Survival of F-Specific RNA Coliphage, Feline Calicivirus, and Escherichia coli in Water: a Comparative Study

The relationship between the survival of enteric viral pathogens and their indicators (coliform bacteria and coliphages) is not well understood. We compared the survival rates of feline calicivirus (FCV), Escherichia coli, and a male-specific RNA coliphage MS2 at 4, 25, and 37°C for up to 28 days in dechlorinated water. The survival rates of E. coli and FCV, a surrogate of noroviruses (NV), had a high degree of correlation at 4 and 25°C, while MS2 phage survived significantly longer (P < 0.05) at these two temperatures. At 37°C, the survival rates for all three organisms were highly correlated. Decimal reduction values indicating the number of days needed for 90% reduction in titer (D values) decreased for all three organisms as storage temperatures increased. FCV had the shortest D value among all three organisms at all temperatures investigated. These findings indicate that F-specific RNA phages may be useful indicators of NV in the environment.     

Effects of temperature and host cell growth phase on replication of F-specific RNA coliphage Q beta.

Human enteric viruses have been found in groundwater in the absence of fecal coliforms. Because detection of human enteric viruses is costly, time-consuming, and lacking in sensitivity, F-specific RNA (FRNA) coliphages, which infect Escherichia coli by attachment to F pili, are being examined for suitability as indicators of human enteric viruses in groundwater. Temperatures and host cell growth conditions that constrain F-pilus expression will limit FRNA coliphage replication in groundwater and wastewater, as is desirable in an indicator. Below 25 degrees C F-pilus synthesis ceases; FRNA coliphage Qbeta did not replicate below this temperature in batch cultures. One-step replication studies indicated that the replicative cycle is prolonged and that fewer progeny are released as the temperature decreases. The decreases in phage replication observed in the one-step replication studies were a consequence of fewer cells infected as the temperature was lowered or as host cells entered stationary phase. The numbers of phage particles released from infected cells did not change. The minimum temperature for replication of Qbeta, 25 degrees C, is not maintained in wastewater and does not occur in Wisconsin groundwater. On the basis of temperature and host cell growth phase, we have concluded that extensive replication of FRNA coliphages does not occur in wastewater and groundwater in Wisconsin and areas with similar cool climates.     

Survival of Escherichia coli and Vibrio harveyi in Dead Sea water

Abstract When suspensions of Escherichia coli or the marine luminescent bacterium Vibrio harveyi were mixed with Dead Sea water, the number of viable bacteria decreased by 90% in a time varying from less than 1 h to several hours, depending on the bacterial strain tested. Survival was better at low temperatures, and diluting the Dead Sea water permitted prolonged survival of both coliform bacteria and V. harveyi . The death rate of E. coli in Dead Sea water was comparable to that in water from the Great Salt Lake (Utah). The high concentrations of calcium and magnesium in Dead Sea water, rather than the high total salinity, was identified as the main factor responsible for the rapid die-off. Exposure to direct solar irradiation significantly increased the die-off rate of E. coli in Dead Sea water.
Large numbers of coliform bacteria were recovered from the lake at distances of at least 20 m from a sewage discharge site on the western shore of the Dead Sea.     

Shiga toxin-producing Escherichia coli, faecal coliforms and coliphage in animal feeds

AIMS: Animal feeds (n = 226), collected from pastures or feeding troughs on UK farms and from feed manufacturers' bulk stores, were analysed for Escherichia coli harbouring shiga-toxin genes (stx), faecal coliforms, coliphages and stx-harbouring bacteriophages. METHODS AND RESULTS: Samples comprised of 79 fresh grasses, 26 silages and 121 dried or heat-processed feeds (DPF). Five of the 79 (6.3%) fresh grass samples contained stx(2)-E. coli. stx-E. coli were not detected in the silages or DPF that were examined. Faecal coliforms were detected in 75/79 (94.9%) of fresh grasses, 19/26 (73.1%) of silages and 36/121 (29.8%) of processed feeds. Coliphages were detected in 63/79 (79.7%) and 18/26 (69.2%) of fresh grasses and silages, respectively. Coliphages were isolated at a significantly lower prevalence of 5% (6/121) from processed feeds. Although stx(2)-phage was isolated from the enrichment of a single grass sample, stx-phages were not detected in any of the silage or processed feeds. We did not detect stx(1)-phage in any of the samples collected. CONCLUSIONS: Pastures have the potential to act as transmission vectors for stx-harbouring E. coli for grazed livestock. SIGNIFICANCE AND IMPACT OF THE STUDY: This is the first study to report on the prevalence of E. coli harbouring stx genes, faecal coliforms, coliphages and stx-harbouring bacteriophages in a range of feedstuffs destined for consumption by UK livestock. This study provides information on the risk of feeds to the spread of stx-phages between livestock and/or the environment.     

Chlorine sensitivity of feline calicivirus, a norovirus surrogate

The sensitivity to free chlorine of feline calicivirus (FCV), a norovirus surrogate, was examined relative to chlorine demand. When a crude suspension of FCV was treated with a sodium hypochlorite solution containing 10 microg/ml free chlorine, the extent of the decrease of viral infectivity clearly depended on the volume of the reaction mixture. The apparent sensitivity of FCV to free chlorine increased with the reduction of host cell debris, indicating that chlorine demand must be minimized to know the true sensitivity of the virus. We therefore partially purified the viruses from the host cell components and found that the infectivity of FCV was reduced by more than log 4.6 by 5 min of treatment with 300 ng/ml free chlorine.     

Survival of verocytotoxigenic Escherichia coli O157 in soil, water and on surfaces

Cattle and sheep are major reservoirs of Escherichia coli O157 and consequently these and certain other farm animals can pass out large numbers of this organism in their faeces. Thus the ability of the organism to survive in faeces, on pastureland and in associated water systems has important implications for its spread to crops by direct application of manure, by irrigation with infected water or directly to man by contact with animals or contaminated soil. Model systems were used to determine the persistence of the organism in river water, cattle faeces, soil cores and on stainless steel work surfaces. Survival of the organism was found to be greatest in soil cores containing rooted grass. Under these conditions viable numbers were shown to decline from approximately 10(8) g(-1) soil to between 10(6) and 10(7) g(-1) soil after 130 d. When the organism was inoculated into cattle faeces it remained detectable at high levels for more than 50 d. In contrast the organism survived much less readily in cattle slurry and river water where it fell in numbers from more than 10(6) ml(-1) to undetectable levels in 10 and 27 d, respectively. The survival of E. coli O157 was also investigated on stainless steel surfaces, where as air-dried deposits, it was shown to survive for periods in excess of 60 d. It was most stable at chill temperatures (4 degrees C) and viability was only partially reduced at 18 degrees C. In addition to stainless steel, the organism was shown to survive for extended periods on domestic (plastic) cutting boards, both at room and chill temperatures. Sanitizing agents, such as hypochlorites and a compound comprising both cationic and anionic-based active ingredients were found to be effective in killing various VTEC on stainless steel surfaces.     

Survival of genetically engineered Escherichia coli in natural soil and river water

Twelve derivatives of Escherichia coli strain HB101 which contained different sizes of plasmids ranging from 3.9 Kb to 48 Kb and encoding resistance to various antibiotics were used. When these organisms were introduced into natural river water, the population declined rapidly and by day 3, the majority (i.e. more than 99.9%) of them could no longer be detected on antibiotic-amended culture plates. If the river water was filter sterilized first, the added organisms maintained their population for up to 7 d without any significant decrease in numbers. Similar results were also observed in sterilized tap water or distilled water. This indicated that the disappearance of these organisms in the aquatic environment was caused mainly by biotic factor(s). The loss of the ability to grow in the presence of antibiotics by some of the E. coli was not observed unless they were allowed to grow in the antibiotic-free environment first. When the test organisms were added to natural silt loam, a large portion of the original population still remained viable after 16 d. There was no relationship between the percentage survival of E. coli in natural river water and the sizes of plasmid harboured. On the other hand, when these bacteria were added to natural soil, survival appeared to increase as plasmid size increased.     

Survival of genetically engineered Escherichia coli in natural soil and river water

Twelve derivatives of Escherichia coli strain HB101 which contained different sizes of plasmids ranging from 3.9 Kb to 48 Kb and encoding resistance to various antibiotics were used. When these organisms were introduced into natural river water, the population declined rapidly and by day 3, the majority (i.e. more than 99.9%) of them could no longer be detected on antibiotic-amended culture plates. If the river water was filter sterilized first, the added organisms maintained their population for up to 7 d without any significant decrease in numbers. Similar results were also observed in sterilized tap water or distilled water. This indicated that the disappearance of these organisms in the aquatic environment was caused mainly by biotic factor(s). The loss of the ability to grow in the presence of antibiotics by some of the E. coli was not observed unless they were allowed to grow in the antibiotic-free environment first. When the test organisms were added to natural silt loam, a large portion of the original population still remained viable after 16 d. There was no relationship between the percentage survival of E. coli in natural river water and the sizes of plasmid harboured. On the other hand, when these bacteria were added to natural soil, survival appeared to increase as plasmid size increased. and accepted 19 August 1989     

Tissue distribution of a coliphage and Escherichia coli in mussels after contamination and depuration

Experiments were undertaken to determine the tissue distribution of Escherichia coli and a coliphage after contamination of the common mussel (Mytilus edulis). Mussels were contaminated with high levels of feces-associated E. coli and a 22-nm icosahedral coliphage over a 2-day period in a flowing-seawater facility. After contamination, individual tissues were carefully dissected and assayed for E. coli and the coliphage. Contaminated mussels were also analyzed to determine the tissue distribution of the contaminants after 24- and 48-h depuration periods. The majority of each contaminant was located in the digestive tract (94 and 89% of E. coli and coliphage, respectively). Decreasing concentrations were found in the gills and labial palps, foot and muscles, mantle lobes, and hemolymph. Our results indicate that contamination above levels in water occurred only in the digestive tract. Contaminated mussels were depurated in a commercial-scale recirculating UV depuration system over a 48-h period. The percent reductions of E. coli occurred in the following order: digestive tract, hemolymph, foot and muscles, mantle lobes, and gills and labial palps. The percent reductions of the coliphage were different, occurring in the following order: hemolymph, foot and muscles, gills and labial palps, mantle lobes, and digestive tract. Our results clearly demonstrate that E. coli and the coliphage are differentially eliminated from the digestive tract. The two microorganisms are eliminated at similar rates from the remaining tissues. Our results also clearly show that the most significant coliphage retention after depuration for 48 h is in the digestive tract. Thus, conventional depuration practices are inappropriate for efficient virus elimination from mussels.     

Co-adaptation of Escherichia coli and coliphage lambda vir in continuous culture

Populations of the bacterium Escherichia coli and of its phage lambda vir appeared to equilibrate in continuous cultures. The bacterial end-populations were heterogeneous in respect of their resistance to lambda vir and their ability to utilize maltose. The most competitive of the selected bacteria were mutants which had a reduced rate of synthesis of lambda-receptor so as to become highly, but not totally, resistant to the phage. The coexisting phage had an increased affinity for the receptor and an altered antigenic specificity, suggesting adaptation of its adsorption site in response to the evolution of resistance in the bacteria.     

Behavior of coliphage lambda in hybrids between Escherichia coli and Salmonella

Salmonella typhosa hybrids able to adsorb lambda were obtained by mating S. typhosa recipients with Escherichia coli K-12 donors. After adsorption of wild-type lambda to these S. typhosa hybrids, no plaques or infective centers could be detected. E. coli K-12 gal(+) genes carried by the defective phage lambdadg were transduced to S. typhosa hybrids with HFT lysates derived from E. coli heterogenotes. The lysogenic state which resulted in the S. typhosa hybrids after gal(+) transduction differed from that of E. coli. Ability to produce lambda, initially present, was permanently segregated by transductants of the S. typhosa hybrid. S. typhosa lysogens did not lyse upon treatment for phage induction with mitomycin C, ultraviolet light, or heat in the case of thermoinducible lambda. A further difference in the behavior of lambda in Salmonella hybrids was the absence of zygotic induction of the prophage when transferred from E. coli K-12 donors to S. typhosa. A new lambda mutant class, capable of forming plaques on S. typhosa hybrids refractory to wild-type lambda, was isolated at low frequency by plating lambda on S. typhosa hybrid WR4254. Such mutants have been designated as lambdasx, and a mutant allele of lambdasx was located between the P and Q genes of the lambda chromosome. Plaques were formed also on the S. typhosa hybrid host with a series of lambda(i21) hybrid phages which contain the N gene of phage 21. The significance of these results in terms of Salmonella species as hosts for lambda is discussed.     

Survival and injury of Escherichia coli, Campylobacter jejuni, and Yersinia enterocolitica in stream water.

Experiments were done to describe the survival and injury of three strains each of enteropathogenic Escherichia coli, Yersinia enterocolitica, and Campylobacter jejuni in agricultural surface water. Bacterial suspensions within membrane diffusion chambers were immersed in two large vessels of stream water that were held at 6 and 16 degrees C and changed daily. The results of daily plate counts, using selective and nonselective media, revealed some variation among strains and genera. Injury increased rapidly in all of the bacteria examined during an initial 4-day period of population stability. Bacterial persistence was generally prolonged at 6 degrees C, while the occurrence of injury was directly related to temperature. However, both survival and injury in C. jejuni were less dependent on temperature, while Y. enterocolitica displayed the greatest survival at both 6 and 16 degrees C. These results suggest that surface water in the temperate zone might serve as a persistent vehicle for the transmission of these enteropathogenic bacteria between animals and humans.     

Survival of Escherichia coli and Campylobacter jejuni in untreated and filtered lake water

The survival of Campylobacter jejuni and Escherichia coli in lake water was studied using viable counts. Escherichia coli survived better than C. jejuni in all the test conditions studied. Both the species survived better in filtered than in untreated water. This suggests that predation and/or competition for nutrients affect the survival of both the species in an aquatic environment. Campylobacter jejuni survived less well in filtered autoclaved water and in 0.9% NaCl than in filtered water without autoclaving. The lack of some essential nutrients, which may be degraded by autoclaving, might explain these results.     

Survival of Escherichia coli and Campylobacter jejuni in untreated and filtered lake water

L.K. KORHONEN AND P.J. MARTIKAINEN. 1991. The survival of Campylobacter jejuni and Escherichia coli in lake water was studied using viable counts. Escherichia coli survived better than C. jejuni in all the test conditions studied. Both the species survived better in filtered than in untreated water. This suggests that predation and/or competition for nutrients affect the survival of both the species in an aquatic environment. Campylobacter jejuni survived less well in filtered autoclaved water and in 0.9% NaC1 than in filtered water without autoclaving. The lack of some essential nutrients, which may be degraded by autoclaving, might explain these results.     

Survival of chlorine-injured enterotoxigenic Escherichia coli in an in vitro water system

Survival of chlorine-injured and noninjured subpopulations of enterotoxigenic Escherichia coli was compared in KH2PO4-buffered water and chlorine-neutralized tap water. Injured cells were no less persistent than noninjured cells and did not exhibit limited survival as a consequence of chlorine injury. At high inoculum densities, some injured cells were able to repair, apparently owing to the accumulation of materials arising from the chlorination procedure.     

Survival of Escherichia coli O157:H7 in bottled natural mineral water

A non-verotoxin-producing isolate of Escherichia coli O157:H7 was inoculated at final concentrations of 10(3) or 10(6) ml-1 into natural non-carbonated mineral water (MW), sterile natural mineral water (SMW) and sterile distilled deionized water (SDDW) and stored at 15 degrees C for 10 weeks. Samples were examined every 7 d for the presence of E. coli O157:H7 using a resuscitative/selective agar procedure. The MW samples were also plated onto a non-selective agar, R2A, to enumerate E. coli O157:H7 and the autochthonous flora. There was a significant difference in the survival of E. coli O157:H7 (10(3) ml-1 inoculum) between the MW and the SDDW at time periods 0, 7, 14 (P < 0.005) 21, 28, 35 (P < 0.001) and 42 d (P < 0.05) and between the MW and the SMW at time periods 7, (P < 0.05) 14, 21 (P < 0.005) 28 (P < 0.01) and 35 d (P < 0.05), with the pathogen surviving longest in the MW samples. In contrast, at 10(6) ml-1, no significant differences in the survival of E. coli O157:H7 were observed between the water types. The presence of E. coli O157:H7 (10(3) ml-1) in the MW samples did not have an antagonistic effect on the recovery of the autochthonous flora. Transmission electron microscopy analysis demonstrated that the E. coli O157:H7 cells lyse during storage, releasing their contents into the surrounding environment. These substances may have been utilized by the autochthonous flora and thereby explain why the numbers of flora recovered from the inoculated MW samples were higher than those recovered from the uninoculated samples.     

Differential depuration of poliovirus, Escherichia coli, and a coliphage by the common mussel, Mytilus edulis

The elimination of sewage effluent-associated poliovirus, Escherichia coli, and a 22-nm icosahedral coliphage by the common mussel, Mytilus edulis, was studied. Both laboratory-and commercial-scale recirculating, UV depuration systems were used in this study. In the laboratory system, the logarithms of the poliovirus, E. coli, and coliphage levels were reduced by 1.86, 2.9, and 2.16, respectively, within 52 h of depuration. The relative patterns and rates of elimination of the three organisms suggest that they are eliminated from mussels by different mechanisms during depuration under suitable conditions. Poliovirus was not included in experiments undertaken in the commercial-scale depuration system. The differences in the relative rates and patterns of elimination were maintained for E. coli and coliphage in this system, with the logarithm of the E. coli levels being reduced by 3.18 and the logarithm of the coliphage levels being reduced by 0.87. The results from both depuration systems suggest that E. coli is an inappropriate indicator of the efficiency of virus elimination during depuration. The coliphage used appears to be a more representative indicator. Depuration under stressful conditions appeared to have a negligible affect on poliovirus and coliphage elimination rates from mussels. However, the rate and pattern of E. coli elimination were dramatically affected by these conditions. Therefore, monitoring E. coli counts might prove useful in ensuring that mussels are functioning well during depuration.     

Design and diversity in bacterial chemotaxis: a comparative study in Escherichia coli and Bacillus subtilis

Comparable processes in different species often involve homologous genes. One question is whether the network structure, in particular the feedback control structure, is also conserved. The bacterial chemotaxis pathways in E. coli and B. subtilis both regulate the same task, namely, excitation and adaptation to environmental signals. Both pathways employ many orthologous genes. Yet how these orthologs contribute to network function in each organism is different. To investigate this problem, we propose what is to our knowledge the first computational model for B. subtilis chemotaxis and compare it to previously published models for chemotaxis in E. coli. The models reveal that the core control strategy for signal processing is the same in both organisms, though in B. subtilis there are two additional feedback loops that provide an additional layer of regulation and robustness. Furthermore, the network structures are different despite the similarity of the proteins in each organism. These results demonstrate the limitations of pathway inferences based solely on homology and suggest that the control strategy is an evolutionarily conserved property.     

Survival of nonspecific porin-deficient mutants of Escherichia coli in black sea water

AIMS: The aim of this study was to investigate the links between survival of Escherichia coli in sea water microcosms in the laboratory and the presence of porins in the outer membrane. The E. coli strains studied were a wild-type strain and a series of outer membrane protein (omp) mutants. METHODS AND RESULTS: Bacteria were suspended in natural or filtered-autoclaved sea water microcosms and numbers determined over an incubation period by plate count and by count of cells capable of respiration. CONCLUSIONS: The type of omp mutation has a significant impact in bacterial survival. The double OmpC-OmpF mutant and the OmpR mutant (which was incapable of synthesizing OmpC and OmpF) survived poorly compared with single omp mutants and the wild-type strain. This suggests that these proteins are important in determining the entry of E. coli into the survival mode. The EnvZ mutant, which lacks the protein by which the cell senses some changes in the environment, survived as well as the wild-type strain when compared by plate counts and by respiring cell count. The loss of the EnvZ protein has no effect on survival but it could prevent the organism sensing the changes in the environment through which entry into the survival state is triggered. SIGNIFICANCE AND IMPACT OF THE STUDY: This work is another piece in the puzzle as to how bacteria survive stress conditions.