Pretreatment to reduce somatic salmonella phage interference with FRNA coliphage assays: successful use in a one-year survey of vulnerable groundwaters

Somatic salmonella (SS) phages were commonly found in higher numbers than F-specific RNA (FRNA) coliphages in a multi-site survey of contamination-vulnerable groundwaters. The relative abundance of SS phages required that a pretreatment procedure be implemented to reduce the SS phage content of samples before FRNA coliphage assay with Salmonella typhimurium WG49. Pretreatment involved selective SS phage removal by Salm. typhimurium WG45 cells. This pretreatment proved effective in producing interference-free samples throughout the one-year survey period and in seeded evaluation, was shown not to affect the detection of representative FRNA coliphage MS2. During the survey, 30 groundwater sites located in the continental United States, Puerto Rico and the Virgin Islands were examined for FRNA coliphages and SS phages at monthly intervals. FRNA coliphages were detected at six of the 30 sites and in 33 of 329 monthly samples. SS phages were also detected at six sites and in 28 of 329 monthly samples. Five of the phage-positive sites were positive for both phage groups. At those five sites, 58 monthly samples were collected during the survey period. Those 58 samples yielded an average FRNA coliphage concentration of 140 pfu per 100 1 of groundwater as compared to an average SS phage concentration of 565 pfu per 100 1 of groundwater. Twenty of the 58 samples were positive for both FRNA coliphages and SS phages. In those samples, FRNA coliphages were more abundant in five samples; SS phages were more abundant in 15 samples. Because these results demonstrate that SS phage levels may often exceed FRNA coliphage levels in environmental waters, it is clear that SS phage removal procedures will greatly enhance the effectiveness of the WG49-based FRNA coliphage assay.     

Factors influencing the replication of somatic coliphages in the water environment

The potential replication of somatic coliphages in the environment has been considered a drawback for their use as viral indicators, although the extent to which this affects their numbers in environmental samples has not been assessed. In this study, the replication of somatic coliphages in various conditions was assayed using suspensions containing naturally occurring somatic coliphages and Escherichia coli WG5, which is a host strain recommended for detecting somatic coliphages. The effects on phage replication of exposing strain WG5 and phages to a range of physiological conditions and the effects of the presence of suspended particles or other bacteria were also assayed. Phage replication was further tested using a strain of Klebsiella terrigena and naturally occurring E. coli cells as hosts. Our results indicate that threshold densities of both host bacterium and phages should occur simultaneously to ensure appreciable phage replication. Host cells originating from a culture in the exponential growth phase and incubation at 37 degrees C were the best conditions for phage replication in E. coli WG5. In these conditions the threshold densities required to ensure phage replication were about 10(4) host cells/ml and 10(3) phages/ml, or 10(3) host cells/ml and 10(4) phages/ml, or intermediate values of both. The threshold densities needed for phage replication were higher when the cells proceeded from a culture in the stationary growth phase or when suspended particles or other bacteria were present. Furthermore E. coli WG5 was more efficient in supporting phage replication than either K. terrigenae or E. coli cells naturally occurring in sewage. Our results indicate that the phage and bacterium densities and the bacterial physiological conditions needed for phage replication are rarely expected to be found in the natural water environments.     

Sequence variation among group III F-specific RNA coliphages from water samples and swine lagoons

Typing of F-specific RNA (FRNA) coliphages has been proposed as a useful method for distinguishing human from animal fecal contamination in environmental samples. Group II and III FRNA coliphages are generally associated with human wastes, but several exceptions have been noted. In the present study, we have genotyped and partially sequenced group III FRNA coliphage field isolates from swine lagoons in North Carolina (NC) and South Carolina (SC), along with isolates from surface waters and municipal wastewaters. Phylogenetic analysis of a region of the 5' end of the maturation protein gene revealed two genetically different group III FRNA subclusters with 36.6% sequence variation. The SC swine lagoon isolates were more closely related to group III prototype virus M11, whereas the isolates from a swine lagoon in NC, surface waters, and wastewaters grouped with prototype virus Q-beta. These results suggest that refining phage genotyping systems to discriminate M11-like phages from Q-beta-like phages would not necessarily provide greater discriminatory power in distinguishing human from animal sources of pollution. Within the group III subclusters, nucleotide sequence diversity ranged from 0% to 6.9% for M11-like strains and from 0% to 8.7% for Q-beta-like strains. It is demonstrated here that nucleotide sequencing of closely related FRNA strains can be used to help track sources of contamination in surface waters. A similar use of phage genomic sequence information to track fecal pollution promises more reliable results than phage typing by nucleic acid hybridization and may hold more potential for field applications.     

Sequence Variation among Group III F-Specific RNA Coliphages from Water Samples and Swine Lagoons

Typing of F-specific RNA (FRNA) coliphages has been proposed as a useful method for distinguishing human from animal fecal contamination in environmental samples. Group II and III FRNA coliphages are generally associated with human wastes, but several exceptions have been noted. In the present study, we have genotyped and partially sequenced group III FRNA coliphage field isolates from swine lagoons in North Carolina (NC) and South Carolina (SC), along with isolates from surface waters and municipal wastewaters. Phylogenetic analysis of a region of the 5′ end of the maturation protein gene revealed two genetically different group III FRNA subclusters with 36.6% sequence variation. The SC swine lagoon isolates were more closely related to group III prototype virus M11, whereas the isolates from a swine lagoon in NC, surface waters, and wastewaters grouped with prototype virus Q-beta. These results suggest that refining phage genotyping systems to discriminate M11-like phages from Q-beta-like phages would not necessarily provide greater discriminatory power in distinguishing human from animal sources of pollution. Within the group III subclusters, nucleotide sequence diversity ranged from 0% to 6.9% for M11-like strains and from 0% to 8.7% for Q-beta-like strains. It is demonstrated here that nucleotide sequencing of closely related FRNA strains can be used to help track sources of contamination in surface waters. A similar use of phage genomic sequence information to track fecal pollution promises more reliable results than phage typing by nucleic acid hybridization and may hold more potential for field applications.     

F-specific RNA bacteriophages and sensitive host strains in faeces and wastewater of human and animal origin

Faeces of humans, pigs, cattle and chickens were investigated for the presence of somatic coliphages, F-specific bacteriophages and Escherichia coli strains sensitive to infection by F-specific phages. Attention was given to the possible effect of age and use of antibiotics on the prevalence of the FRNA phages and sensitive E . coli strains. Somatic coliphages were often detected in high numbers in all types of faeces. In contrast, FRNA phages were rarely detected in faeces from humans and cattle but more often in faeces from pigs and adult chickens. Samples from young chickens (with or without antibiotics) were consistently positive for FRNA phages (up to 3 × 10⁶ pfu/g). F-specific RNA phages were found in substantial numbers (> 10³ pfu/ml) in a variety of wastewaters: domestic, hospital, slaughterhouses and occasionally in 'grey water'. Their origin in wastewater was not clear. Strains from faeces usually belonged to serogroups I and IV. These types were also found in wastewater, as were group II and III strains. Serogroup II phages were abundant in wastewater of human origin but rare in faeces. Escherichia coli strains sensitive to infection by F-specific phages were common in faeces (overall 290/1081: 27%). No strains with fully derepressed F-pilus synthesis were detected among the sensitive strains. It is concluded that the occurrence of F-specific RNA bacteriophages in water points to sewage pollution rather than faecal pollution; the mechanism of replication of these organisms in wastewater is not understood.     

Bacterial host strains that support replication of somatic coliphages

Somatic coliphages detected by Escherichia coli strain WG5 have been proposed as potential indicators of water quality. Their potential replication in the water environment is considered a drawback for their use as indicators. However, the contribution of replication outside the gut to the total numbers has never been quantified. It has not been determined either the fraction of bacterial strains that might support replication of phages detected by strain WG5 in the water environment. We examined the sensitivity of 291 host strains to 25 phages by streaking slants of the presumptive host strain onto an agar layer that contains bacteriophages, which gives a total of 7275 combinations (sensitivity tests). Only a 3.02% of the tests showed sensitivity. Additionally, six environmental strains were used as hosts to count phages in sewage and seawater. Phages isolated on these strains were used to infect strain WG5. The environmental strains detected 1 log₁₀ fewer phages than strain WG5 in sewage and seawater. The fraction of phages that were detected by the six strains and that also infected strain WG5 ranged from < 0.07% to < 2.0% of the total amount of bacteriophages detected by strain WG5 in the same samples. Our results confirm that less than 3% of naturally occurring hosts support replication of phages infecting E. coli. We conclude that the contribution of replication to the number of somatic coliphages detected in the aquatic environment is negligible. This revised version was published online in June 2006 with corrections to the Cover Date.     

F-specific RNA bacteriophages and sensitive host strains in faeces and wastewater of human and animal origin

Faeces of humans, pigs, cattle and chickens were investigated for the presence of somatic coliphages, F-specific bacteriophages and Escherichia coli strains sensitive to infection by F-specific phages. Attention was given to the possible effect of age and use of antibiotics on the prevalence of the FRNA phages and sensitive E. coli strains. Somatic coliphages were often detected in high numbers in all types of faeces. In contrast, FRNA phages were rarely detected in faeces from humans and cattle but more often in faeces from pigs and adult chickens. Samples from young chickens (with or without antibiotics) were consistently positive for FRNA phages (up to 3 x 10(6) pfu/g). F-specific RNA phages were found in substantial numbers (greater than 10(3) pfu/ml) in a variety of wastewaters: domestic, hospital, slaughterhouses and occasionally in 'grey water'. Their origin in wastewater was not clear. Strains from faeces usually belonged to serogroups I and IV. These types were also found in wastewater, as were group II and III strains. Serogroup II phages were abundant in wastewater of human origin but rare in faeces. Escherichia coli strains sensitive to infection by F-specific phages were common in faeces (overall 290/1081: 27%). No strains with fully depressed F-pilus synthesis were detected among the sensitive strains. It is concluded that the occurrence of F-specific RNA bacteriophages in water points to sewage pollution rather than faecal pollution; the mechanism of replication of these organisms in wastewater is not understood.     

Persistence of F-Specific RNA Coliphages in Surface Waters from a Produce Production Region along the Central Coast of California

F+ RNA coliphages (FRNA) are used to source-track fecal contamination and as surrogates for enteric pathogen persistence in the environment. However, the environmental persistence of FRNA is not clearly understood and necessitates the evaluation of the survival of prototype and environmental isolates of FRNA representing all four genogroups in surface waters from the central coast of California. Water temperature played a significant role in persistence–all prototype and environmental strains survived significantly longer at 10°C compared to 25°C. Similarly, the availability of host bacterium was found to be critical in FRNA survival. In the absence of E. coli F_amp, all prototypes of FRNA disappeared rapidly with a D-value (days for one log reduction) of <1.2 d from water samples incubated at 25°C; the longest surviving prototype was SP. However, in the presence of the host, the order of persistence at 25°C was QB>MS2>SP>GA and at 10°C it was QB = MS2>GA>SP. Significant differences in survival were observed between prototypes and environmental isolates of FRNA. While most environmental isolates disappeared rapidly at 25°C and in the absence of the host, members of genogroups GIII and GI persisted longer with the host compared to members of GII and GIV. Consequentially, FRNA based source tracking methods can be used to detect phages from recent fecal contamination along with those that persist longer in the environment as a result of cooler temperatures and increased host presence.     

Replication of coliphage Qβ as affected by host cell number, nutrition, competition from insusceptible cells and non-FRNA coliphages

F-specific RNA (FRNA) coliphages, which infect Escherichia coli by attachment to F pili, might serve as indicators of human enteric viruses in groundwater, provided these phages do not replicate in groundwater and replicate only to a limited extent in wastewater. Several factors that could influence phage replication in either of these environments were examined. Qβ did not replicate when host cells were fewer than 10⁴ cfu ml⁻¹. Replication selected for insusceptible cells when Qβ was incubated with its E. coli host. Loss of Qβ, presumably by inactivation, occurred in autoclaved on-site and urban wastewater, autoclaved groundwater, and in filter-sterilized spent LB broth. Replication did not occur in LB broth diluted with sterile saline to 1% of its original strength, which indicates that replication of FRNA coliphages cannot occur in such nutrient-poor environments as wastewater and groundwater. Competition from non-FRNA coliphages and insusceptible cells tended to reduce Qβ replication, as predicted, but phage yields unexpectedly increased significantly when Enterococcus faecalis was added to cultures.     

Detection of phages carrying the Shiga toxin 1 and 2 genes in waste water and river water samples

AIMS: To evaluate the occurrence and abundance of phages that carry the stx(1) and stx(2) gene in water samples of different quality. METHODS AND RESULTS: Phages growing on the Shiga toxin-negative Escherichia coli O157:H7 (ATCC 43,888) strain were enumerated by a plaque assay in concentrated raw and treated waste water samples and river water samples. Plaques were investigated for the presence of stx(1) and stx(2) genes by a multiplex/nested PCR procedure. An overall number of 805 plaques were tested for the presence of stx-carrying phages. Stx genes could be demonstrated in 2% (stx(1)) and 16% (stx(2)) of the plaques. Stx-phages were eliminated with approximately the same efficiency in comparison with somatic coliphages during the waste water treatment process. CONCLUSIONS: Due to the low numbers of phages carrying the stx genes 1 and 2 in treated waste water and river water, the dilution and inactivation of host bacteria and the unsuitable conditions for the transduction of host organisms in aquatic environments, it is difficult to derive from the data the direct evidence for a public health problem. SIGNIFICANCE AND IMPACT OF THE STUDY: The results show the quantitative occurrence of stx-carrying phages in waste and river water and confirm the frequent circulation of these viruses in the aquatic environment.     

Distribution of F-specific bacteriophages and coliphages in wastewater

A new method for quantifying F-specific bacteriophages in wastewater is described. Somatic coliphages were also determined. Host-strainSalmonella typhimurium WG 49 was sensitive to only a few bacteriophages and this could have arisen from infection by F-RNA phages. Host-strainEscherichia coli ATCC 9723 C, however, supported multiplication of a wide range of bacteriophages present in sewage, giving plaque counts one to three orders of magnitude greater than those on F⁺ and F^- salmonellas.L. Bonadonna, R. Liberti and L. Volterra are with the Istituto Superiore di Sanita, Lab. Igiene Ambientale, Viale Regina Elena 299, 00161 Rome, Italy.     

A method for the enumeration of male-specific bacteriophages in sewage

Male-specific bacteriophages adsorb to F-pili and thus can only infect male host strains. A method was developed for the selective enumeration of these phages, based on the observation that in sewage there are few phages capable of infecting F- -salmonellas--usually less than 10 pfu/ml. Using a male Salmonella strain, constructed by the introduction of the plasmid F'42 lac::Tn5 into Salmonella typhimurium phage type 3, plaque counts in secondary effluent were found to be in the range of 60-8200 pfu/ml. Practically all the phages detected had a host range restricted to male Salmonella or Escherichia coli strains, were resistant to chloroform and their infectivity was inhibited by RNase. Electron microscopy of lysates revealed phage particles that were morphologically identical to the male-specific single-strand RNA phages. Similar results were obtained with a strain of Salm. indiana carrying F'42 lac. A derivative of the Salm. typhimurium LT2 strain carrying an F-plasmid (F'42 lac fin P301) derepressed for fertility inhibition by the resident plasmid pSLT was equally sensitive to male-specific phages, but from sewage samples many other phages infecting F- E. coli but not F- Salmonella were isolated using this host strain.     

Evaluation of Escherichia coli Host Strain CB390 for Simultaneous Detection of Somatic and F-Specific Coliphages

Escherichia coli WG5, the strain recommended by the International Organization for Standardization (ISO) to detect somatic coliphages, was transformed to F⁺ by introducing the plasmid Famp, which rendered it capable of simultaneously detecting both somatic and F-specific coliphages. Indeed, this strain, CB390, proved as effective in detecting similar numbers of phages as the sum of somatic and F-specific bacteriophages detected by the host strains recommended by both the ISO and the U.S. Environmental Protection Agency standardized methods.     

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.     

Diversity of temperate bacteriophages induced in bovine and ovine Mannheimia haemolytica isolates and identification of a new P2-like phage

The diversity of temperate bacteriophages was examined in 32 Mannheimia haemolytica, six Mannheimia glucosida and four Pasteurella trehalosi isolates. Phage particles were induced and identified by electron microscopy in 24 (75%) M. haemolytica isolates, but in only one (17%) M. glucosida and one (25%) P. trehalosi isolate. The M. haemolytica phages were relatively diverse as seven Siphoviridae, 15 Myoviridae and two Podoviridae-like phages were identified; the Myoviridae-type phages also exhibited structural variation of their tails. The bacteriophages induced in M. glucosida and P. trehalosi were of the Myoviridae type. Restriction endonuclease (RE) analysis identified nine distinct RE types among the M. haemolytica bacteriophages, providing further evidence of their relative diversity. A limited number of phages caused plaques on indicator strains and the phages exhibited a narrow host range. A subgroup of 11 bovine serotype A1 and A6 isolates contained Myoviridae-type phages of the same RE type (type A), but these differed in their abilities to infect and form plaques on the same panel of indicator strains. A P2-like phage (phiPHL213.1), representative of the RE type A phages, was identified from the incomplete M. haemolytica genome sequence. The phiPHL213.1 genome contains previously unidentified genes and represents a new member of the P2 phage family.     

Isolation and selection of coliphages as potential biocontrol agents of enterohemorrhagic and Shiga toxin‐producing E. coli(EHEC and STEC) in cattle

Aims: To isolate, characterize and select phages as potential biocontrol agents of enterohemorrhagic and Shiga toxin‐producing Escherichia coli (EHEC and STEC) in cattle. Methods and Results: Sixteen STEC and EHEC coliphages were isolated from bovine minced meat and stool samples and characterized with respect to their host range against STEC, EHEC and other Gram‐negative pathogens; their morphology by electron microscopy; the presence of the stx1, stx2 and cI genes by means of PCR; RAPD and rep‐PCR profiles; plaque formation; and acid resistance. Six isolates belonged to the Myoviridae and 10 to the Podoviridae families. The phages negative for stx and cI that formed large, well‐defined plaques were all isolated using EHEC O157:H7 as host. Among them, only CA911 was a myophage and, together with CA933P, had the broadest host range for STEC and EHEC; the latter phage also infected Shigella and Pseudomonas. Isolates CA911, MFA933P and MFA45D differed in particle morphology and amplification patterns by RAPD and rep‐PCR and showed the highest acidity tolerance. Conclusions: Myophage CA911 and podophages CA933P, MFA933P and MFA45D were chosen as the best candidates for biocontrol of STEC and EHEC in cattle. Significance and Impact of the Study: This work employs steps for a rational selection and characterization of bacteriophages as therapeutic agents. This report constitutes the first documentation of STEC and EHEC phages isolated in Argentina and proposes for the first time the use of rep‐PCR as a complement of RAPD on DNA fingerprinting of phages.     

Bacteriophages and indicator bacteria in human and animal faeces

In an attempt to explain the presence of F-specific (RNA) bacteriophages in waste-water, faecal material from humans and a variety of animals was examined. The phages were detected in appreciable numbers only in faeces from pigs, broiler chickens, sheep and calves but not from dogs, cows, horses and humans. Parallel examinations for somatic coliphages, thermotolerant coliforms, faecal streptococci and spores of sulphite-reducing clostridia revealed the consistent presence of these organisms in all types of samples, albeit in variable numbers. The number of F-specific bacteriophages was related to the total number of somatic coliphages, but phage counts were unrelated to bacterial counts. F-specific RNA phages were grouped by serotyping and all animal isolates were found to belong to either group I (MS2 subtype) or IV (four different subtypes). Among the group IV isolates, most belonged to well-known subtypes SP (24 isolates) or FI (18 isolates) but five isolates were related to phage ID2 and one isolate was a new subtype. In contrast with animal isolates, 19 isolates from hospital wastewater belonged to serogroups II or III.     

Bacteriophages and indicator bacteria in human and animal faeces

In an attempt to explain the presence of F-specific (RNA) bacteriophages in waste-water, faecal material from humans and a variety of animals was examined. The phages were detected in appreciable numbers only in faeces from pigs, broiler chickens, sheep and calves but not from dogs, cows, horses and humans. Parallel examinations for somatic coliphages, thermotolerant coliforms, faecal streptococci and spores of sulphite-reducing clostridia revealed the consistent presence of these organisms in all types of samples, albeit in variable numbers. The number of F-specific bacteriophages was related to the total number of somatic coliphages, but phage counts were unrelated to bacterial counts. F-specific RNA phages were grouped by serotyping and all animal isolates were found to belong to either group I (MS2 subtype) or IV (four different subtypes). Among the group IV isolates, most belonged to well-known subtypes SP (24 isolates) or FI (18 isolates) but five isolates were related to phage ID2 and one isolate was a new subtype. In contrast with animal isolates, 19 isolates from hospital wastewater belonged to serogroups II or III.     

Isolation and characterization of two types of actinophages infecting Streptomyces scabies MR13

Two types of actinophages, phi S and phi L, were isolated from soil samples by using Streptomyces scabies MR13, a potato scab pathogen, as an indicator strain. The phages were partially characterized according to their physicochemical properties, plaques and particles morphology and their host-range. The host-range of these phages was narrow for phi S and wide for phi L. The adsorption rate constants of the phi S and phi L were 3.44 x 10(-9) and 3.18 x 10(-9) ml/min, and their burst sizes were 1.61 and 3.75 virions, respectively. One-step growth indicated that phi S and phi L have a latent period of 30 min followed by a rise period of 30 min. The temperate character of these phages was tested in other isolates of Streptomyces. Four of the phages (phi SS3, phi SS12, phi SS13 and phi SS17) were identified as temperate phages, since they were able to lysogenize SS3, SS12, SS13 and SS17. phi SS3, phi SS12 and phi SS13 were homoimmune, and they were heteroimmune with respect to phi SS17. The restriction barriers of lysogenic isolates (SS12, SS13 and SS17) interfered with the blockage of plaques formation by phages (phi SS12, phi SS13 or phi SS17) propagated on them, about 75% of lysogenic isolates had restriction systems. The exposure of the lysogenic isolates (SS12, SS13 and SS17) to UV-irradiation prevented the possible restriction barriers of these isolates, and these barriers could be overcome.