embryos and in the presence of nutrition with a temperature upshift. The resuscitative times were 6 days and 8 days, respectively. The morphological changes of VBNC, normal, and resuscitative E. tarda CW7 cells were studied with a scanning electron microscope. The results showed that when the cells entered into the VBNC state, they gradually changed in shape from short rods to coccoid and decreased in size, but the resuscitative cells did not show any obvious differences from the normal cells. The VBNC and the resuscitative E. tarda CW7 cells were intraperitoneally inoculated into turbot separately, and the fish inoculated with the resuscitative cells died within 7 days, which suggested that VBNC E. tarda CW7 might retain pathogenicity.     

Membrane fatty acid and virulence changes in the viable but nonculturable state of Vibrio vulnificus

The nonculturable state of Vibrio vulnificus and, for comparison, that of Escherichia coli were studied in artificial-seawater microcosms at 5 degrees C. Total cell counts were monitored by acridine orange epifluorescence, metabolic activity by direct viable counts, and culturability by plate counts on selective and nonselective media. Whereas total counts remained constant, plate counts of V. vulnificus suggested nonculturability by day 24. In contrast, direct viable counts indicated significant cell viability throughout 32 days of incubation. As an indication of the metabolic changes that occurred as cells entered the state of nonrecoverability, membrane fatty acid analyses were performed. At the point of nonculturability of V. vulnificus, the major fatty acid species (C16 and C16:1) had decreased 57% from the T0 level, concomitant with the appearance of several short-chain acids. Although the bacteria were still recoverable, a similar trend was observed with E. coli. Electron microscopy of nonculturable V. vulnificus showed that the cells were rounded and reduced in size and contained fewer ribosomes. Mouse infectivity studies conducted with these cells suggested loss of virulence.     

Membrane fatty acid and virulence changes in the viable but nonculturable state of Vibrio vulnificus.

The nonculturable state of Vibrio vulnificus and, for comparison, that of Escherichia coli were studied in artificial-seawater microcosms at 5 degrees C. Total cell counts were monitored by acridine orange epifluorescence, metabolic activity by direct viable counts, and culturability by plate counts on selective and nonselective media. Whereas total counts remained constant, plate counts of V. vulnificus suggested nonculturability by day 24. In contrast, direct viable counts indicated significant cell viability throughout 32 days of incubation. As an indication of the metabolic changes that occurred as cells entered the state of nonrecoverability, membrane fatty acid analyses were performed. At the point of nonculturability of V. vulnificus, the major fatty acid species (C16 and C16:1) had decreased 57% from the T0 level, concomitant with the appearance of several short-chain acids. Although the bacteria were still recoverable, a similar trend was observed with E. coli. Electron microscopy of nonculturable V. vulnificus showed that the cells were rounded and reduced in size and contained fewer ribosomes. Mouse infectivity studies conducted with these cells suggested loss of virulence.     

Transduction of Escherichia coli by bacteriophage P1 in soil

Transduction of Escherichia coli W3110(R702) and J53(RP4) (10(4) to 10(5) CFU/g of soil) by lysates of temperature-sensitive specialized transducing derivatives of bacteriophage P1 (10(4) to 10(5) PFU/g of soil) (P1 Cm cts, containing the resistance gene for chloramphenicol, or P1 Cm cts::Tn501, containing the resistance genes for chloramphenicol and mercury [Hg]) occurred in soil amended with montmorillonite or kaolinite and adjusted to a -33-kPa water tension. In nonsterile soil, survival of introduced E. coli and the numbers of E. coli transductants resistant to chloramphenicol or Hg were independent of the clay amendment. The numbers of added E. coli increased more when bacteria were added in Luria broth amended with Ca and Mg (LCB) than when they were added in saline, and E. coli transductants were approximately 1 order of magnitude higher in LCB; however, the same proportion of E. coli was transduced with both types of inoculum. In sterile soil, total and transduced E. coli and P1 increased by 3 to 4 logs, which was followed by a plateau when they were inoculated in LCB and a gradual decrease when they were inoculated in saline. Transduction appeared to occur primarily in the first few days after addition of P1 to soil. The transfer of Hg or chloramphenicol resistance from lysogenic to nonlysogenic E. coli by phage P1 occurred in both sterile and nonsterile soils. On the basis of heat-induced lysis and phenotype, as well as hybridization with a DNA probe in some studies, the transductants appeared to be the E. coli that was added. Transduction of indigenous soil bacteria was not unequivocally demonstrated.(ABSTRACT TRUNCATED AT 250 WORDS)     

Transduction of Escherichia coli by bacteriophage P1 in soil.

Transduction of Escherichia coli W3110(R702) and J53(RP4) (10(4) to 10(5) CFU/g of soil) by lysates of temperature-sensitive specialized transducing derivatives of bacteriophage P1 (10(4) to 10(5) PFU/g of soil) (P1 Cm cts, containing the resistance gene for chloramphenicol, or P1 Cm cts::Tn501, containing the resistance genes for chloramphenicol and mercury [Hg]) occurred in soil amended with montmorillonite or kaolinite and adjusted to a -33-kPa water tension. In nonsterile soil, survival of introduced E. coli and the numbers of E. coli transductants resistant to chloramphenicol or Hg were independent of the clay amendment. The numbers of added E. coli increased more when bacteria were added in Luria broth amended with Ca and Mg (LCB) than when they were added in saline, and E. coli transductants were approximately 1 order of magnitude higher in LCB; however, the same proportion of E. coli was transduced with both types of inoculum. In sterile soil, total and transduced E. coli and P1 increased by 3 to 4 logs, which was followed by a plateau when they were inoculated in LCB and a gradual decrease when they were inoculated in saline. Transduction appeared to occur primarily in the first few days after addition of P1 to soil. The transfer of Hg or chloramphenicol resistance from lysogenic to nonlysogenic E. coli by phage P1 occurred in both sterile and nonsterile soils. On the basis of heat-induced lysis and phenotype, as well as hybridization with a DNA probe in some studies, the transductants appeared to be the E. coli that was added. Transduction of indigenous soil bacteria was not unequivocally demonstrated.(ABSTRACT TRUNCATED AT 250 WORDS)     

Maintenance of plasmids pBR322 and pUC8 in nonculturable Escherichia coli in the marine environment.

Maintenance of plasmids pBR322 and pUC8 in Escherichia coli that was nonculturable after exposure to seawater was studied. E. coli JM83 and JM101, which contained plasmids pBR322 and pUC8, respectively, were placed in sterile artificial seawater for 21 days. Culturability was determined by plating on both nonselective and selective agar, and plasmid maintenance was monitored by direct isolation of plasmid nucleic acid from bacteria collected on Sterivex filters. E. coli JM83 became nonculturable after incubation for 6 days in seawater yet maintained plasmid pBR322 for the entire period of the study, i.e., 21 days. E. coli JM101 was nonculturable after incubation in seawater for 21 days and also maintained plasmid pUC8 throughout the duration of the microcosm experiment. Direct counts of bacterial cells did not change significantly during exposure to seawater, even though plate counts yielded no viable (i.e., platable) cells. We concluded that E. coli cells are capable of maintaining high-copy-number plasmids, even when no longer culturable, after exposure to the estuarine or marine environment.     

Retention of Virulence in a Viable but Nonculturable Edwardsiella tarda Isolate

Edwardsiella tarda is pathogen of fish and other animals. The aim of this study was to investigate the viable but nonculturable (VBNC) state and virulence retention of this bacterium. Edwardsiella tarda CW7 was cultured in sterilized aged seawater at 4°C. Total cell counts remained constant throughout the 28-day period by acridine orange direct counting, while plate counts declined to undetectable levels (<0.1 CFU/ml) within 28 days by plate counting. The direct viable counts, on the other hand, declined to ca. 10⁹ CFU/ml active cells and remained fairly constant at this level by direct viable counting. These results indicated that a large population of cells existed in a viable but nonculturable state. VBNC E. tarda CW7 could resuscitate in experimental chick embryos and in the presence of nutrition with a temperature upshift. The resuscitative times were 6 days and 8 days, respectively. The morphological changes of VBNC, normal, and resuscitative E. tarda CW7 cells were studied with a scanning electron microscope. The results showed that when the cells entered into the VBNC state, they gradually changed in shape from short rods to coccoid and decreased in size, but the resuscitative cells did not show any obvious differences from the normal cells. The VBNC and the resuscitative E. tarda CW7 cells were intraperitoneally inoculated into turbot separately, and the fish inoculated with the resuscitative cells died within 7 days, which suggested that VBNC E. tarda CW7 might retain pathogenicity.     

Maintenance of plasmids pBR322 and pUC8 in nonculturable Escherichia coli in the marine environment

Maintenance of plasmids pBR322 and pUC8 in Escherichia coli that was nonculturable after exposure to seawater was studied. E. coli JM83 and JM101, which contained plasmids pBR322 and pUC8, respectively, were placed in sterile artificial seawater for 21 days. Culturability was determined by plating on both nonselective and selective agar, and plasmid maintenance was monitored by direct isolation of plasmid nucleic acid from bacteria collected on Sterivex filters. E. coli JM83 became nonculturable after incubation for 6 days in seawater yet maintained plasmid pBR322 for the entire period of the study, i.e., 21 days. E. coli JM101 was nonculturable after incubation in seawater for 21 days and also maintained plasmid pUC8 throughout the duration of the microcosm experiment. Direct counts of bacterial cells did not change significantly during exposure to seawater, even though plate counts yielded no viable (i.e., platable) cells. We concluded that E. coli cells are capable of maintaining high-copy-number plasmids, even when no longer culturable, after exposure to the estuarine or marine environment.     

Examination of recovery in vitro and in vivo of nonculturable Escherichia coli O157:H7

Escherichia coli O157:H7 (strains ATCC 43895 and FO46) became nonculturable in sterile, distilled, deionized water or after exposure to chlorine. Recovery of nonculturable E. coli O157:H7 was examined by in vitro and in vivo methods. The decline in culturability of starved E. coli O157:H7 was measured by plate count on rich medium. Recovery in vitro of nonculturable cells was conducted with media amended with catalase or sodium pyruvate; however, there was no apparent increase over culturable cell counts on amended versus nonamended media. Although nonculturable E. coli O157:H7 did not recover under in vitro conditions, a mouse model was used to determine if in vivo conditions would provide sufficient conditions for recovery of nonculturable E. coli O157:H7. In separate studies, mice were orally challenged with starvation-induced nonculturable cells (FO46) or chlorine-induced nonculturable cells (43895 and FO46). Passage through the mouse gastrointestinal tract had no effect on recovery of nonculturable (starvation or chlorine induced) E. coli O157:H7 (43895 or FO46), based on analysis of fecal samples. Mouse kidneys were assayed for the presence of Shiga toxin using the Vero cell assay. Differences in cytotoxicity towards Vero cells from kidney samples of mice receiving nonculturable cells and control mice were not significant, suggesting a loss of virulence.     

Characterization and resuscitation of viable but nonculturable <Emphasis Type="Italic">Vibrio alginolyticus</Emphasis> VIB283

The aim of this study was to investigate the viable but nonculturable (VBNC) state of the bacterium. Vibrio alginolyticus VIB283 was cultured in sterilized seawater microcosm at 4°C. Culturability of the cells in the microcosm was monitored by spread plate count (PC) on 2216E agar, PCs declined to undetectable levels (<0.1 CFU/ml) within 90 days. Total cell counts remained constant throughout the period as determined by acridine orange direct count (AODC). The direct viable counts, on the other hand, declined from 10¹⁰ to 10⁹ CFU/ml active cells and remained fairly constant at this level by direct viable count (DVC), which indicated that a large population of cells entered into the VBNC state. The VBNC cells could be resuscitated by temperature upshift with and without the presence of nutrition. The resuscitated time were 16 h and 8 days respectively. The resuscitation was not achieved in chick embryos. The morphology of the VBNC, normal and resuscitated cells was studied with scanning electron microscope and flow cytometry. The cells changed from rod or arc to coccoid and decreased in size when entered into the VBNC state. The resuscitated and the normal cells had almost no morphological differences.     

Potential for gene transfer from recombinantEscherichia coli K-12 used in bovine somatotropin production to indigenous bacteria in river water

Summary This study examined the transfer of the plasmid pBGH1, an expression vector for bovine somatotropin (BST), fromEscherichia coli K-12 strain W3110G [pBGH1] to indigenous microorganisms present in flasks containing Missouri River water. Strain LBB269 is a nalidixic acid-resistant derivative of W3110G which was used as a plasmid-free control strain in these studies. Water samples were inoculated with strains W3110G [pBGH1] and LBB269; after 21 days of incubation the number of viable colony-forming units (CFU) of W3110G [pBGH1] and LBB269 were reduced from an initial level of about 1×10⁷ CFU per ml to less than 1 CFU per 100 ml. At this time indigenous microbes resistant to both ampicillin and tetracycline (the antibiotic resistance markers on pBGH1) were isolated from 100 ml of water from each of the flasks inoculated with either strain W3110G [pBGH1] or LBB269. Plasmid DNA was isolated from these organisms and examined for sequences containing the gene for BST from pBGH1, using a polymerase chain reaction (PCR) assay. As expected, the day 0 sample from the flask inoculated withE. coli K-12 strain W3110G [pBGH1] gave a positive PCR response and the day 0 sample from the flask inoculated withE. coli K-12 strain LBB269 gave a negative PCR response. All of the day 21 samples containing indigenous microbes isolated from flasks that were inoculated with either W3110G [pBGH1] or LBB269 were negative in the PCR assay, indicating that the target sequence from pBGH1 was not present in any of these indigenous microorganisms. The results of this particular assay indicate that pBGH1 or the portion of pBGH1 including the BST structural gene had not been transferred from W3110G [pBGH1] to indigenous microbial inhabitants of the Missouri River water flasks during this study.     

Characterization of the gcd gene from Escherichia coli K-12 W3110 and regulation of its expression.

DNA sequence and expressional analyses of the gcd gene of Escherichia coli K-12 W3110 revealed that two promoters that were detected were regulated negatively by cyclic AMP and positively by oxygen. Sequence conservation of the gcd gene between E. coli K-12 W3110 and PPA42 suggests that glucose dehydrogenase is required for the E. coli cells, even though it ordinarily exists as an apoprotein.     

Inducible gene expression by nonculturable bacteria in milk after pasteurization

The viability of bacteria in milk after heat treatments was assessed by using three different viability indicators: (i) CFU on plate count agar, (ii) de novo expression of a gfp reporter gene, and (iii) membrane integrity based on propidium iodide exclusion. In commercially available pasteurized milk, direct viable counts, based on dye exclusion, were significantly (P < 0.05) higher than viable cell counts determined from CFU, suggesting that a significant subpopulation of cells in pasteurized milk are viable but nonculturable. Heating milk at 63.5 degrees C for 30 min resulted in a >4-log-unit reduction in the number of CFU of Escherichia coli and Pseudomonas putida that were marked with lac-inducible gfp. However, the reduction in the number of gfp-expressing cells of both organisms under the same conditions was <2.5 log units. These results demonstrate that a substantial portion of cells rendered incapable of forming colonies by heat treatment are metabolically active and are able to transcribe and translate genes de novo.     

Recovery of hydrogen peroxide-sensitive culturable cells of Vibrio vulnificus gives the appearance of resuscitation from a viable but nonculturable state

The viabilities of five strains of Vibrio vulnificus were evaluated during the storage of the organisms in sterile seawater at 5 degrees C. The number of CFU was measured by plate count methods on rich media. The total cell numbers were determined by direct microscopic count methods. The titer of CFU declined logarithmically to undetectable levels over a period of 2 to 3 weeks, while the total cell numbers were unchanged. Midway through each study, higher culturable cell counts began to be observed on plates containing catalase or sodium pyruvate; during the latter stages of the study, the plate counts on such media were up to 1,000-fold higher than those on unsupplemented plates. Because autoclaving is known to generate hydrogen peroxide in rich media, and because catalase and sodium pyruvate are known to eliminate hydrogen peroxide, it appears that the conditions of the experiments led to the selection of a hydrogen peroxide-sensitive culturable cell subpopulation. At the time of the final stage of the decline in viability of each culture, hydrogen peroxide-sensitive cells were the only culturable cells present. Warming samples of the cultures to room temperature led to the growth of these residual culturable cells, utilizing nutrients provided by the nonculturable cells. The cells that grew recovered hydrogen peroxide resistance. When mixtures of culturable and nonculturable cells were diluted to the point where only nonculturable cells were present, or when the hydrogen peroxide-sensitive culturable cells had declined to undetectable levels, warming had no effect; no culturable cells were recovered. Warming has been reported to "resuscitate" nonculturable cells. Recognition of the existence of hydrogen peroxide-sensitive culturable cell populations, as well as their ability to grow to high levels in the warmed seawater microcosms, leads instead to the conclusion that while warming permits culturable cells to grow, it has no effect on nonculturable cells.     

Presence and growth of naturalized Escherichia coli in temperate soils from Lake Superior watersheds

The presence of Escherichia coli in water is used as an indicator of fecal contamination, but recent reports indicate that soil populations can also be detected in tropical, subtropical, and some temperate environments. In this study, we report that viable E. coli populations were repeatedly isolated from northern temperate soils in three Lake Superior watersheds from October 2003 to October 2004. Seasonal variation in the population density of soilborne E. coli was observed; the greatest cell densities, up to 3 x 10(3) CFU/g soil, were found in the summer to fall (June to October), and the lowest numbers, < or =1 CFU/g soil, occurred during the winter to spring months (February to May). Horizontal, fluorophore-enhanced repetitive extragenic palindromic PCR (HFERP) DNA fingerprint analyses indicated that identical soilborne E. coli genotypes, those with > or =92% similarity values, overwintered in frozen soil and were present over time. Soilborne E. coli strains had HFERP DNA fingerprints that were unique to specific soils and locations, suggesting that these E. coli strains became naturalized, autochthonous members of the soil microbial community. In laboratory studies, naturalized E. coli strains had the ability to grow and replicate to high cell densities, up to 4.2 x 10(5) CFU/g soil, in nonsterile soils when incubated at 30 or 37 degrees C and survived longer than 1 month when soil temperatures were < or =25 degrees C. To our knowledge, this is the first report of the growth of naturalized E. coli in nonsterile, nonamended soils. The presence of significant populations of naturalized populations of E. coli in temperate soils may confound the use of this bacterium as an indicator of fecal contamination.     

Formation of nonculturable Escherichia coli in drinking water

AIMS: To examine whether incubation of Escherichia coli in nondisinfected drinking water result in development of cells that are not detectable using standard procedures but maintain a potential for metabolic activity and cell division. METHODS AND RESULTS: Survival and detectability of four different E. coli strains were studied using drinking water microcosms and samples from contaminated drinking water wells. Recovery of E. coli was compared using different cultivation-dependent methods, fluorescence in situ hybridization (FISH) using specific oligonucleotide probes, direct viable counts (DVC), and by enumeration of gfp-tagged E. coli (green fluorescent protein, GFP). Two levels of stress responses were observed after incubation of E. coli in nondisinfected drinking water: (i) the presence of cells that were not detected using standard cultivation methods but could be cultivated after gentle resuscitation on nonselective nutrient-rich media, and (ii) the presence of cells that responded to nutrient addition but could only be detected by cultivation-independent methods (DVC, FISH and GFP). Collectively, the experiments demonstrated that incubation for 20-60 days in nondisinfected drinking water resulted in detection of only 0.7-5% of the initial E. coli population using standard cultivation methods, whereas 1-20% could be resuscitated to a culturable state, and 17-49% could be clearly detected using cultivation-independent methods. CONCLUSIONS: Resuscitation of stressed E. coli on nonselective nutrient-rich media increased cell counts in drinking water using both traditional (CFU), and cultivation-independent methods (DVC, FISH and GFP). The cultivation-independent methods resulted in detection of 10-20 times more E. coli than the traditional methods. The results indicate that a subpopulation of substrate-responsive but apparent nonculturable E. coli may develop in drinking water during long-term starvation survival. SIGNIFICANCE AND IMPACT OF THE STUDY: The existence of substrate-responsive but nonculturable cells should be considered when evaluating the survival potential of E. coli in nondisinfected drinking water.     

Green fluorescent protein-based direct viable count to verify a viable but non-culturable state of Salmonella typhi in environmental samples.

The gfp-tagging method and lux-tagging method were compared to select a better method for verifying a viable but nonculturable (VBNC) state of bacteria in the environment. An environmental isolate of Salmonella typhi was chromosomally marked with a gfp gene encoding green fluorescent protein (GFP). The hybrid transposon mini-Tn5 gfp was transconjugated from E. coli to S. typhi. Using the same method, S. typhi was chromosomally marked with luxAB genes encoding luciferase. The survival of gfp-tagged S. typhi introduced into groundwater microcosms was examined by GFP-based plate count, total cell count, and a direct viable count method. In microcosms containing lux-tagged S. typhi, luminescence-based plate count and the measurement of bioluminescence of each microcosm sample were performed. In microcosms containing lux-tagged S. typhi, viable but nonculturable cells could not be detected by using luminometry. As no distinguishable luminescence signals from the background signals were found in samples containing no culturable cells, a VBNC state of S. typhi could not be verified in lux-based systems. However, comparison between GFP-based direct viable counts and plate counts was a good method for verifying the VBNC state of S. typhi. Because GFP-based direct viable count method provided a direct and precise estimation of viable cells of introduced bacteria into natural environments, it can be used for verifying the VBNC state of bacteria in environmental samples.     

Enumeration of viable E. coli in rivers and wastewaters by fluorescent in situ hybridization

A combination of direct viable count (DVC) and fluorescent in situ hybridization (FISH) procedures was used to enumerate viable Escherichia coli in river waters and wastewaters. A probe specific for the 16S rRNA of E. coli labeled with the CY3 dye was used; enumeration of hybridized cells was performed by epifluorescence microscopy. Data showed that the method was able to accurately enumerate a minimum of 3000 viable E. coli among a large number of non-fecal bacteria. When applied to river water and wastewater samples, the DVC-FISH method gave systematically higher E. coli counts than a reference culture-based method (miniaturized MPN method). The ratio between both counts (DVC-FISH/MPN) increased with decreasing abundance of culturable E. coli indicating that the proportion of viable but non-culturable (VBNC) E. coli (detectable by the DVC-FISH procedure and not by a culture-based method) was higher in low contaminated environments. We hypothesized that the more stressing conditions, i.e. nutritional stress and sunlight effect, met in low contaminated environments were responsible for the larger fraction of VBNC E. coli. A survival experiment, in which sterile mineral water was inoculated with a pure E. coli strain and incubated, confirmed that stressing conditions induced the apparition of non-culturable E. coli detectable by the DVC-FISH procedure. The analysis of the E. coli concentration along a Seine river longitudinal profile downstream a large input of fecal bacteria by a WWTP outfall showed an increasing fraction of VBNC E. coli with increasing residence time of the E. coli in the river after release. These data suggest that the DVC-FISH method is useful tool to analyze the dynamics of fecal bacteria in river water.     

Predominance of Nonculturable Cells of the Biocontrol Strain Pseudomonas fluorescens CHA0 in the Surface Horizon of Large Outdoor Lysimeters

The persistence of the biocontrol agent Pseudomonas fluorescens CHA0 in the surface horizon of 12 large outdoor lysimeters planted with winter wheat, Phacelia tanacetifolia followed by spring wheat, or maize was monitored for 1 year. Soil was inoculated with a spontaneous rifampin-resistant mutant (CHA0-Rif) of CHA0, and the strain was studied by using colony counts, Kogure's direct viable counts, and total counts (immunofluorescence). The number of culturable cells of the inoculant decreased progressively from 8 to 2 log CFU/g of soil or lower. However, culturable cells of CHA0-Rif accounted for less than 1% of the total cells of the inoculant 8 months after release in autumn. Since viable but nonculturable cells represented less than a quarter of the latter, most cells of CHA0-Rif in soil were thus inactive-dormant or dead at that time. Nonculturable cells of the inoculant were predominant also in the surface horizon of the lysimeters inoculated in the spring, and a significant fraction of them were viable. Results suggest that the occurrence of nonculturable cells of CHA0-Rif was influenced by climatic factors (water availability and soil temperature) and the abundance of roots in soil. The fact that the inoculant persisted as mixed populations of cells of different physiological states, in which nonculturable cells were predominant, needs to be taken into account when assessing the autecology of wild-type or genetically modified pseudomonads released into the soil ecosystem.