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The ability to detect human fecal pollution in water is of great importance when assessing the associated health risks. Many microbial source tracking (MST) markers have been proposed to determine the origin of fecal pollution, but their application remains challenging. A range of factors, not yet sufficiently analyzed, may affect MST markers in the environment, such as dilution and inactivation processes. In this work, a statistical framework based on Monte Carlo simulations and non-linear regression was used to develop a classification procedure for use in MST studies. The predictive model tested uses only two parameters: somatic coliphages (SOMCPH), as an index of general fecal pollution, and human host-specific bacteriophages that infect Bacteroides thetaiotaomicron strain GA17 (GA17PH). Taking into account bacteriophage dilution and differential inactivation, the threshold concentration of SOMCPH was calculated to be around 500 PFU/100 mL for a limit of detection of 10 PFU/100 mL. However, this threshold can be lowered by increasing the analyzed volume sample, which in turn lowers the limit of detection. The resulting model is sufficiently accurate for application in practical cases involving MST and could be easily used with markers other than those tested here.

Shiga toxins (Stx) of Shiga toxin-producing Escherichia coli (STEC) are generally encoded in the genome of lambdoid bacteriophages, which spend the most time of their life cycle integrated as prophages in specific sites of the bacterial chromosome. Upon spontaneous induction or induction by chemical or physical stimuli, the stx genes are co-transcribed together with the late phase genes of the prophages. After being assembled in the cytoplasm, and after host cell lysis, mature bacteriophage particles are released into the environment, together with Stx. As members of the group of lambdoid phages, Stx phages share many genetic features with the archetypical temperate phage Lambda, but are heterogeneous in their DNA sequences due to frequent recombination events. In addition to Stx phages, the genome of pathogenic STEC bacteria may contain numerous prophages, which are either cryptic or functional. These prophages may carry foreign genes, some of them related to virulence, besides those necessary for the phage life cycle. Since the production of one or more Stx is considered the major pathogenicity factor of STEC, we aim to highlight the new insights on the contribution of Stx phages and other STEC phages to pathogenicity.

Enteric bacteriophages (somatic coliphages, F-specific coliphages or both together) are now recognized as useful viral indicators in water, shellfish, and biosolids and are being progressively included in national and international sanitary regulations. Among them, somatic coliphages have an advantage in that they usually outnumber F-RNA coliphages in water environments. Their enumeration using Modified Scholten’s (MS) media, following the ISO 10705-2 standard for the growth of Escherichia coli host strain WG5, is highly efficient and a common practice worldwide. These media contain a high concentration of nutrients, which may be modified to save costs without loss of bacterial growth host efficiency. This study explored reducing the concentration of nutrients in the current formulation and/or incorporating new components to improve the host bacterial growth and/or the enumeration of somatic coliphages at an affordable analytical cost. A twofold dilution of the original MS media was found not to affect the bacterial growth rate. The addition of combinations of assayed compounds to twofold diluted MS media slightly enhanced its analytical performance without altering bacterial growth. By generating savings in both cost and time while maintaining optimal results, media dilution could be applied to design new simple applications for coliphage enumeration.

Here we introduce methods for the detection, enumeration, and isolation of bacteriophages from Escherichia coli. In bacteria, horizontal gene transfer may be mediated by virulent and temperate phages. Strict virulent phages, able to propagate in a suitable strain following the lytic pathway, can be isolated directly from different natural environments. In temperate phages, the lytic cycle must be activated, and phages are detected after their induction. In both cases, detection is based on the production of visible plaques in a confluent lawn of the host strain using a double agar layer method. Further purification and characterization are achieved by density gradients, electron microscopy studies, and genomic analysis. This straightforward methodology can be applied to the detection, enumeration, and isolation of bacteriophages from any bacterial species, using the appropriate host strain, media, and culture conditions.

Objectives Antimicrobial resistance genes (ARGs) can be transferred by means of mobile genetic elements, which play a critical role in the dissemination of resistance in the bacterial community. ARG transmission within mobile genetic elements has been reported in plasmids and transposons but less frequently in bacteriophages. Here, the bacteriophage fraction of seven human faecal samples was purified and deep-sequenced to detect the presence of ARGs in the phage particles. Methods Seven faecal samples (five from healthy individuals and two from a patient before and after receiving ciprofloxacin treatment) were used to extract phage DNA, which was purified and then sequenced in a MiSeq (Illumina). Generated reads were checked for quality and assembled, and then the generated contigs analysed with Kraken, PHASTER, VirSorter and Prokka. Some genes were also validated by quantitative PCR. Results Analysis of the purified phage DNA by Kraken identified from 4 to 266 viruses in the samples. The viral fraction corresponded mainly to the order Caudovirales, including phages from the Siphoviridae and Myoviridae families. Bacterial genes associated with antimicrobial resistance were detected in the viral DNA, as confirmed by quantitative PCR. Higher densities of ARG-carrying phage particles were observed in the post- versus pre-ciprofloxacin treatment sample. Conclusions The finding of ARGs in phage particles supports the description of phages as mobile elements contributing to the dissemination of bacterial antibiotic resistance and suggests ciprofloxacin treatment may play a role in the release of ARG-carrying particles, thereby increasing resistance.

Hemolytic uremic syndrome (HUS), principally caused by Shiga toxins (Stxs), is associated with Shiga toxin-producing Escherichia coli (STEC) infections. We previously reported Stx2 expression by host cells in vitro and in vivo. As the genes encoding the two Stx subunits are located in bacteriophage genomes, the aim of the current study was to evaluate the role of bacteriophage induction in HUS development in absence of an E. coli O157:H7 genomic background. Mice were inoculated with a non-pathogenic E. coli strain carrying the lysogenic bacteriophage 933W (C600Φ933W), and bacteriophage excision was induced by an antibiotic. The mice died 72 h after inoculation, having developed pathogenic damage typical of STEC infection. As well as renal and intestinal damage, markers of central nervous system (CNS) injury were observed, including aberrant immunolocalization of neuronal nuclei (NeuN) and increased expression of glial fibrillary acidic protein (GFAP). These results show that bacteriophage 933W without an E. coli O157:H7 background is capable of inducing the pathogenic damage associated with STEC infection. In addition, a novel mouse model was developed to evaluate therapeutic approaches focused on the bacteriophage as a new target. Fil: del Cogliano, Manuel Eugenio. Universidad Nacional de Quilmes; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina Fil: Vasconcelos Esteves Pinto, Alipio. Consejo Nacional de Investigaciones Científicas y Técnicas. Oficina de Coordinación Administrativa Houssay. Instituto de Fisiología y Biofísica Bernardo Houssay. Universidad de Buenos Aires. Facultad de Medicina. Instituto de Fisiología y Biofísica Bernardo Houssay; Argentina Fil: Goldstein Raij, Jorge. Consejo Nacional de Investigaciones Científicas y Técnicas. Oficina de Coordinación Administrativa Houssay. Instituto de Fisiología y Biofísica Bernardo Houssay. Universidad de Buenos Aires. Facultad de Medicina. Instituto de Fisiología y Biofísica Bernardo Houssay; Argentina Fil: Zotta, Elsa. Consejo Nacional de Investigaciones Científicas y Técnicas. Oficina de Coordinación Administrativa Houssay. Instituto de Fisiología y Biofísica Bernardo Houssay. Universidad de Buenos Aires. Facultad de Medicina. Instituto de Fisiología y Biofísica Bernardo Houssay; Argentina Fil: Ochoa, Federico Claudio. Consejo Nacional de Investigaciones Científicas y Técnicas. Oficina de Coordinación Administrativa Houssay. Instituto de Fisiología y Biofísica Bernardo Houssay. Universidad de Buenos Aires. Facultad de Medicina. Instituto de Fisiología y Biofísica Bernardo Houssay; Argentina Fil: Fernández Brando, Romina Jimena. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Medicina Experimental. Academia Nacional de Medicina de Buenos Aires. Instituto de Medicina Experimental; Argentina Fil: Muniesa, Maite. Academia Nacional de Medicina de Buenos Aires; Argentina Fil: Ghiringhelli, Pablo Daniel. Universidad Nacional de Quilmes; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina Fil: Palermo, Marina Sandra. Consejo Nacional de Investigaciones Científicas y Técnicas. Instituto de Medicina Experimental. Academia Nacional de Medicina de Buenos Aires. Instituto de Medicina Experimental; Argentina Fil: Bentancor, Leticia Verónica. Universidad Nacional de Quilmes; Argentina. Consejo Nacional de Investigaciones Científicas y Técnicas; Argentina

The emergence and prevalence of antibiotic resistance genes (ARGs) in the environment is a serious global health concern. ARGs from bacteria can be mobilized by mobile genetic elements, and recent studies indicate that phages and phage-derived particles, among others, could play a role in the spread of ARGs through the environment. ARGs are abundant in the bacterial and bacteriophage fractions of water bodies and for successful transfer of the ARGs, their persistence in these environments is crucial. In this study, three ARGs (blaTEM, blaCTX-M and sul1) that naturally occur in the bacterial and phage fractions of raw wastewater were used to evaluate the persistence of ARGs at different temperatures (4 °C, 22 °C and 37 °C) and pH values (3, 7 and 9), as well as after various disinfection treatments (thermal treatment, chlorination and UV) and natural inactivation in a mesocosm. Gene copies (GC) were quantified by qPCR; then the logarithmic reduction and significance of the differences between their numbers were evaluated. The ARGs persisted for a long time with minimal reductions after all the treatments. In general, they showed greater persistence in the bacteriophage fraction than in the bacterial fraction. Comparisons showed that the ARGs persisted under conditions that reduced culturable Escherichia coli and infectious coliphages below the limit of detection. The prevalence of ARGs, particularly in the bacteriophage fraction, poses the threat of the spread of ARGs and their incorporation into a new bacterial background that could lead to the emergence of new resistant clones.

F-specific coliphages have been proposed as viral indicators of fecal pollution. These intestinal phages infect cells through the F-pili of the host strains used for their detection, Escherichia coli HS/FAmp in the US-EPA standard method and Salmonella enterica WG49 in the ISO method. The recently designed Bluephage protocol allows the rapid detection of as low as one somatic coliphage in a working day. The current study describes a new Bluephage method designed to exclusively detect F-specific phages. It employs two new host strains, CB14 and CB16, which detect the same number of F-specific phages as their respective parental strains HS and WG49. In the Bluephage method, when the strain is lysed by bacteriophage infection, the yellow medium turns blue. As low as one F-specific phage was detected in 3 to 5 hours by this approach and when the sample contained high phage concentrations, results were obtained in less than 3 hours. The F-specific Bluephage method can be used with different sample volumes and allows phage quantification by the most probable number technique. Strain CB14 performed more consistently than CB16, with comparable detection efficiency after increasing the incubation time to 50 minutes without shaking.

Phage particles have emerged as elements with the potential to mobilise antibiotic resistance genes (ARGs) in different environments, including the intestinal habitat. This study aimed to determine the occurrence of ARGs in phage particles present in faecal matter and induced from strains isolated from faeces. Nine ARGs (bla(TEM), bla(CTX-M-1 group), bla(CTX-M-9 group), bla(OXA-48), qnrA, qnrS, mecA, sul1 and armA) were quantified by qPCR in the phage DNA fractions of 150 faecal samples obtained from healthy individuals who had not received antibiotic treatment or travelled abroad in the 3 months prior to sample collection. On the suspicion that the detected particles originated from bacterial flora, 82 Escherichia coli and Klebsiella pneumoniae isolates possessing at least one identified ARG (bla(TEM), bla(CTX-M-1 group), bla(CTX-M-9 group), armA, qnrA, qnrS and sul1) were isolated and their capacity to produce phage particles carrying these ARGs following induction was evaluated. Of 150 samples, 72.7% were positive for at least one ARG, with bla(TEM) and bla(CTX-M-9 group) being the most prevalent and abundant. Of the 82 isolates, 51 (62%) showed an increase in the number of copies of the respective ARG in the phage fraction following induction, with bla(TEM), bla(CTX-M-1 group), bla(CTX-M-9 group) and sul1 being the most abundant. Phages induced from the isolates were further purified and visualised using microscopy and their DNA showed ARG levels of up to 1010 gene copies/mL. This study highlights the abundance of phage particles harbouring ARGs and indicates that bacterial strains in the intestinal habitat could be source of these particles. (C) 2017 Elsevier B.V. and International Society of Chemotherapy. All rights reserved.

The emergence and increased prevalence of antibiotic resistance genes (ARGs) in the environment may pose a serious global health concern. This study evaluates the abundance of several ARGs in bacterial and bacteriophage DNA via real-time qPCR in samples from five different sampling points in Tunisia; three wastewater treatment plants (WWTP 1, 2 and 3) and wastewater from two abattoirs slaughtering different animals. Results are compared with those obtained in the Barcelona area, in northeast Spain.Eight ARGs were quantified by qPCR from total and phage DNA fraction from the samples. Three β-lactamases (blaTEM, blaCTX-M cluster 1 and blaCTX-M cluster 9), two quinolone resistance genes (qnrA and qnrS), the mecA gene that confers resistance to methicillin in Staphylococcus aureus, the emerging armA gene, conferring resistance to aminoglycosides and sul1, the most extended gene conferring resistance to sulfonamides, were evaluated.Sul1 and blaTEM were the most prevalent ARGs detected at all five Tunisian sampling points, similarly with the observations in Barcelona. blaCTX-M-9 was more prevalent than blaCTX-M-1 both in bacterial and DNA within phage particles in all samples analysed. mecA and armA were almost absent in Tunisian waters from human or animal origin in contrast with Barcelona that showed a medium prevalence. qnrA was more prevalent than qnrS in bacterial and phage DNA from all sampling points.In conclusion, our study shows that ARGs are found in the bacterial and is reflected in the phage DNA fraction of human and animal wastewaters. The densities of each ARGs vary depending on the ARGs shed by each population and is determined by the characteristics of each area. Thus, the evaluation of ARGs in wastewaters seems to be suitable as marker reflecting the antibiotic resistance patterns of a population. Keywords: Bacteriophages, Antibiotic resistance, β-lactamases, Quinolones, Sul1, Sewage water

Here we describe the detection, enumeration, and isolation of bacteriophages infecting Bacteroides. The method is based on the infection of Bacteroides host strains and the production of visible plaques in a confluent lawn of the host strain using the double-layer agar method. This is a straightforward methodology that can be applied for the detection, enumeration and isolation of bacteriophages for other anaerobic bacteria, using an appropriate host strain and culture conditions. In the case of bacteriophages of Bacteroides the results can be obtained in less than 24 h, although the time could vary depending on the growth rate of the host strain.

Cytolethal distending toxin (Cdt) is produced by a variety of pathogenic bacteria, including pathogenic serotypes of Shiga toxin-producing Escherichia coli (STEC). The Cdt family comprises five variants (Cdt-I to Cdt-V) encoded by three genes located within the chromosome or plasmids or, in the case of Cdt-I, within bacteriophages. In this study, we evaluated the occurrence of the cdt gene in a collection of 140 environmental STEC isolates. cdt was detected in 12.1% of strains, of which five strains carried inducible bacteriophages containing the Cdt-V variant. Two Cdt-V phages of the Siphoviridae morphology lysogenized Shigella sonnei , generating two lysogens: a single Cdt phage lysogen and a double lysogen, containing a Cdt phage and an Stx phage, both from the wild-type strain. The rates of induction of Cdt phages were evaluated by quantitative PCR, and spontaneous induction of Cdt-V phage was observed, whereas induction of Stx phage in the double lysogen was mitomycin C dependent. The Cdt distending effect was observed in HeLa cells inoculated with the supernatant of the Cdt-V phage lysogen. A ClaI fragment containing the cdt-V gene of one phage was cloned, and sequencing confirmed the presence of Cdt-V, as well as a fragment downstream from the cdt homolog to gpA , encoding a replication protein of bacteriophage P2. Evaluation of Cdt-V phages in nonclinical water samples showed densities of 10 2 to 10 9 gene copies in 100 ml, suggesting the high prevalence of Cdt phages in nonclinical environments.

Microbial source tracking (MST) methods allow the identification of specific faecal sources. The aim is to detect the sources of faecal pollution in a water body to allow targeted, efficient and cost-effective remediation efforts in the catchment. Bacteriophages infecting selected host strains of Bacteroides species are used as markers to track faecal contaminants in water. By using a suitable Bacteroides host from a given faecal origin, it is possible to specifically detect bacteriophages of this faecal origin. It can thus be used to detect specific phages of Bacteroides for MST. With this objective, we isolated several Bacteroides strains from pig, cow and poultry faeces by applying a previously optimized methodology used to isolate the host strains from humans. The isolated strains belonged to Bacteroides fragilis and Bacteroides thetaiotaomicron. These strains, like most Bacteroides species, detected phages of the Siphoviridae morphology. Using the newly isolated host strains for phage enumeration in a range of samples, we showed that these detect phages in faecal sources that coincide with their own origin (70-100% of the samples), and show no detection or very low percentages of detection of phages from other animal origins (from 0 to 20% of the samples). Only strains isolated from pig wastewater detected phages in 50% of human sewage samples. Nevertheless, those strains detecting phages from faecal origins other than their own detected fewer phages (2-3 log₁₀ pfu·100 ml⁻¹) than the phages detected by the specific strain of the same origin. On the basis of our results, we propose that faecal source tracking with phages infecting specific Bacteroides host strains is a useful method for MST. In addition, the method presented here is feasible in laboratories equipped with only basic microbiological equipment, it is more rapid and cost-effective than other procedures and it does not require highly qualified staff.

Shiga toxin-converting bacteriophages (Stx phages) are involved in the pathogenicity of some enteric bacteria, such as Escherichia coli O157:H7. Stx phages are released from their bacterial hosts after lytic induction and remain free in the environment. Samples were analyzed for the presence of free Stx phages by an experimental approach based on the use of real-time quantitative PCR (qPCR), which enables stx to be detected in the DNA from the viral fraction of each sample. A total of 150 samples, including urban raw sewage samples, wastewater samples with fecal contamination from cattle, pigs, and poultry, and fecal samples from humans and diverse animals, were used in this study. Stx phages were detected in 70.0% of urban sewage samples (10 to 10 3 gene copies [GC] per ml) and in 94.0% of animal wastewater samples of several origins (10 to 10 10 GC per ml). Eighty-nine percent of cattle fecal samples were positive for Stx phages (10 to 10 5 GC per g of sample), as were 31.8% of other fecal samples of various origins (10 to 10 4 GC per g of sample). The stx 2 genes and stx 2 variants were detected in the viral fraction of some of the samples after sequencing of stx 2 fragments amplified by conventional PCR. The occurrence and abundance of Stx phages in the extraintestinal environment confirm the role of Stx phages as a reservoir of stx in the environment.

The four subgroups of F-specific RNA bacteriophages (I–IV) have been proposed as potential tracers for faecal source tracking. Groups II and III predominate in human sources while groups I and IV are most abundant in animal sources. The four subgroups of naturally occurring F-specific RNA bacteriophages were identified in different samples by plaque hybridization with genotype-specific probes and the persistence of each subgroup was evaluated. The proportions of the F-specific RNA bacteriophage subgroups were measured in wastewaters, after inactivation in surface waters or after wastewater treatment and in mixtures of wastewater of human and animal origin. Our results indicate that phage groups differ in their persistence in the environment and to different disinfecting treatments. The greater survival of subgroups I and II in treated samples hinders the interpretation of results obtained with F-specific RNA bacteriophages. The phages of subgroups III and IV were the least resistant to all treatments. These results should be considered when using genotypes of F-specific RNA as sole tracers for faecal source tracking.

Shiga toxin 2 ( stx 2 ) gene-carrying bacteriophages have been shown to convert Escherichia coli strains to Shiga toxin-producing Escherichia coli (STEC). In this study, 79 E. coli strains belonging to 35 serotypes isolated from wastewaters of both human and animal origin were examined for the presence of stx 2 -carrying bacteriophages in their genomes. The lytic cycle of the bacteriophages was induced by mitomycin, and the bacteriophage fraction was isolated and used for morphological and genetic characterization. The induced bacteriophages showed morphological diversity, as well as restriction fragment length polymorphism variation, in the different strains belonging to different serotypes. The ability to infect new hosts was highly variable, although most of the induced phages infected Shigella sonnei host strain 866. In summary, in spite of carrying either the same or different stx 2 variants and in spite of the fact that they were isolated from strains belonging to the same or different serotypes, the induced bacteriophages were highly variable. The high level of diversity and the great infectious capacity of these phages could enhance the spread of the stx 2 gene and variants of this gene among different bacterial populations in environments to which humans may be exposed.

Shiga toxin-producing Escherichia coli (STEC) is an emergent pathogen characterized by the expression of Shiga toxins, which are encoded in the genomes of lambdoid phages. These phages are infectious for other members of the Enterobacteriaceae and establish lysogeny when they integrate into the host chromosome. Five insertion sites, used mainly by these prophages, have been described to date. In the present study, the insertion of stx 2 prophages in these sites was analyzed in 168 STEC strains isolated from cattle. Additionally, insertion sites were determined for stx 2 phages which (i) converted diverse laboratory host strains, (ii) coexisted with another stx 2 prophage, and (iii) infected a recombinant host strain lacking the most commonly used insertion site. Results show that depending on the host strain, phages preferentially use one insertion site. For the most part, yehV is occupied in STEC strains while wrbA is preferentially selected by the same stx phages in E. coli laboratory strains. If this primary insertion site is unavailable, then a secondary insertion site is selected. It can be concluded that insertion site occupancy by stx phages depends on the host strain and on the availability of the preferred locus in the host strain.

Enterohemorrhagic Escherichia coli (EHEC) (O157 and other serotypes) are zoonotic pathogens linked with severe human illnesses. The main virulence factors of EHEC are the Shiga toxins, among others. Most of the genes coding for these toxins are bacteriophage-encoded. Although ruminants are recognized as their main natural reservoir, water has also been documented as a way of transmission of EHEC. E. coli O157:H7 and other EHEC may contaminate waters (recreational, drinking or irrigation waters) through feces from humans and other animals. Indeed, the occurrence of EHEC carrying the stx2 gene in raw municipal sewage and animal wastewater from several origins has been widely documented. However, the evaluation of the persistence of naturally occurring EHEC in the environment is still difficult due to methodological problems. Methods proposed for the detection and isolation of stx-encoding bacteria, ranging from the classic culture-based methods to molecular approaches, and their application in the environment, are discussed here. Most virulence factors associated with these strains are linked to either plasmids or phages, and consequently they are likely to be subject to horizontal gene transfer between species or serotypes. Moreover, the presence of infectious stx-phages isolated as free particles in the environment and their high persistence in water systems suggest that they may contribute to the spread of stx genes, as they are directly involved in the emergence of new pathogenic strains, which might have important health consequences.

Shiga toxin-converting bacteriophages are the main vehicle involved in horizontal transmission of stx1 and stx2 genes, which has led to the current spread of stx genes among a high number of Escherichia coli serotypes and other enterobacteria. Several stx gene variants have been described, although some of the variants have never been isolated from inducible bacteriophages. In this study, two stx2g-carrying bacteriophages induced from two different E. coli O2:H25 strains isolated from different wastewater samples were characterized. These bacteriophages when transduced into Shigella sonnei retained their ability to produce Stx2 protein. They had similar but not identical DNA restriction patterns, and similar host ranges. Electron microscopy studies showed that they had isometric capsids with short tails, which resembled phage 933W. However, DNA cross-hybridization studies showed that phage 933W was not closely related to stx2g bacteriophages. This first description of stx2g-carrying bacteriophages enlarges the list of stx-carrying bacteriophages involved in horizontal transmission of stx genes in the environment.

Enrichment cultures are widely used for the isolation of bacteria in clinical, biotechnological, and environmental studies. However, competition, relative growth rates, or inhibitory effects may alter the outcome of enrichment cultures, causing the phenomenon known as enrichment bias. Bacteriophages are a major component in many microbial systems, and it abounds in natural settings. This abundance means that bacteriophages are likely to be present in many laboratory enrichment cultures. Our hypothesis was that bacteriophages present in the sample might bias the enriched subpopulation, since it can infect and lyse the target bacteria during the enrichment step once the bacteria reach a given density. Here we show that the presence of bacteriophages inSalmonellaandShigellaenrichment cultures produced a significant reduction (more than 1 log unit) in the number of these bacteria compared with samples in which bacteriophages had been reduced by filtration through 0.45-μm non-protein-binding membranes. Furthermore, our data indicate that theSalmonellabiotypes isolated after the enrichment culture change if bacteriophages are present, thus distorting the results of the analysis.

Aims: To assess the usefulness of bacterial and viral indicators in chlorination processes and to collect quantitative information necessary for risk assessment analysis in water disinfection processes based on chlorination. Methods and Results: Naturally occurring bacterial indicators, bacteriophages and enteroviruses were determined to evaluate the effect of chlorination in groundwater and secondary sewage effluents. Additionally, the effect of chlorinating on selected bacteriophages, enteroviruses and Escherichia coli was also tested in spiked samples of bottled water and sewage effluents. Results indicate that chlorination inactivates more efficiently bacteria than phages and enteroviruses. Among the human viruses, phages infecting Bacteroides fragilis and selected somatic coliphages belonging to the Siphoviridae family were the most persistent to chlorination. Conclusions: The three groups of bacteriophages studied were all more resistant to chlorination than bacteria and some of the phages were more resistant than enteroviruses. Results presented here indicate that it is very risky to generalize from information obtained with inactivation experiments done with single isolates of any phage or virus. If possible, inactivation studies should be done with naturally occurring populations. Phages offer a good opportunity for studying naturally occurring populations. Thus, the bacteriophages offer a range of resistance to chlorination that may represent most of the viruses that can be found in water. Significance and Impact of the Study: Data reported in this study support the inclusion of bacteriophages as additional indicators of the efficiency of water chlorination processes and water quality.

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.

The emergence and prevalence of antibiotic resistance genes (ARGs) in the environment is a serious global health concern. ARGs found in bacteria can become mobilized in bacteriophage particles in the environment. Sludge derived from secondary treatment in wastewater treatment plants (WWTPs) constitutes a concentrated pool of bacteria and phages that are removed during the treatment process. This study evaluates the prevalence of ARGs in the bacterial and phage fractions of anaerobic digested sludge; five ARGs (blaTEM, blaCTX-M, qnrA, qnrS, and sul1) are quantified by qPCR. Comparison between the wastewater and sludge revealed a shift in the prevalence of ARGs (blaTEM and sul1 became more prevalent in sludge), suggesting there is a change in the bacterial and phage populations from wastewater to those selected during the secondary treatment and the later anaerobic mesophilic digestion of the sludge. ARGs densities were higher in the bacterial than in the phage fraction, with high densities in both fractions; particularly for blaTEM and sul1 (5 and 8 log10 gene copies (GC)/g, respectively, in bacterial DNA; 5.5 and 4.4 log10 GC/g, respectively, in phage DNA). These results question the potential agricultural uses of treated sludge, as it could contribute to the spread of ARGs in the environment and have an impact on the bacterial communities of the receiving ecosystem.

Shiga toxin-converting bacteriophages are involved in the pathogenicity of some enteric bacteria, such as Escherichia coli O157:H7. Recent studies have demonstrated a relatively high presence of Shiga toxin 2 phages in sewage from Spain, but no data on sewage from other areas were available. In order to evaluate the presence of such phages in sewage from diverse geographical origins, 33 sewage samples, including samples from eight different European countries as well as from New Zealand and South Africa were analysed. Using an experimental approach based on the detection of Stx 2 gene by a phage enrichment culture followed by PCR, bacteriophages infecting E. coli O157:H7 carrying the Shiga toxin 2 gene were detected in 15 of the samples studied. Results presented here show that the presence of phages carrying the Stx 2 gene is common in sewage from developed countries.

The behavior outside the gut of seeded Escherichia coli O157:H7, naturally occurring E. coli , somatic coliphages, bacteriophages infecting O157:H7, and Shiga toxin 2 (Stx2)-encoding bacteriophages was studied to determine whether the last persist in the environment more successfully than their host bacteria. The ratios between the numbers of E. coli and those of the different bacteriophages were clearly lower in river water than in sewage of the area, whereas the ratios between the numbers of the different phages were similar. In addition, the numbers of bacteria decreased between 2 and 3 log units in in situ survival experiments performed in river water, whereas the numbers of phages decreased between 1 and 2 log units. Chlorination and pasteurization treatments that reduced by approximately 4 log units the numbers of bacteria reduced by less than 1 log unit the numbers of bacteriophages. Thus, it can be concluded that Stx2-encoding phages persist longer than their host bacteria in the water environment and are more resistant than their host bacteria to chlorination and heat treatment.

The aim of the present work was to observe the morphological differences between bacteriophages from sewage, recent pollution and those from samples that contain microorganisms that have survived either natural inactivation or water treatment processes (persistent pollution). We studied the occurrence of bacteriophages infecting Bacteroides fragilis (HSP40 strain), F-specific coliphages (HS(pFamp)R strain) and somatic coliphages (CN13 strain). Phages isolated with B. fragilis in both wastewater and samples with persistent pollution were in all cases members of the Siphoviridae group with flexible tails. With E. coli strain HS(pFamp)R we detected F-specific coliphages in 97.7% wastewater. However, the percentage decreased to 76.9% in samples with persistent pollution. In the case of somatic coliphages in wastewater, detected using E. coli CN13, 91% of the phages belonged to the Myoviridae family and a 6% to the Siphoviridae family. In contrast, in persistent pollution samples, an increase of Siphoviridae phages was observed (up to 26.4%).

A group of antibiotic resistance genes (ARGs) ( bla TEM , bla CTX-M-1 , mecA , armA , qnrA , and qnrS ) were analyzed by real-time quantitative PCR (qPCR) in bacteriophage DNA isolated from feces from 80 healthy humans. Seventy-seven percent of the samples were positive in phage DNA for one or more ARGs. bla TEM , qnrA , and, bla CTX-M-1 were the most abundant, and armA , qnrS , and mecA were less prevalent. Free bacteriophages carrying ARGs may contribute to the mobilization of ARGs in intra- and extraintestinal environments.

A membrane of inorganic material with a honeycomb pore structure was used to concentrate phages infecting Bacteroides fragilis from drinking water. Phages were removed from the membrane with 0.25 M glycine buffer pH 9.5. Phages were not inactivated by storage in this buffer neutralized to pH 7.0 for at least 9 days at 4 degrees C. The method allows recovery of around 50% in drinking water. When the turbidity of the water increased, the efficiency of the concentration decreased markedly. The efficiency of concentration was evaluated versus a presence/absence test in 317 water samples with turbidity level below the threshold of drinking water. Results obtained by concentration of 11 provided data which were significantly more informative than the presence/absence tests carried out on 100 ml. A number of additional tests carried out with both somatic and F-specific coliphages indicated that these conclusions can be extended to these groups of bacteriophages.

Stx bacteriophages in 68 samples of beef and salad were quantified by real-time quantitative PCR (qPCR). Stx phages from the samples were propagated in Escherichia coli C600, E. coli O157:H7, and Shigella strains and further quantified. Fifty percent of the samples carried infectious Stx phages that were isolated from plaques generated by lysis.

Aims: To evaluate a qPCR-based protocol for the enumeration of Shiga toxin (Stx) 2 phages and to compare the results of qPCR with the number of infective Stx phage particles. Methods and Results: An approach based on qPCR was applied to count Stx phages in five phage lysates of known titre. The number of viral particles from each phage lysate was determined by electron microscopy using latex spheres. The infectivity of the Stx phages was evaluated onto three bacterial host strains, by double agar layer assay and plaque blot hybridization. The number of phage particles detected by electron microscopy correlates with the number calculated by qPCR in all the phages assayed. The number of infectious phages was from 1 to 3 log10 units below the numbers obtained by qPCR and electron microscopy. Conclusions: The approach allows accurate quantification of Stx phages with a high recovery. The number of infectious phages is always below the number of phage particles detected by qPCR. Significance and Impact of the Study: The qPCR method is a good approach to enumerate Stx phages. However, these results should be carefully considered when related to the number of infectious phages for each lysate that could be applied in real samples, because values of infectious particles are always below the number of Stx phages detected by qPCR.

Shiga toxin ( stx ) transduction in various food matrices has been evaluated with lysogens of Stx phages. stx transduction events were observed for many phages under appropriate conditions. Transduction did not occur at low pH and low temperatures. A total of 10 3 to 10 4 CFU ml −1 was the minimal amount of donor and recipient strains necessary to generate transductants.

Background The Red recombinase system of bacteriophage lambda has been used to inactivate chromosomal genes in E. coli K-12 through homologous recombination using linear PCR products. The aim of this study was to induce mutations in the genome of some temperate Shiga toxin encoding bacteriophages. When phage genes are in the prophage state, they behave like chromosomal genes. This enables marker genes, such as antibiotic resistance genes, to be incorporated into the stx gene. Once the phages' lytic cycle is activated, recombinant Shiga toxin converting phages are produced. These phages can transfer the marker genes to the bacteria that they infect and convert. As the Red system's effectiveness decreased when used for our purposes, we had to introduce significant variations to the original method. These modifications included: confirming the stability of the target stx gene increasing the number of cells to be transformed and using a three-step PCR method to produce the amplimer containing the antibiotic resistance gene. Results Seven phages carrying two different antibiotic resistance genes were derived from phages that are directly involved in the pathogenesis of Shiga toxin-producing strains, using this modified protocol. Conclusion This approach facilitates exploration of the transduction processes and is a valuable tool for studying phage-mediated horizontal gene transfer.

International audience; Bacteriophages infecting Bacteroides are potentially a good tool for fecal source tracking, but different Bacteroides host strains are needed for different geographic areas. A feasible method for isolating Bacteroides host strains for phages present in human fecal material is described. Useful strains were identified for application in Spain and the United Kingdom. One strain, GA-17, identified as Bacteroides thetaiotaomicron, was tested in several locations in Europe with excellent performance in Southern Europe.Microbial source tracking methods are designed to enable researchers to uncover the sources of fecal pollution in a water body (19). Bacteriophages infecting Bacteroides are potential tools for microbial source tracking (4, 13, 22, 24, 26, 29). However, it is well documented that Bacteroides host strains vary in their ability to discriminate between phages of different sources but also that phage detection by a given host strain varies geographically. Thus, Bacteroides fragilis strain HSP40 detects good numbers of phages in different areas of the Mediterranean region (4, 9, 10, 28, 29, 30) and in South Africa (12), but it fails to detect significant numbers of phages in Northern Europe (22) and the United States (15). In contrast, other strains, such as RYC 2056, detect similar numbers of phages in different geographical areas but do not discriminate between the sources of fecal pollution (5, 7, 18, 22). Strains tested in the United States to date appear to behave like RYC 2056 (15).Limitations of existing source tracking methods (19, 24, 25, 26, 27), combined with the good source tracking performance of strain HSP40 in certain geographical areas (4, 9, 12, 28, 30), along with increasing information about the specificity between the animal host and the bacteria of the Bacteroides group (11, 32) and the narrow host ranges reported for phages infecting Bacteroides (6, 8, 16, 22, 30), prompted our search for new Bacteroides host strains.We describe here a rapid method for isolating and further testing Bacteroides host strains potentially useful for source tracking.

The presence of bacteriophages encoding Shiga toxin 2 (stx 2 phages) was analysed in 168 strains of Shiga-toxin-producing Escherichia coli (STEC) isolated from cattle. Following mitomycin C induction, strains carrying stx 2 phages were screened by plaque blot and hybridization with an stx 2 A-probe. In the stx 2-phage-carrying strains, the amounts of phage production, phage DNA extracted and Stx2 produced after induction were assessed. The induced stx 2 phages were characterized morphologically and genetically. Assays to obtain lysogens from different strains were also carried out and phages induced from the lysogens were compared with those induced from the STEC isolates. Results indicated that 18 % of the strains carried an inducible stx 2 phage. Most of them showed a direct relationship between phage induction and toxin production. Each strain carried only one inducible stx 2 phage, although a few strains had two copies of the stx 2 in the chromosome. The stx 2 phages showed diverse morphology and a wide variability in their genome. Assays to obtain lysogens showed that not all the phages were transduced with the same frequency and only six lysogens were obtained. Phages in the lysogens were the same as those induced from their respective initial STEC host strains, although the induction and relative toxin production of the lysogens varied. Most phages carried the stx 2 gene, while a few carried stx 2 variants. Infectivity of the phages depended on the different hosts, although O157 : H7 was preferentially infected by phages induced from O157 strains. The results show that inducible stx 2 phages are common among STEC of animal origin and that they may enhance the spread of stx 2.

Bacteriophages infecting Bacteroides fragilis strains RYC2056 and HSP40 have been proposed as indicators of water quality. To accomplish this function, homogeneity of the group of phages detected by these strains is necessary to ensure that the final results are not due to the different kinetics of inactivation of the phages. To evaluate homogeneity, we observed by electron microscopy bacteriophages isolated from sewage with two Bacteroides fragilis strains (HSP40 and RYC2056). A predominant group of phages was observed, Siphoviridae with slightly curved tails. Detection of other minority groups, which could be present in the sample, was done with neutralization experiments by using antiserum against the majority group and with host mutants resistant to infection with the predominant phage. Although two other minority groups were observed, results showed that bacteriophages infecting B. fragilis strain HSP40 and strain RYC2056 form a homogeneous group, Siphoviridae with slightly curved tails being the most predominant in sewage.

During the European project 'Bacteriophages in bathing waters' (January 1996-June 1999), research was carried out to optimise the method for detection and enumeration of F-specific (RNA) phages in water. It was evaluated whether further optimisation would be possible/needed for the procedure as described in the standard method of the International Organisation for Standardisation (ISO) 10705-1. The research focused mainly on optimisation of the different steps for culturing the host strain WG49 Salmonella Typhimurium. It was concluded that all steps described in ISO 10705-1 are necessary and, if followed carefully, using a culture of host strain WG49 Salmonella Typhimurium of good quality, reliable results could be obtained for the enumeration of F-specific RNA phages.

A method for the detection and enumeration of bacteriophages infecting Bacteroides fragilis has been standardised. The recommended host strain is RYC2056 (ATCC 700786) because of the relatively high counts (10(4)-10(5) PFU/100ml) that it recovers in sewage from very different geographical areas. The addition of 0.25% bile to the culture and assay media and the manipulation of the host strain under strict anaerobic conditions resulted in a significant increase (more than 100%) in the number of phages detected. No other changes in the media and culture conditions resulted in changes in the phage counts detected. However, these increases do not justify changing the culture conditions and media described, taking into consideration that bile renders the media cloudy making it difficult to follow the host growth and that most laboratories do not have the facilities to work under strict anaerobic conditions. Nalidixic acid (100 microg/ml) and kanamycin (100 microg/ml) in the assay medium significantly reduce the background flora from polluted samples without affecting the phage counts. Freezing cultures just before the end of the log-phage growth at (-70+/-10) degrees C with BSA-sucrose as cryoprotector, storing of 1-2 ml in glass vials at (-70+/-10) degrees C and using them directly to inoculate fresh broth allows the obtention of cultures ready for phage enumeration in about 2.5 h. All these developments have been incorporated into a procedure that makes the method for detecting phages infecting B. fragilis as workable as the standardised methods available for the detection of coliphages.

Shiga toxin (Stx)-producing Escherichia coli (STEC) strains are a worldwide cause of diarrhea, hemorrhagic colitis, and the hemolytic-uremic syndrome (HUS) (8). Stx identified in human STEC isolates comprise Stx1, Stx2 and variants of Stx2, including Stx2c, Stx2d, and Stx2e (21, 31, 35). STEC strains associated with diarrhea and HUS usually produce Stx1, Stx2, and Stx2c, either alone or in various combinations (6, 24). In contrast, Stx2d was frequently identified in STEC isolates from asymptomatic carriers (21). Stx2e is typically produced by STEC strains that cause pig edema disease and belong to serogroups O138, O139, and O141 (15). However, Stx2e-producing STEC strains have also been isolated, albeit rarely, from patients with diarrhea (20) and HUS (35). These human isolates belonged to serogroups O101 and O9 that have not been reported in STEC strains associated with pig edema disease. Interestingly, Stx2e-producing STEC belonging to serogroup O101 have been isolated from slaughtered healthy pigs (2), suggesting this animal species as a potential reservoir of human infections. Several stx2e genes have been cloned and sequenced from STEC O101 isolates originating from a patient with diarrhea and from healthy pigs, respectively (4), and were demonstrated to be identical or almost identical to stx2e present in an STEC O139 isolate from a pig with edema disease (36). Stx1 and Stx2 are encoded in the genome of temperate bacteriophages (11, 32, 33). Phages that contain the structural genes for Stx1 and Stx2 have been isolated from STEC O157 and O26 strains, and their morphology, genome sizes, and restriction fragment length polymorphism patterns have been characterized (23, 32, 38). Moreover, the Stx1-converting phage H-19B isolated from STEC O26:H11 strain H19 and the Stx2-converting phage 933W originating from STEC O157:H7 strain EDL 933 (19) have been characterized by nucleotide sequencing and shown to have a genetic structure related to that of bacteriophage λ (18, 22). Analysis of a 17-kb region of the genome of phage H-19B demonstrated that the stx1 gene was located downstream of a gene encoding an analogue of the transcription activator Q of lambdoid phages and upstream of the analogues of λ genes encoding lysis functions (18). Phage 933W and phage VT2-Sakai had a related structure in this region (14, 22). Functional studies in phage H-19B suggested a role for the Q protein and the lysis genes in the release of toxin from the bacterial cell (18). In contrast to stx1 and stx2, the stx2e genes in STEC strains associated with pig edema disease have been reported to be located in the chromosome because no Stx-converting phages could be isolated from such strains (15, 37). No data have been provided in the literature on the location of stx2e genes in sporadic Stx2e-producing STEC isolates of human origin described until now (20, 35). The lack of information on the localization of the stx2e gene prompted us to investigate the presence of Stx2e-converting bacteriophages in stx2e-harboring E. coli strains isolated from patients in our laboratory. We were able to isolate and characterize such a phage from the human STEC isolate 2771/97.

Environments without any contact with anthropogenic antibiotics show a great abundance of antibiotic resistance genes that use to be chromosomal and are part of the core genes of the species that harbor them. Some of these genes are shared with human pathogens where they appear in mobile genetic elements. Diversity of antibiotic resistance genes in non-contaminated environments is much greater than in human and animal pathogens, and in environments contaminated with antibiotic from anthropogenic activities. This suggests the existence of some bottleneck effect for the mobilization of antibiotic resistance genes among different biomes. Bacteriophages have characteristics that make them suitable vectors between different biomes, and as well for transferring genes from biome to biome. Recent metagenomic studies and detection of bacterial genes by genomic techniques in the bacteriophage fraction of different microbiota provide indirect evidences that the mobilization of genes mediated by phages, including antibiotic resistance genes, is far more relevant than previously thought. Our hypothesis is that bacteriophages might be of critical importance for evading one of the bottlenecks, the lack of ecological connectivity that modulates the pass of antibiotic resistance genes from natural environments such as waters and soils, to animal and human microbiomes. This commentary concentrates on the potential importance of bacteriophages in transferring resistance genes from the environment to human and animal body microbiomes, but there is no doubt that transduction occurs also in body microbiomes.

Shiga toxin-converting bacteriophages are involved in the pathogenicity of some enteric bacteria, such asEscherichia coliO157:H7, but data on the occurrence and distribution of such phages as free particles in nature were not available. An experimental approach has been developed to detect the presence of the Shiga toxin 2 (Stx 2)-encoding bacteriophages in sewage. The Stx 2 gene was amplified by PCR from phages concentrated from 10-ml samples of sewage. Moreover, the phages carrying the Stx 2 gene were detected in supernatants from bacteriophage enrichment cultures by using an Stx 2-negativeE. coliO157:H7 strain infected with phages purified from volumes of sewage as small as 0.02 ml. Additionally, the A subunit of Stx 2 was detected in the supernatants of the bacteriophage enrichment cultures, which also showed cytotoxic activity for Vero cells. By enrichment of phages concentrated from different volumes of sewage and applying the most-probable-number technique, it was estimated that the number of phages infectious forE. coliO157:H7 and carrying the Stx 2 gene was in the range of 1 to 10 per ml of sewage from two different origins. These values were approximately 1% of all phages infectingE. coliO157:H7.

Aims: The removal and inactivation of faecal coliform (FC) bacteria, enterococci (ENT), sulphite-reducing clostridia (SRC), somatic coliphages, F-specific RNA bacteriophages and bacteriophages infecting Bacteroides fragilis in fresh waters. Methods and Results: Removal was studied in two areas of a river. The results showed different removal of each group of microbes. Faecal coliform bacteria were removed faster than any other, whereas SRC and bacteriophages infecting Bact. fragilis were the most persistent. Inactivation was measured by `in situ' experiments, which showed significant differences in survival of the different groups of bacterial and bacteriophage indicators. The SRC and bacteriophages were more resistant than faecal coliforms and enterococci, with the exception of F-specific RNA bacteriophages in the summer. Inactivation experiments with pure cultures of bacteriophages confirmed that phage B40-8 of Bact. fragilis was the most resistant. Conclusions: Bacteria and bacteriophages show different resistance to natural inactivation. The use of phages allows information to be obtained in addition to that provided by bacterial indicators. Somatic coliphages and phages infecting Bact. fragilis might supply that indicator function. Significance and Impact of the Study: Confirmation was obtained that bacteriophages provided additional information to that provided by bacterial indicators to monitor the natural inactivation of viruses and/or pathogens.

Objectives: This study quantifies quinolone antibiotic resistance genes (qnrA and qnrS) in DNA of phage particles isolated from faecally polluted waters and evaluates the influence of phage inducers on the abundance of antibiotic resistance genes in packaged DNA. Methods: qnrA and qnrS were quantified by qPCR in DNA of phage particles isolated from 18 raw urban wastewater samples, 18 river samples and 28 archived samples of animal wastewater. The bacterial fraction of the samples was treated with mitomycin C, ciprofloxacin, EDTA or sodium citrate under different conditions, and the number of resistance genes in DNA of phage particles was compared with the non-induced samples. Results: qnrA was more prevalent than qnrS, with 100% of positive samples in urban wastewater and river and 71.4% of positive samples in animal wastewater. Densities of qnrA ranged from 2.3×10 2 gene copies (GC)/mL in urban wastewater to 7.4×10 1 GC/mL in animal wastewater. qnrS was detected in 38.9% of urban wastewater samples, in 22.2% of river samples and only in one animal wastewater sample (3.6%). Despite the lower prevalence, qnrS densities reached values of 10 3 GC/mL. Both qnr genes and other resistance genes assayed (blaTEM and blaCTX-M) showed a significant increase in DNA of phage particles when treated with EDTA or sodium citrate, while mitomycin C and ciprofloxacin showed no effect under the different conditions assayed. Conclusions: This study confirms the contribution of phages to the mobilization of resistance genes and the role of the environment and certain inducers in the spread of antibiotic resistance genes by means of phages.

Some cdt genes are located within the genome of inducible or cryptic bacteriophages, but there is little information about the mechanisms of cdt transfer because of the reduced number of inducible Cdt phages described. In this study, a new self-inducible Myoviridae Cdt phage (ΦAA91) was isolated from a nonclinical O157:H7 Shiga toxin-producing Escherichia coli strain and was used to lysogenize a cdt -negative strain of Shigella sonnei . We found that the phage induced from S. sonnei (ΦAA91-ss) was not identical to the original phage. ΦAA91-ss was used to infect a collection of 57 bacterial strains, was infectious in 59.6% of the strains, and was able to lysogenize 22.8% of them. The complete sequence of ΦAA91-ss showed a 33,628-bp genome with characteristics of a P2-like phage with the cdt operon located near the cosR site. We found an IS 21 element composed of two open reading frames inserted within the cox gene of the phage, causing gene truncation. Truncation of cox does not affect lytic induction but could contribute to phage recombination and generation of lysogens. The IS 21 element was not present in the ΦAA91 phage from E. coli , but it was incorporated into the phage genome after its transduction in Shigella . This study shows empirically the evolution of temperate bacteriophages carrying virulence genes after infecting a new host and the generation of a phage population with better lysogenic abilities that would ultimately lead to the emergence of new pathogenic strains.

The idea that bacteriophage transduction plays a role in the horizontal transfer of antibiotic resistance genes is gaining momentum. Such transduction might be vital in horizontal transfer from environmental to human body–associated biomes and here we review many lines of evidence supporting this notion. It is well accepted that bacteriophages are the most abundant entities in most environments, where they have been shown to be quite persistent. This fact, together with the ability of many phages to infect bacteria belonging to different taxa, makes them suitable vehicles for gene transfer. Metagenomic studies confirm that substantial percentages of the bacteriophage particles present in most environments contain bacterial genes, including mobile genetic elements and antibiotic resistance genes. When specific genes of resistance to antibiotics are detected by real-time PCR in the bacteriophage populations of different environments, only tenfold lower numbers of these genes are observed, compared with those found in the corresponding bacterial populations. In addition, the antibiotic resistance genes from these bacteriophages are functional and generate resistance to the bacteria when these genes are transfected. Finally, reports about the transduction of antibiotic resistance genes are on the increase.