Abstract
Bacteriophages are bacterial-specific viruses and the most abundant biological form on Earth. Each bacterial species possesses one or multiple bacteriophages and the specificity of infection makes them a promising alternative for bacterial control and environmental safety, as a biotechnological tool against pathogenic bacteria, including those resistant to antibiotics. This application can be either directly into foods and food-related environments as biocontrol agents of biofilm formation. In addition, bacteriophages are used for microbial source-tracking and as fecal indicators. The present review will focus on the uses of bacteriophages like bacterial control tools, environmental safety indicators as well as on their contribution to bacterial control in human, animal, and environmental health.
Introduction
Bacteriophages, also known as phages, are prokaryotes viruses, being the most abundant life form, present in all environments and the predominant entities in the sea (; Suttle, 2005). Several studies have demonstrated a 1:5 relative abundance between bacteria and bacteriophage (; ; Rohwer, 2003). They were discovered independently by Twort (1915), who isolated them from Staphylococcus spp., and from patients with dysentery. described bacteriophage as a virus that has the capability to parasitize bacteria (Twort, 1915; ). Bacteriophages vary greatly in morphology and replicative characteristics, containing either RNA or DNA, being these parameters currently used by the International Committee on Taxonomy of Viruses (ICTV) for bacteriophage classification (King et al., 2012; Table 1). However, the identification of bacteriophages is difficult since there are no universally conserved markers, unlike e.g., the bacterial 16S rRNA gene (Paul et al., 2002), with only minor parts of bacteriophage genomes being used to determine family specific makers, such as the viral capsid g20 of T4 (; Marston and Sallee, 2003; Sullivan et al., 2008).
TABLE 1
| Family | Genus | Nucleic acid | Morphology | Main host |
| Leviviridae | Levivirus | ssRNA | Icosahedral | E. coli |
| Cystoviridae | Cystovirus | dsRNA | Icosahedral | Pseudomonas spp. |
| Microviridae | Phix174microvirus | ssDNA | Icosahedral | E. coli |
| Inoviridae | Fibrovirus | ssDNA | Filamentous or rod | Vibrio spp. |
| Podoviridae | P22virus | dsDNA | Tailed | S. typhimurium |
| Plasmaviridae | Plasmavirus | dsDNA | Spherical to pleomorphic | Mycoplasma spp. |
Taxonomy, morphological, and molecular characteristics of bacteriophage groups.
Bacteriophages can present different life cycles: lytic, lysogenic, and chronic (Figure 1A). Lytic bactériophages, such as T4 and MS2, insert their genetic material inside the bacteria, forcing the cell to produce a large amount of bacteriophage copies. After replication the membrane is then ruptured, releasing the new bacteriophages. Lysogenic bacteriophages (such as T1) possesses an alternative sub-cycle, in which the virus may integrate its DNA in the bacterial genome, becoming non-infectious and replicating together with the bacterial chromosome; the bacteriophage then becomes a prophage, producing new bacteriophage particles under appropriate conditions. Finally, chronic bacteriophages (such as M13) preserve their genome in the bacterial cell, in which the release from the host occurs gradually with less damage to the cell, preserving it longer (; ; Janczuk et al., 2016). There is an intimate relation between bacteriophages and bacterial cell functions acquisition (; , ). Bacteriophages can serve as points for genomic rearrangements due to their mosaic nature, with lysogenic bacteriophages even protecting bacteria from lytic infection in certain conditions (; Tree et al., 2014; Penadés et al., 2015). While bacterial hosts can benefit from the presence of bacteriophages (as they can express important regulators for adaptation to specific niches by the addition of bacteriophage genes in the cell’s genome) bacteriophages can be involved in the transfer of virulence genes, producing proteins participating in invasion, immune evasion, and toxins related to toxin-mediated diseases (; ; Tree et al., 2014; Penadés et al., 2015).
FIGURE 1
The specificity of bacteriophage infection allows their application in several areas such as biotechnology, ecology, health and environment (bacterial control), and as environmental monitoring agents (
In this review, a vast amount of scientific literature has been reviewed on the application of phage-based products, discussing the benefits and limitations of the use of bacteriophages as bacterial control tools in the health, food, and environmental fields.
Bacteriophages Application
Fighting Bacterial Infections
Bacterial infections are a major public health concern worldwide, representing an enormous economical and medical burden with a fatal outcome in a significant proportion of those affected. Dysentery caused by Shigella spp., Salmonella spp., Proteus spp. Staphylococcus, Escherichia coli, and Pseudomonas, usually associated with contamination of food and water, is a serious health problem affecting millions of people annually in the world, with shigellosis, a disease caused by Shigella spp., resulting in approximately 600,000 deaths each year (Walker et al., 1990; World Health Organization [WHO], 2017).
Lytic bacteriophages are the main tools for phage therapy, for their capacity to invade the bacterial cell and kill it. Lysogenic bacteriophages could also have an application, the transduction mechanisms could allow the use of bacteriophages as genetic tools to increase bacterial susceptibility to antibiotics; however, this approach has not been widely studied (Lu and Collins, 2009;
There is evidence that bacteriophages can be effectively used against bacterial infections, including those that have proved to be resistant to treatments with antibiotics (
Although treatment with bacteriophages seems a promising advantage compared to conventional antibiotics and disinfectants, a major drawback of this approach is the need for identification of the specificity range against the pathogenic bacteria prior to starting the bacteriophage treatment and the lack of protocols for testing bacterial susceptibility in vitro (Kutateladze and Adamia, 2010). As with antibiotics, if incomplete bacterial elimination by bacteriophages occurs, this could result in the pathogen reemergence (
However, contrasting findings of the bacteriophages cocktails effectiveness (compared to “conventional” treatments such as antibodies) were also achieved, with limitations and advantages in the use of cocktails to treat bacterial infections being extensively reviewed (
There are some limitations in the use of bacteriophages for treating human infections. Due to the ability of certain bacteriophages to integrate their genome into the host’s genome, care must be taken when selecting isolated bacteriophages. Some bacteriophages have potential for gene transfer; for instance, the bacterial acquisition of antibiotic resistance genes (ARGs) occurs by transduction, with bacteriophages acting as mobile genetic elements (MGE). Consequently, bacteriophages have been studied as possible vehicles of ARGs, not only as a source, but also as propagators in the environment (Gunathilaka et al., 2017). Bacteriophages containing ARGs are present in a wide range of environments; however, some environmental niches have a greater abundance, such as freshwater or marine environments (Lekunberri et al., 2017a,b;
Control Tools for Food and Environmental Bacterial Contamination
Foodborne pathogens are a major food safety threat, in 2010 an estimated 2 billion individuals contracted foodborne illnesses, resulting in 1 million deaths around the world (Kirk et al., 2015). Food safety is regarded by the World Health Organization [WHO] (2015) as a major obstacle in human development, especially in developing countries that lack infrastructure and proper environmental health practices to counter the issue. The application of bacteriophages has been proposed as an alternative tool to disinfect food and food-related environments (Pang et al., 2017). The advantage of this method is that bacteriophages kill their bacterial hosts without changing food organoleptic properties (Loc-Carrillo and Abedon, 2011; Perera et al., 2015). Also, bacteriophage low-cost large scale production, self-replicating nature, and low toxicity provide a cheap and safe disinfecting agent for low-income communities, being employed in the former Soviet Union for over 100 years (Skurnik et al., 2007;
The United States Department of Agriculture (USDA) approved some products based on bacteriophages as food sanitizers, such as ListShield™, Listex P-100™, SalmoFresh™, and Salmonelex™ (Hagens and Loessner, 2010). The use of a bacteriophage cocktail to inactivate foodborne bacteria like S. enteritidis and S. typhimurium on the chicken breast has also been proposed (
Bacteriophages also show significant potential in the animal production chain such as fish, poultry, shrimps, oysters, sheep, pork and also as additives in food products such as poultry meat and eggs (Moye et al., 2018). They can prevent foodborne pathogens such as Campylobacter spp., E. coli, L. monocytogenes, Salmonella enterica, and Shigella spp., that are the top five foodborne public health threatening pathogens (
Bacteriophages have shown very effective to control L. monocytogenes by the commercial product based on bacteriophages LISTEXP™100 reported a better efficacy against L. monocytogenes than nisin and sodium lactate in ready-to-eat (RTE) sliced pork ham (
The number of commercial solutions containing bacteriophages is increasing worldwide, being an emerging industry and field of research (Sulakvelidze, 2013; Vikram et al., 2020). Different examples of bacteriophage applications on food industry are already available: a three-bacteriophage cocktail (containing EC6, EC9, and EC11) was able to reduce E. coli contamination; E. coli ATCC 25922 and E. coli O127:H6 in Ultra High Temperature (UHT) milk at 25°C and under refrigeration temperatures (5–9°C) (McLean et al., 2013). The cocktail EcoShield™ was able to reduce 2 logs of E. coli O157:H7, 30 min after administration on leafy greens under packaging storage (
TABLE 2
| Host | Bacteriophage | Dose | Treatment time | Matrix | Reduction log | References |
| Listeria monocytogenes | LISTEX™ P100 | 107 PFU/cm2 | 30 min, 1, 2, 3, 7, 10, 14, 20, and 28 days | Roast beef and cooked turkey | 2 log10 CFU/cm2 | |
| FWLLm1 | 2.5 × 107 PFU/cm2 | 24 h | Ready-to-eat chicken breast roll | 2.5 log10 CFU/cm2 | ||
| P100/A511 | 3 × 108 PFU/g | 6 days | Hot dogs (sausages), cooked and sliced turkey breast meat (cold cuts), smoked salmon, mixed seafood (cooked and chilled cocktail of shrimp, mussels, and calamari), chocolate milk (pasteurized, 3.5% fat), mozzarella cheese brine (unsalted pasteurized whey from plastic bag containers containing fresh mozzarella cheese), iceberg lettuce (leaves), and cabbage (sliced fresh leaves) | 1–3 log10 CFU/cm2 | ||
| ListShield™ | 109 PFU/mL | 0, 2, 5, and 7 days | Fresh-cut melons and apples | 3.5 log10 CFU/cm2 | Leverentz et al. (2001) | |
| Salmonella nteritidis | SJ2 | 108 PFU/mL | 24 h | Raw and pasteurized milk cheeses | 1–2 log10 CFU/cm2 | Modi et al. (2001) |
| PHL 4 | 1010 PFU/mL | 24 h | Poultry carcass | 3 log10 CFU/mL | Higgins et al. (2005) | |
| Salmonella typhimurium | Felix-O1 | 5.25 × 106 PFU | 24 h | Chicken frankfurters | 2 log10 CFU/g | Whichard et al. (2003) |
| SalmoFresh | 108 PFU/mL | 5 h | Ready-to-eat chicken products | 2 log10 CFU/mL | ||
| S. enteritidis and S. typhimurium | wksl3 | 2.2 × 108 PFU/mL | 1, 2, 3, 5, and 7 days | Chicken skin | 3 log10 CFU/mL | Kang et al. (2013) |
| SalmoFREE | 108 PFU/mL | 36 days | In vivo–chicken production | 3 log10 CFU | ||
| Salmonelex™ | 109 PFU/mL | 24 h | Ground beef and ground pork | 1.1 and 0.9 log10 CFU/g | Yeh et al. (2017) |
Current commercial products containing bacteriophages and conditions for use.
Indicators of the Presence of Foodborne Pathogens
Bacteriophages have been suggested as an alarm system in food and environmental microbiology and epidemiology since they generally fit the indicator criteria of pollution. Bacteriophages can be used as fecal indicators or microbial water quality bioindicators as an early warning of contamination by sewage, and as an efficiency marker of water or wastewater treatment (Yahya et al., 2015). This can be attributed to the bacteriophage response to the presence of pollutants, they are characteristic to adsorb to solid particles in the environment, and also due to some limitations of traditional indicators for public health such as fecal coliforms, E. coli and enterococci (
Somatic coliphages are more persistent than traditional indicators, being also more resistant to sludge treatments, particularly when adsorbed to surfaces (Martín-Díaz et al., 2020). Many authors highlight the use of bacteriophages as indicators not only for enteric pathogenic bacteria, but also for enteric viruses such as human noroviruses, adenoviruses, and rotaviruses (
One of the challenges with bacteriophage application is related to bacteriophage-host interaction, which could vary depending on exposition temperature, where greater bacterial reductions are associated with higher temperatures (Tomat et al., 2013). The use of bacteriophages on wastewater treatment systems is based on their lytic capacity, which is a useful tool for the removal of human and animal pathogenic bacteria from wastewater or applied as an indicator for the presence of bacteria in wastewater treatment systems (Stefanakis et al., 2019). MS2 bacteriophages have been proposed to be suitable as operational monitoring indicators as established by guidelines of Australia, due to resistance to variation of pH and temperature (
Challenges, Concerns and Trends in the Use of Bacteriophages for Environmental Health Purposes
Although a worldwide acceptance of bacteriophages as environmental agents is not yet achieved, bacteriophage-based technologies in the environmental field are still being developed. Besides being employed as monitoring agents, or by directly controlling pathogens, bacteriophages have demonstrated promising results in agricultural microbiome modulation, increasing crop production by infecting crop detrimental bacteria in leaves and soil (Jones et al., 2012; Ye et al., 2019). Plant-soil microbiome modulation by bacteriophages was even related to an increase in ammonium concentration, likely through lysis of certain bacteria and overall community shifting (
Similar to soil applications, bacteriophages appears to have a low environmental impact in fish farming plants compared to “traditional” methods such as antibodies, as it is necessary a continuous application since seawater is considered a reservoir of antibiotic resistance bacteria (
In sight that bacteriophages may persist in food production plants due the virus high stability, potentially creating a genetic hazard in such facilities, the adoption of strategies for the use and manipulation of bacteriophages are required to counter bacteria resistance and achieve successful pathogen control (Hungaro et al., 2013;
Aside from ARGs screening and mapped host targeting, the phage product must be suitable to the external factors present in the area of application, being resistant to the pH, temperature, UV radiation, salinity and ionic profile of the environment (Jończyk et al., 2011; Zaczek-Moczydłowska et al., 2020). In addition, the criteria for bacteriophage use in food and the environment, such as minimum exposure time, minimum effective dosage and characterization of animal local application must be established to achieve the expected therapy result while avoiding potentials drawbacks such as the presence of inhibitory compounds like antibodies, whey proteins or bacteriocins (
Special regards covering the bacteriophage properties are also advisable for an optimal and highly scalable confection of the final viral product, being of special relevance in extensive environmental applications. Bacteriophage production is directly related to the characteristics of the bacterial host (e.g., metabolic activity, growth rate, stage in cell life cycle, and abundance of bacteriophage receptors on cell surface), and the bacteriophage attributes (e.g., lysis time, burst size, and adsorption rate) (
With advances in molecular biology the engineering of bacteriophage particles allows a selected virus (favorited due desirable characteristics to the target therapy, such as host range and replicative potential) to be further enhanced through genetic modifications, removing undesirable viral properties that could hinder the application of the bacteriophage product as a safe and reliable object (
Although bacteriophages present certain safety drawbacks, largely due to negligence of mapping the product properties, bacteriophages are still considered safer than chemical treatments in environmental and food processing plants treatments applications (Meaden and Koskella, 2013; Zaczek et al., 2014). Bacteriophages stand as cheap and highly flexible structures, being able to be selected and edited for different approaches (
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Statements
Author contributions
PR directs the first version of the manuscript. GF and DR-L revised the first version of the manuscript and wrote the final version of the manuscript. The rest of the authors gave fundamental contributions to the first version of the manuscript. All authors contributed to the article and approved the submitted version.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
bacteriophages, food safety, biocontrol, foodborne pathogens, antimicrobial resistance
Citation
Rogovski P, Cadamuro RD, da Silva R, de Souza EB, Bonatto C, Viancelli A, Michelon W, Elmahdy EM, Treichel H, Rodríguez-Lázaro D and Fongaro G (2021) Uses of Bacteriophages as Bacterial Control Tools and Environmental Safety Indicators. Front. Microbiol. 12:793135. doi: 10.3389/fmicb.2021.793135
Received
11 October 2021
Accepted
11 November 2021
Published
30 November 2021
Volume
12 - 2021
Edited by
Laurent Dufossé, Université de la Réunion, France
Reviewed by
Diogo Silva, University of Brighton, United Kingdom; Hak-Kim Chan, The University of Sydney, Australia
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© 2021 Rogovski, Cadamuro, da Silva, de Souza, Bonatto, Viancelli, Michelon, Elmahdy, Treichel, Rodríguez-Lázaro and Fongaro.
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*Correspondence: David Rodríguez-Lázaro, drlazaro@ubu.esGislaine Fongaro, gislaine.fongaro@ufsc.br
This article was submitted to Food Microbiology, a section of the journal Frontiers in Microbiology
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