Survival of Aeromonas salmonicida in lake water.

The survival of Aeromonas salmonicida subsp. salmonicida in lake water was investigated by using a variety of techniques. They included acridine orange epifluorescence, respiration, cell culture, cell revival, flow cytometry, plasmid maintenance, and membrane fatty acid analysis. During a 21-day study, A. salmonicida became nonculturable in sterile lake water samples. Flow cytometry and direct microscopy indicated that cells were present. Although the nonculturable cells could not be revived, the recovery method did indicate that the presence of low numbers of culturable cells within samples could produce misleading results. Plasmid DNA, genomic DNA, and RNA were maintained in the nonculturable cells; in addition, changes in the fatty acid profiles were also detected. Although viability could not be proven, it was shown that the morphological integrity of nonculturable cells was maintained.     

Survival of Aeromonas salmonicida in lake water

The survival of Aeromonas salmonicida subsp. salmonicida in lake water was investigated by using a variety of techniques. They included acridine orange epifluorescence, respiration, cell culture, cell revival, flow cytometry, plasmid maintenance, and membrane fatty acid analysis. During a 21-day study, A. salmonicida became nonculturable in sterile lake water samples. Flow cytometry and direct microscopy indicated that cells were present. Although the nonculturable cells could not be revived, the recovery method did indicate that the presence of low numbers of culturable cells within samples could produce misleading results. Plasmid DNA, genomic DNA, and RNA were maintained in the nonculturable cells; in addition, changes in the fatty acid profiles were also detected. Although viability could not be proven, it was shown that the morphological integrity of nonculturable cells was maintained.     

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.     

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.     

Survival and detection of bacteria in an aquatic environment

A genetically engineered plasmid, pPSA131, was used as a DNA probe to detect homologous DNA in Escherichia coli HB101(pPSA131) after it was mixed with aquatic microorganisms from Lake Mead, Nevada, water samples. An isolate from the pLAFR1 chromosomal library of Pseudomonas syringae Cit 7 was used to detect parent P. syringae Cit 7 that had been mixed with Lake Mead water. E. coli(pPSA131) was kept in variously treated samples of lake water or buffer, and its survival was measured by viable cell counting on modified Luria-Bertani (LB) agar. Full-strength LB agar proved better than 0.1 x LB agar at recovering E. coli(pPSA131) after survival in low-nutrient environments. Survival of E. coli(pPSA131) remained high in filtered (0.22-micron pore size) lake water and salts buffer on both selective and nonselective agars but was lower in untreated lake water or lake water filtered with a 0.8-micron-pore-size membrane. Total recoverable colonies grown on LB agar were higher when lake water was filter treated (0.8-micron pore size) than when lake water was untreated. Microorganisms recovered from lake water alone grew rapidly on nonselective media, probably because of the "bottle effect." After being mixed with Lake Mead water, E. coli(pPSA131) and P. syringae were detected by colony blotting with non-radioactively labeled DNA probes. E. coli(pPSA131) were recovered at three times during 48 h from variously treated samples of lake water and from a mixture with Lake Mead water organisms. Colonies were supported on either nonselective or selective agar for comparison.(ABSTRACT TRUNCATED AT 250 WORDS)     

Survival and detection of bacteria in an aquatic environment.

A genetically engineered plasmid, pPSA131, was used as a DNA probe to detect homologous DNA in Escherichia coli HB101(pPSA131) after it was mixed with aquatic microorganisms from Lake Mead, Nevada, water samples. An isolate from the pLAFR1 chromosomal library of Pseudomonas syringae Cit 7 was used to detect parent P. syringae Cit 7 that had been mixed with Lake Mead water. E. coli(pPSA131) was kept in variously treated samples of lake water or buffer, and its survival was measured by viable cell counting on modified Luria-Bertani (LB) agar. Full-strength LB agar proved better than 0.1 x LB agar at recovering E. coli(pPSA131) after survival in low-nutrient environments. Survival of E. coli(pPSA131) remained high in filtered (0.22-micron pore size) lake water and salts buffer on both selective and nonselective agars but was lower in untreated lake water or lake water filtered with a 0.8-micron-pore-size membrane. Total recoverable colonies grown on LB agar were higher when lake water was filter treated (0.8-micron pore size) than when lake water was untreated. Microorganisms recovered from lake water alone grew rapidly on nonselective media, probably because of the "bottle effect." After being mixed with Lake Mead water, E. coli(pPSA131) and P. syringae were detected by colony blotting with non-radioactively labeled DNA probes. E. coli(pPSA131) were recovered at three times during 48 h from variously treated samples of lake water and from a mixture with Lake Mead water organisms. Colonies were supported on either nonselective or selective agar for comparison.(ABSTRACT TRUNCATED AT 250 WORDS)     

Survival of genetically-marked Aeromonas hydrophila in water

Survival of a genetically-marked Aeromonas hydrophila was monitored in water microcosms. There was no apparent loss of a marker plasmid which encoded the xylE reporter gene during prolonged incubation in lake water. Survival was best in sterile lake water but in sea water, cells died rapidly during the first 9 d, recovered up to day 12 and thereafter numbers fell up to 28 d accompanied by loss of the plasmid in a proportion of the cells.     

Determination of plasmid DNA concentration maintained by nonculturable Escherichia coli in marine microcosms.

The concentration of plasmid pBR322 DNA in nonculturable Escherichia coli JM83 was measured to determine whether the plasmid concentration changed during survival of E. coli in marine and estuarine water. E. coli JM83 containing the plasmid pBR322 was placed in both sterile seawater and sterile estuarine water and analyzed for survival (i.e., culturability) and plasmid maintenance. The concentration of pBR322 DNA remained stable in E. coli JM83 for 28 days in an artificial seawater microcosm, even though nonculturability was achieved within 7 days. E. coli JM83 incubated in sterile natural seawater or sterile estuarine water did not reach nonculturability within 30 days. Under all three conditions, plasmid pBR322 DNA was maintained at approximately the initial concentration. Cloning of DNA into the plasmid pUC8 did not alter the ability of E. coli to maintain vector plasmid DNA, even when the culture was in the nonculturable state, but the concentration of plasmid DNA decreased with time in the microcosm. We conclude that E. coli is able to maintain plasmid DNA while in the nonculturable state and that the concentration at which the plasmid is maintained appears to be dependent upon the copy number of the plasmid and/or the presence of foreign DNA.     

Determination of plasmid DNA concentration maintained by nonculturable Escherichia coli in marine microcosms.

The concentration of plasmid pBR322 DNA in nonculturable Escherichia coli JM83 was measured to determine whether the plasmid concentration changed during survival of E. coli in marine and estuarine water. E. coli JM83 containing the plasmid pBR322 was placed in both sterile seawater and sterile estuarine water and analyzed for survival (i.e., culturability) and plasmid maintenance. The concentration of pBR322 DNA remained stable in E. coli JM83 for 28 days in an artificial seawater microcosm, even though nonculturability was achieved within 7 days. E. coli JM83 incubated in sterile natural seawater or sterile estuarine water did not reach nonculturability within 30 days. Under all three conditions, plasmid pBR322 DNA was maintained at approximately the initial concentration. Cloning of DNA into the plasmid pUC8 did not alter the ability of E. coli to maintain vector plasmid DNA, even when the culture was in the nonculturable state, but the concentration of plasmid DNA decreased with time in the microcosm. We conclude that E. coli is able to maintain plasmid DNA while in the nonculturable state and that the concentration at which the plasmid is maintained appears to be dependent upon the copy number of the plasmid and/or the presence of foreign DNA.     

Survival and Activity of lux-Marked Aeromonas salmonicida in Seawater

The fish pathogen Aeromonas salmonicida was chromosomally marked with genes encoding bacterial luciferase, luxAB, isolated from Vibrio fischeri, resulting in constitutive luciferase production. During exponential growth in liquid batch culture, luminescence was directly proportional to biomass concentration, and luminometry provided a lower detection limit of approximately 10(sup3) cells ml(sup-1), 1 order of magnitude more sensitive than enzyme-linked immunosorbent assay detection. In sterile seawater at 4(deg)C, lux-marked A. salmonicida entered a dormant, nonculturable state and population activity decreased rapidly. The activity per viable cell, however, increased by day 4, indicating that a proportion of the population remained active and culturable. Putative dormant cells were not resuscitated after the addition of a range of substrates.     

Resident enhanced repair: novel repair process action on plasmid DNA transformed into Escherichia coli K-12.

The survival of UV-irradiated DNA of plasmid NTP16 was monitored after its transformation into recipient cells containing an essentially homologous undamaged plasmid, pLV9. The presence of pLV9 resulted in a substantial increase in the fraction of damaged NTP16 molecules which survived in the recipient cells. This enhanced survival requires the host uvrA+ and uvrB+ gene products, but not the host recA+ gene product. The requirement for both homologous DNA and the uvrA+ and uvrB+ gene products suggests that a novel repair process may act on plasmid DNA. Possible mechanisms for this process are considered.     

Electrostatic mechanism of survival of virulent Aeromonas salmonicida strains in river water.

The ecological mechanism of survival of Aeromonas salmonicida, the bacterial pathogen of fish furunculosis, in river water was investigated by laboratory-based experiments with two virulent strains (which were autoagglutinating) and two virulent strains (which were nonagglutinating). A difference in net electrical charge of A. salmonicida cells was detected by electrophoresis; cells of the virulent strains were negative, whereas cells of the avirulent strains were positive. Despite the loss of viable cells within a week in distilled water and physiological saline (0.85% sodium chloride), the cells of the virulent strains survived for more than 15 weeks in the presence of diluted humic acid (10 micrograms/ml), tryptone (10 micrograms/ml), and cleaned river sand (100 g/100 ml of medium), but loss of viable cells occurred within 5 weeks in the absence of sand. The cells of the avirulent strains lost viability within 2 weeks with no relation to the presence of sand. Using ion-exchange columns, humic acid and the amino acids of tryptone were found to be anionic and cationic in water (pH 7.0), respectively. Sand particles had a high capacity to adsorb humic acid alone and amino acid-humic acid complexes. Thirty to fifty times the environmental concentration of amino acids (10 micrograms/ml) were accumulated on the surface of sand particles, thereby permitting only bacterial cells carrying net negative electrical charges (virulent cells) to survive for a long period on the surface of the sand particles. These electrostatic interrelationships among river sand, humic acid, and bacterial cells are closely implicated in the mechanism of long-term survival of virulent A. salmonicida in river sediments.     

Survival of cells and DNA of Aeromonas salmonicida released into aquatic microcosms

D. DEERE, J. PORTER, R.W. PICKUP AND C. EDWARDS. 1996. The survival of the bacterial fish pathogen Aeromonas salmonicida , and persistence of its DNA, were monitored in aquatic microcosms using selective culture and most probable number PCR. Bacterial cells and naked DNA were released into natural non-sterile microcosms consisting of lake sediment overlayered with lake water. Two different types of surface sediment were used. One was sandy in character, taken from the shoreline whilst the other was a littoral loamy surface mud. Inoculated cells and naked DNA became undetectable from water overlayers within 4 weeks of release. Colony counts of Aer. salmonicida declined below detectable limits after 4 weeks in loamy sediment or 7 weeks in sandy sediment; however, naked DNA and DNA from released cells remained detectable for more than 13 weeks.     

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.     

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.     

Starvation survival of the fish pathogen Aeromonas salmonicida in seawater

Abstract Three strains of the fish pathogenic bacterium Aeromonas salmonicida were examined with respect to their ability to survive in seawater. Five to seven days after plate counts decreased below the detection limit of 10 cells/ml, the population of respiring A. salmonicida cells comprised less than 4% of the initial total bacterial population. At this stage, samples were transferred either to sterile nutrient or to control flasks containing sterile nutrient-free medium. The addition of nutrients caused reappearance of growing bacteria, detected by plating on agar medium and an increase of the population of respiring bacteria to 85–95% of the total population. In a separate experiment it was shown that after more than six months of starvation at 15°C, a few of the starved A. salmonicida cells were able to regrow in liquid media after addition of nutrients, but not on agar media. These cells evade detection by direct microscopic respiratory measurement but appear to be reactivated after addition of nutrients.     

Competitive polymerase chain reaction for quantification of nonculturable Enterococcus faecalis cells in lake water

Among the survival strategies developed by bacteria when faced with adverse environmental conditions, the viable but nonculturable (VNC) state has been described. In this state, bacteria are unable to form colonies but are still alive and capable of metabolic activity. The VNC state has been described in numerous Gram-negative species, but recently also in Enterococcus faecalis, a Gram-positive species which can be found in the environment. In this study we describe a competitive PCR (cPCR) protocol to detect and quantify a specific sequence of DNA from culturable and nonculturable E. faecalis cells present in water samples. The protocol was found to be specific and capable of detecting amounts of DNA up to 0.1 pg corresponding to approximately 2 cells ml(-1). Moreover, it allows an internal standard to be used to quantify the amount of specific DNA present in samples from different environments. The application of this cPCR method to water samples from Lake Garda enabled us to demonstrate the presence of nonculturable forms of E. faecalis in lake water and to quantify their DNA and the corresponding concentration of nonculturable cells.     

Resuscitation of Vibrio cholerae O1 strain TSI-4 from a viable but nonculturable state by heat shock

Abstract Vibrio cholerae strain TSI-4 was incubated in an M9 salt solution at 15 °C for more than 100 days. The plate counts showed no viable cells on day 30, but a broth culture from that day showed the growth of bacteria. However, after 35 days the bacteria entered the nonculturable state, based on the assessment of both the plate counts and broth culture. A portion of the culture was heated at 45 °C for 1 min in a water bath and subsequently plated onto a nutrient agar plate. More than 1000 colonies were recovered after this heat-shock treatment. The recovered cells showed the same chromosomal DNA pattern in the restriction map and the same outer membrane protein pattern in SDS-PAGE. Recovery of viable cells by heat-shock was achieved in cultures grown on M9 salt but not from cultures grown in phosphate-buffered saline. This suggests that the presence of NH₄Cl in the M9 salt solution may support the growth of the bacteria in a low nutrient medium, while also playing an important role in resuscitation.