key: cord-334108-4ey725dv authors: Seymour, I.J.; Appleton, H. title: Foodborne viruses and fresh produce date: 2008-07-07 journal: J Appl Microbiol DOI: 10.1046/j.1365-2672.2001.01427.x sha: doc_id: 334108 cord_uid: 4ey725dv nan Raw and minimally processed fruits and vegetables are typically sold to the consumer in a ready-to-use or readyto-eat form. These products do not generally contain preservatives or antimicrobial agents and rarely undergo any heat processing prior to consumption. For many years raw fruits and vegetables have been implicated as vehicles for transmission of infectious micro-organisms. Although fresh produce can support the growth and/or survival of many pathogenic bacteria there is little published information on the stability of human pathogenic viruses on these food products. Viruses cannot grow in or on foods but may sometimes be present on fresh produce as a result of faecal contamination. This contamination can arise at source in the growth and harvesting area from contact with polluted water and inadequately or untreated sewage sludge used for irrigation and fertilization. Alternatively, fruits or vegetables handled by an infected person might become contaminated with virus and transmit infection. The most frequently reported foodborne viral infections are viral gastroenteritis and hepatitis A: both have been associated with the consumption of fresh fruit or vegetables. In recent years it has been recognized that viruses are an important cause of foodborne disease. Unlike bacteria, viruses do not grow or multiply in or on foods, but foods may become contaminated with human viruses and transmit infection. There are many groups of viruses which could contaminate food items, but the major foodborne viral pathogens are those that infect via the gastrointestinal tract, such as the gastroenteritis viruses and hepatitis A virus. It is these viruses that are the main subject of this review. Viruses that infect via the gastrointestinal tract are excreted in faeces and may also be present in vomit. Foods become contaminated either directly by infected people or through sewage pollution. Those enteric viruses, which are commonly associated with foodborne outbreaks, either cannot be cultured in the laboratory or can only be cultured with dif®culty. Hence information and experimental studies on survival and recovery of viruses from foods often relates to other virus types that are readily cultured. Some of these viruses may be good models for important foodborne viral pathogens, but others may have widely differing characteristics. Enteroviruses, such as Coxsackieviruses and vaccine strains of poliovirus, have been used particularly. They infect via the gastrointestinal tract, occur in the environment as a result of sewage contamination and are relatively stable. However, there are very few published reports of foodborne outbreaks of illness caused by enteroviruses. There is the potential for contamination with other virus groups, such as respiratory viruses, although transmission to humans through foods has not been recognized. Infrequently endogenous contamination of meat and milk can occur with viruses such as tick-borne encephalitis. Such zoonotic infections have been reviewed by and need not be considered in this review. Viruses are usually transmitted directly from person to person, but epidemiological and laboratory investigations indicate that viral diseases can on occasions be transmitted via foods, particularly those that are minimally processed. These include seafood, especially the bivalve molluscan shell®sh, and fresh fruits, vegetables and salad items. It might be expected that any virus that infects via the gastrointestinal tract could be foodborne. In practice, however, the most commonly reported foodborne viral infections are viral gastroenteritis and less frequently hepatitis A. It is believed that the incidence of both is greatly under reported, but for different reasons. Viral gastroenteritis is a relatively mild disease and most people do not consult a medical practitioner; hence, the majority of cases are not investigated and are not reported. A recent national study funded by the Department of Health of infectious intestinal disease (IID) in the community indicated that for every case of IID detected by national laboratory surveillance, there are 136 cases in the community. The study also concluded that a smaller proportion of cases due to common viral pathogens are reported than cases due to common bacterial pathogens (Wheeler et al. 1999; Food Standards Agency, 2000) . Viral gastroenteritis has a short incubation period of 1±4 days depending on the type of virus. This means that when cases are investigated, the possibility of foodborne transmission is likely to be considered. In contrast, hepatitis A is often a more severe disease and is more likely to be reported. However, the incubation period is 3±6 weeks and hence an association with a food source is unlikely to be made, unless there is a very clearly de®ned outbreak. Several different viruses cause gastroenteritis: the most important include rotavirus, the small round-structured viruses (SRSV) otherwise known as Norwalk-like viruses (NLV), astrovirus and adenovirus types 40 and 41. However, in almost all foodborne outbreaks where a virus is identi®ed, it is an NLV. Rotavirus and astrovirus are only rarely implicated. Adenovirus has not been associated with food or waterborne transmission. Viral gastroenteritis is usually regarded as a mild selflimiting disease lasting 24±48 h. However, people can feel debilitated for 2 or 3 weeks, which has considerable economic implications in terms of working days lost and impaired performance. Symptoms include malaise, abdominal pain, pyrexia, diarrhoea and/or vomiting. A range of symptoms occurring in an outbreak should alert investigators to the possibility of a viral cause. The viruses are usually transmitted by the faecal±oral route, but they are also present in vomitus. Onset of viral gastroenteritis may be sudden and can commence with projectile vomiting. Virus will be disseminated over a wide area in aerosol droplets, which is a particular hazard where food is being prepared * Where the organism identi®ed in an outbreak was the main aetiological agent. Outbreaks in which there was foodborne transmission followed by person-to-person transmission, but the proportion of each mode was unknown. Data from PHLS Communicable Disease Surveillance Centre. and laid out. Although most transmission is directly from person to person, contaminated food and water can give rise to common source outbreaks. The infective doses are not known, but the evidence from volunteer studies and the typically high attack rates observed in outbreaks suggest that they are very low (Westwood and Sattar 1976; Caul et al. 1988) . For instance, it has been estimated that NLVs have an infective dose of between 10 and 100 virus particles (Caul 1994; Stolle and Sperner 1997) . Viruses account for 6% of foodborne and 5% of waterborne outbreaks occurring in England and Wales reported to the PHLS Communicable Disease Surveillance Centre (CDSC) (Appleton, 2000; O'Brien et al. 2000) (Table 1) . A recent paper prepared by the Public Health Laboratory Service (PHLS) reported on the microbiological status of ready-to-eat fruit and vegetables between 1992 and 1999 in England and Wales (O'Brien et al. 2000) . Fruit and vegetables accounted for 4á3% (60/1408) of the total foodborne outbreaks reported during that period. The most commonly identi®ed aetiological agent was the NLVs, which were linked to 20% of the outbreaks. The causative organism of a further 42% of outbreaks was reported as unknown, although the clinical and epidemiological features of these outbreaks suggested that the majority (64%) were also viral. 3.1.1 Norwalk-like viruses. This group of viruses infects all age groups. There is a variable incubation period of 12± 60 h, which is thought to be dose-dependent. It occurs all year round, although in temperate climates most infections occur over the winter months. These viruses are responsible for both sporadic cases of gastroenteritis in the community and for outbreaks in schools, hospitals, old people's homes, hotels and cruise ships. The national IID study indicated that viruses are the most common cause of IID in the community, with NLV the most frequently reported organism (Wheeler et al. 1999; Food Standards Agency, 2000) . From 1992 to 1997, NLVs accounted for one-third of all gastroenteritis outbreaks reported to the PHLS Communicable Disease Surveillance Centre (CDSC) and the number of outbreaks of NLV gastroenteritis exceeded the number of outbreaks of salmonellosis. Unlike the salmonellosis outbreaks, however, only 6% of the NLV outbreaks were known to be food or waterborne (Appleton, 2000) . The virus is extremely infectious and secondary cases are a characteristic feature of foodborne outbreaks. Therefore, it is not always possible to determine whether illness is acquired from a foodborne source or by person-to-person transmission (see Table 1 ). This accounts partly for underrecognition of the extent of foodborne transmission of these viruses. In a review of NLV (SRSV) infection in England and Wales between 1990 and 1995 by the PHLS, direct foodborne transmission could be ascertained in only 14% of outbreaks (Dedman et al. 1998 ). There have been reports of outbreaks where NLVs have been epidemiologically associated with various items of fresh produce, such as washed salads (Lieb 1985; Lo et al. 1994) , imported frozen raspberries (Ponka et al. 1999) , coleslaw (Currier 1996) , green salads (Grif®n et al. 1982) , fresh cut fruits (Herwaldt et al. 1994 ) and potato salad (Patterson et al. 1997) . The virus was discovered in 1972 by electron microscopy (Kapikian et al. 1972) (Fig. 1 ). The ®rst virus originated from the town of Norwalk in the United States, and became the prototype of the group. The name small roundstructured virus (SRSV), which describes the morphology of the virus particle (Caul and Appleton 1982, Appleton, 2000) , was used in the United Kingdom and elsewhere until recently. It has now been agreed informally by virologists working with this group to adopt the name Norwalk-like virus, for the present, so as to bring some conformity to the nomenclature of these viruses. However, formal names have not yet been agreed by the International Committee on Virus Nomenclature. The NLVs form a complex group of viruses. They have formally been classi®ed with the Caliciviridae and are often referred to as human caliciviruses. They are split into two broad genogroups. Most viruses in these two groups have the typical morphology of a 30±35 nm diameter particle with an amorphous surface and ragged outline, as originally described for the SRSV group (Caul and Appleton 1982) . Within the Caliciviridae there is a second genus of human gastroenteritis viruses, provisionally named Sapporo-like viruses (SLVs). The SLVs have the morphology of classical caliciviruses and are genomically distinct from the NLVs . On sequencing, some strains with There are suggestions that the epidemiology of SLVs differs from NLVs, in that SLVs mainly cause infections of young children. It is not clear whether SLVs are of signi®cance in foodborne infections and more studies are needed to clarify their role. Genotypic analysis is being used increasingly to investigate the epidemiology of these two groups of viruses (Fankhauser et al. 1998; Maguire et al. 1999; Hale et al. 2000; Hedlund et al. 2000; Koopmans et al. 2000) . There are several serotypes of human caliciviruses, which correspond broadly with the genotypic groups. Most studies have been carried out with NLVs, and indicate that immunity is complex and short-lived (Matsui and Greenberg, 2000) . Volunteer studies have shown that people can be infected repeatedly with the same virus strain (Parrino et al. 1977; Johnson et al. 1990 ). 3.1.2 Rotavirus. Rotaviruses mainly infect young children . It is estimated that they cause one million deaths a year in children under 5 years of age, mostly in developing countries. In developed countries deaths are relatively rare, but rotavirus gastroenteritis is the most frequent reason for admission of young children to hospital. Rotaviruses consistently account for around 80% of all gastroenteritis viruses reported to CDSC, although this ®gure is probably biased by reports of hospitalized children, rather than the occurrence in the community, where NLVs are of greater signi®cance. Foodborne and particularly waterborne spread are probably a signi®cant route of transmission in developing countries, but in developed countries reports are rare (Table 1) . 3.1.3 Astrovirus. The astroviruses form a morphologically distinct group of viruses, and are named from the ®ve-or six-point star seen by electron microscopy on the surface of some particles. Astroviruses have mainly been associated with illness in young children, often under 1 year of age. Reports of astrovirus infection in older children and adults are infrequent, although outbreaks have been reported in the elderly. This may re¯ect testing policy: detection normally relies on electron microscopy, which is insensitive and often not performed on sporadic samples from adults. The use of more sensitive molecular detection methods is required to assess the incidence and epidemiology of these viruses. Astroviruses have been seen in some adults following the consumption of shell®sh or contaminated water, but these incidents appear to be comparatively rare (Kurtz and Lee 1987; Kurtz 1994) (Table 1) . There are two forms of enterically transmitted hepatitis ± hepatitis A and hepatitis E (Cromeans et al. 2001 ). The most characteristic symptom of hepatitis A is jaundice, but milder symptoms of nausea and general malaise without jaundice are common. Patients may feel unwell for several weeks, but recovery is complete. Deaths are rare. Some infections, particularly in children, may be asymptomatic. Like viral gastroenteritis, transmission is by the faecal±oral route, but the primary site of viral replication is the liver. Virus excretion may commence up to a week before symptoms are apparent, making control dif®cult. The epidemiology of foodborne hepatitis A is essentially similar to that of viral gastroenteritis. Food-and waterborne outbreaks have been recognized for over 40 years, but are infrequently reported. Epidemiological evidence to link hepatitis infection to food and water sources is sparse, because of the long incubation period. Between 1992 and 1997, 228 outbreaks occurring in England and Wales were reported to CDSC, but only one of these was known to be foodborne. That outbreak was associated with shell®sh. From 1992 to 1999, CDSC received 19 747 laboratory-con®rmed reports of cases of hepatitis A. The source of most of these infections was unknown and just 155 were recorded as foodborne. In the United States, the Centers for Disease Control and Prevention (CDC) placed hepatitis A as the sixth leading cause of foodborne disease from 1988 to 1992 (Centers for Disease Control and Prevention 1996) . Outbreaks associated with fresh produce, particularly soft fruits and salads, have been reported from several countries. Iceberg lettuce (Rosenblum et al. 1990 ), strawberries (Niu et al. 1992) , diced tomatoes (Williams et al. 1995) and salad items (Pebody et al. 1998 ) have all been implicated. A recent outbreak of hepatitis A in the United States was associated with consumption of food items containing frozen strawberries imported from Mexico (Anon 1997; Cliver 1997) . In the United Kingdom, outbreaks have been traced to frozen raspberries. There was evidence that the raspberries in these outbreaks were contaminated by infected fruit-pickers (Noah 1981; Reid and Robinson 1987; Ramsay and Upton 1989) . There is only one serotype of hepatitis A. Following infection immunity is lifelong. An effective vaccine is available. Currently it is used for persons at high risk, such as travellers (Department of Health et al. 1996) . Food packagers and food handlers in the United Kingdom have not been associated with HAV transmission suf®ciently often to justify routine immunization, except in outbreaks. The incidence of hepatitis A in developed countries has fallen in recent years and hence a susceptible population has built up. As endemic infection declines, it is possible that an increase in foodborne outbreaks will be seen. The yearround global distribution of fruit and vegetable products poses a risk of infection, particularly when these products are imported from countries with a high incidence of hepatitis A. Hepatitis E has been associated with large waterborne outbreaks in some developing countries, notably in Asia, Africa and Central America. Foodborne transmission has been suggested, but not proved conclusively. Illness appears more severe than hepatitis A, particularly in pregnant women where a death rate of 17±33% has been observed (Cromeans et al. 2001) . The primary source of infection appears to be contaminated water rather than person-to-person spread. Secondary person-to-person transmission is estimated at only 0á7±8% (Cromeans et al. 2001) . Cases in the United Kingdom are reported infrequently and are mainly imported from endemic areas. With the worldwide distribution of foods, vigilance should be maintained. Viruses are very small micro-organisms, and basically comprise a nucleic acid core of either DNA or RNA, surrounded by a protein coat. They require living cells in order to replicate and generally have a very restricted host range. Viruses do not multiply in foods or water, or in or on any other environmental sample. However, viruses can survive outside living cells and remain infectious. Enteric viruses are hardy and survive well in the environment. These viruses survive on inanimate surfaces, on hands and in dried faecal suspensions (Green et al. 1998a; Barry-Murphy et al. 2000; Bidawid et al. 2000; Sattar et al. 2000) . Lingering outbreaks have occurred in hospitals, in residential homes and on cruise ships, probably as a result of environmental contamination. NLVs have been detected by PCR in environmental swabs from hospital lockers and hotel carpets supposedly cleaned after incidents of vomiting (Green et al. 1998a) . The viruses survive just as well on kitchen surfaces and food preparation areas. In one reported outbreak, a kitchen worker vomited into a sink. The following day the sink, which had been cleaned with a chlorine-based disinfectant, was used for washing salad and an outbreak of gastroenteritis associated with NLVs ensued (Patterson et al. 1997) . Enteric viruses are acid stable and so are able to survive in the gastrointestinal tract. It is likely that they will survive food processes designed to produce the low pH that inhibits bacterial spoilage organisms (e.g. pickling in vinegar and fermentation processes that produce foods such as yoghurt). Both NLVs and hepatitis A virus retain activity after exposure to acidity levels below pH 3 Scholtz et al. 1989) . Most viruses remain infectious after refrigeration and freezing. Frozen foods, that have not received further cooking, have been implicated in a number of incidents of viral gastroenteritis and hepatitis A (Noah 1981; Reid and Robinson 1987; Ramsay and Upton 1989; Niu et al. 1992) . Gastroenteritis viruses and hepatitis A virus are inactivated by conventional cooking processes, but retain their infectivity after heating to 60°C for 30 min Parry and Mortimer 1984; Fleming et al. 1985; Millard et al. 1987; Slomka and Appleton 1998) . It is uncertain whether they would be inactivated completely in some pasteurization processes. NLVs cannot be cultured in the laboratory and until recently detection relied on the use of electron microscopy. This technique is fairly insensitive and requires a minimum of 10 6 virus particles per ml of sample. It has been used widely for detection of virus in faecal samples from patients, but cannot be used for looking for the lower concentration of virus particles present in contaminated food, water and environmental samples. Sequencing of the genome of the Norwalk virus has led to the development of PCR assays, with greatly enhanced sensitivity for virus detection . However, there is great genomic diversity among the NLVs and one set PCR primers will not detect all strains (Norcott et al. 1994) . PCR assays are being used for the examination of food samples, particularly shell®sh, but far more complex nucleic acid extraction techniques are required than when working with clinical specimens from patients (Atmar et al. 1993; Green et al. 1998b ). There are also greater problems with naturally occurring inhibitors to the PCR reaction in these types of samples. NLVs have been detected in samples of raspberries associated with an outbreak of gastroenteritis in Quebec. Sequence analysis demonstrated that the strain of NLV identi®ed in the raspberries was identical to that found in the patients (Gaulin et al. 1999) . Expression of recombinant virus capsids in yeast and insect cells is allowing the development of ELISA-based diagnostic assays, but reagents are not widely available and so far the tests only detect a very limited number of NLV strains (Jiang et al. 2000) . Further development and more widespread use of ELISA tests will greatly facilitate the detection of NLVs in clinical samples, although such tests may not be suf®ciently sensitive to detect virus in food samples. At the present time, PCR and ELISA assays for NLVs are only available in specialist laboratories and are not used for the routine testing of food samples. Commercial test kits are not yet available. Rotavirus and astrovirus can both be grown in cell cultures in the laboratory. However, it is unreliable and time-consuming for isolation from primary specimens and is not normally used. Rotavirus is frequently detected using commercial ELISA or latex agglutination tests and PCR assays are available. Rotavirus has been detected in lettuce (Hernandez et al. 1997 ) and shell®sh samples, but it is not clear if these were of human origin. Electron microscopy is still the most usual method for the detection of astroviruses, although PCR assays are used in a few laboratories. Diagnosis of hepatitis A infection in patients is by detection of speci®c IgM antibody, since virus excretion has largely ceased by the time illness becomes apparent. The virus can be cultured in the laboratory, but this is a long and unreliable procedure. In one outbreak at a summer camp in the United States, virus was isolated from the drinking water supply, but this took 21 weeks. PCR assays have been developed and have been used for detecting virus in water, shell®sh and other food and environmental samples. Due to the long incubation period of hepatitis A, food items are not usually available for testing, even if suspected as the source of illness. In particular, minimally processed fruits and vegetables have a short shelf life. There have been a few experimental studies to investigate seeding and recovery of viruses from fresh produce. Transfer of hepatitis A virus to lettuce leaves has been investigated Sattar et al. 2000) . Rotavirus and poliovirus were recovered from the surface of vegetables in a method described by Badawy et al. (1985b) . Average recovery rates of 80 and 65%, respectively, were obtained from lettuce; however, recovery of rotavirus from non-leafy vegetables was lower, averaging 44%. Ward et al. (1982) also recovered poliovirus and adenovirus from vegetable surfaces, obtaining mean ef®ciencies of approximately 55±58%. There is a need to develop more effective quantitative methods in order to assess the survival of viruses on fresh produce and to determine the decontamination ef®ciencies of current commercial washing systems for fruit and vegetables. Fruits and vegetables may become contaminated with viruses in two ways. First, they may be contaminated in their growing area before harvest by coming into contact with inadequately treated sewage or sewage polluted water. Secondly, contamination can arise during processing, storage, distribution or ®nal preparation either directly from infected people or by contact with a contaminated environment. In most outbreaks of foodborne viral disease involving fresh produce, it is not known whether contamination took place before, during or after harvest. Guidelines issued by the World Health Organization state that fruits and vegetables to be eaten raw should not be fertilized with sewage or irrigated with contaminated water (Beuchat 1998) . Sewage sludge is sometimes applied to agricultural land, with the bene®t that useful plant nutrients and organic matter are recycled to the soil. However, the UK government is proposing more stringent controls for harvesting vegetables from land where conventionally processed sewage sludge is applied (ADAS, 2000) . The transmission of viruses is thought to be mainly by surface contamination. There are relatively few reported studies on the possible uptake of viruses within damaged plant tissues during primary growth. Studies with poliovirus report that virus can in®ltrate into the roots and body of plants from the soil (Oron et al. 1995) , but there is no evidence of illness from this source. Viruses from sewage do not bind readily with soil particles and can enter groundwaters leading to contamination of water sources. The viruses causing gastroenteritis and hepatitis A appear to be extremely infectious in very low doses. Large numbers of virus particles can be excreted in the faeces from an infected person. Levels of the order of 10 6 ±10 11 infective units per gram have been estimated (Feachem et al. 1983) . Poor personal hygiene is therefore a major route through which viruses can directly reach foods. Virus can be transferred from faecally contaminated ®ngers to foods or to work surfaces and door handles. There is a signi®cant risk of contamination from ®eld workers who do not have adequate on-site toilet and hand-washing facilities. Even when these facilities are put in place, the workers need to be supervised in such a way as to ensure that the facilities are used (Cliver 1994) . In an outbreak of hepatitis A, associated with frozen raspberries, infection was con®rmed in a fruit picker on the farm where the raspberries were cultivated (Ramsay and Upton 1989). A number of outbreaks have also been linked to contamination of fresh produce from the vomitus of infected food handlers ). It has been suggested that between 20 and 30 million virus particles are liberated during vomiting (Reid et al. 1988; Caul 1994) . As well as direct transmission, aerosols produced by vomiting can contaminate exposed food, or surfaces with subsequent transfer to foods. Human enteric viruses will potentially be present in any type of water contaminated by human faecal material and by sewage. The Department of Environment, Transport and Regions (DETR) jointly with UK Water Industry Research Limited and the Environment Agency, recently commissioned four reviews on enteroviruses. These covered the source (Sellwood et al. 1999 ) and survival (Irving and Morris 1999) in the environment and their fate through sewage treatment processes (Merrett and Weatherley 1999) . Mounting evidence suggests that viruses can survive long enough and in high enough numbers to cause human diseases through direct contact with polluted water or contaminated foods (Nasser 1994; Bosch 1995) . Irving and Morris (1999) concluded that a thorough and valid assessment of the occurrence and signi®cance of viruses in natural waters is hampered by lack of reliable information. They suggested that this is due to inef®cient analytical techniques, and because different analytical methods have been used so that comparisons on survival data between different studies cannot be made. However, it does appear that different types of viruses are inactivated at different rates under identical conditions, and therefore no single microorganism can be expected to be an indicator for all viruses. Temperature is an important factor, with low temperatures favouring viral survival in natural waters. Raphael et al. (1985) found no signi®cant drop in rotavirus titre after 64 days at 4°C in raw water, treated tap water or ®ltered water. However, a 99% drop in titre was observed after 10 days at 20°C. Astrovirus survival has been demonstrated in drinking water after 90 days at 4°C (Abad et al. 1997b ). Nasser et al. (1993) concluded that hepatitis A virus and poliovirus could survive in wastewater and groundwater for 90 days or more at 10°C . Hepatitis A virus and poliovirus were shown to survive in excess of one year in mineral water stored at 4°C (Biziagos et al. 1988 ). Hepatitis A virus can survive in fresh or salt water for up to a year (Sobsey et al. 1988) . Evidence suggests that adsorption of viruses to particulate matter and sediments confers substantial protection against inactivating in¯uences. Salinity and pH do not appear to have a signi®cant direct effect on virus survival under conditions normally found in natural waters, but may have indirect effects by modifying interaction of viruses with particulates. There is some evidence that solar radiation promotes inactivation of viruses, but the effects have not been extensively studied. Development of PCR-based assays has allowed the detection of NLVs in both river water and seawater Wyn-Jones et al. 2000) . In 1997, an outbreak of NLV gastroenteritis occurred among canoeists and was associated with river water at a water sports centre (Gray et al. 1997) . When hepatitis A virus was detected in lettuce from Costa Rica, it was suggested that the possible source of contamination was the discharge of untreated sewage into river water used to irrigate crops, which is common practice in some less well-developed countries (Hernandez et al. 1997) . In another outbreak of hepatitis A, traced to commercially distributed lettuce or tomatoes, it was hypothesized that contamination may have occurred in the ®elds from dirty water used for growing or irrigation, or possibly from the use of night soil, although this was dif®cult to prove (Rosenblum et al. 1990) . Enteric viruses may contaminate soil through the land disposal of sewage sludge and dirty irrigation water. A number of research studies have investigated the survival of human pathogenic viruses in soils with con¯icting results. Survival appears to depend on a number of different variables, particularly the growing season, soil temperature, rainfall, soil type and composition. For example, viable poliovirus was recovered from spray-irrigated soil after 96 days during the winter season Tierney et al. 1977) . This compared to a maximum survival period of only 11 days during the summer, which suggested the higher temperature and solar radiation levels in the warmer seasons accelerated viral inactivation. The possibility also exists that viruses may be mechanically transmitted to fruits and vegetables during harvest. Sadovski et al. (1978) noted the persistence of inoculated poliovirus in drip irrigation pipes and soil. Moderate environmental conditions and alluvial-type soil, which restricts water in®ltration, enhanced viral recoveries in the upper soil layers. Oron et al. (1995) found that relatively high soil temperature (30°C) and a low moisture content hindered poliovirus survival. Wet soil conditions are frequently associated with low soil temperature. Gerba (1983) reported that a large proportion of outbreaks of waterborne disease in the Unite States resulted from contaminated groundwater. Climate, the nature of the soil and the nature of the resident micro¯ora determine virus survival and retention within soil particles. Both electrostatic and hydrophobic interactions are thought to contribute towards virus adsorption and are controlled by the characteristics of the soil. Some investigations have focused on the survival of viruses on inanimate environmental surfaces such as stainless steel, glass and plastics. Abad et al. (1994) observed that a range of enteric viruses, including hepatitis A virus and rotavirus, persisted for extended periods (greater than 30 days) on several types of porous and nonporous surfaces. Greater virus survival was noted at 4°C than at 20°C. The effect of relative humidity on survival of hepatitis A virus on nonporous surfaces has been investigated Sattar et al. 2000) . At 5°C, relative humidity had little effect on survival time, but at 20°C survival was longest when relative humidity was low. It is apparent from the lingering outbreaks that have occurred on cruise ships that NLVs survive well on environmental surfaces. NLVs have been detected in swabs of lockers in hospital outbreaks and from hotel carpets (Green et al. 1998a; Barry-Murphy et al. 2000) . A disinfectant formulation is considered to be effective if it is capable of inducing a 1000-fold (99á9%) or greater reduction in the virus titre Springthorpe et al. 1986) . Experimental studies have shown that a free chlorine level of 5000 ppm reduced the infectivity titre by more than 99á9% on stainless-steel disks V I R U S E S A N D F R E S H P R O D U C E 765 contaminated with the enteric viruses Coxsackievirus B3 and hepatitis A virus, and the respiratory viruses adenovirus type 5, parain¯uenza virus type 3 and coronavirus 229E (Sattar et al. 1989; Mbithi et al. 1990 ). The virucidal action of sodium hypochlorite (1250 ppm at pH 9á56) was also tested against hepatitis A virus, human rotavirus and a Bacteroides fragilis bacteriophage dried on polystyrene (Abad et al. 1997a ). Overall, a less than 1000-fold titre reduction was achieved for all the viruses examined. Chlorine is a common disinfectant used by many fresh produce processors to wash fruits and vegetables (Beuchat 1998; Seymour 1999) . However, chlorine levels greater than 200 ppm are thought to cause adverse discoloration (bleaching) and off avours in the ®nished product (Hurst and Schuler 1992) . Survival times for some enteric viruses have been determined on a range of different fruit and vegetable commodities. It is dif®cult to draw conclusions from the different studies, since experimental conditions and methods varied. However, most of these studies report viability in excess of the product shelf life. Konowalchuk and Speirs (1974) established no signi®cant loss in Coxsackievirus B5 titre when contaminated lettuce was stored for 16 d under moist conditions at 4°C, but some inactivation took place during storage under dry conditions. They hypothesized that under conditions of low or no moisture the aqueous part of the virus inoculum evaporated leaving the virus exposed to air and/or salts. Celery, lettuce and carrots stored at 4°C supported the survival of a range of enteric viruses for up to 8 days (Konowalchuk and Speirs 1975a) . Badawy et al. (1985a) indicated that rotavirus SA-11 (a simian rotavirus that can be cultured) survived on lettuce, radishes and carrots for up to 30 days at 4°C. Viral inactivation at room temperature (25°C) was signi®cantly greater than at 4°C; however, viable rotavirus SA-11 was still detected on lettuce after 25 days. They concluded that the rough or irregular surfaces present on lettuce might offer some additional protection for virus particles. Indeed, protected segments of plants such as the roots, closed leaves and internal fruit parts, may offer favourable conditions that increase survival time up to 60 days (Smith 1982) . Viable poliovirus was recovered from ef¯uent spray-irrigated lettuce and radishes 23 days after inoculation Tierney et al. 1977) . Sadovski et al. (1978) isolated polioviruses from cucumbers grown in ef¯uentirrigated soil for a full 8 days after inoculation. Oron et al. (1995) investigated the transmission of poliovirus from subsurface drip-irrigated soil to tomato plant leaves and tomato fruits. Virus was not detected in the tomato fruits. However, a number of leaf samples were positive for poliovirus even though the virus was injected 10 cm below the surface of the soil. This result suggests that poliovirus can penetrate into plant tissue through the root system. The lack of viable poliovirus in the tomato fruits may be due to the presence of antiviral substances as witnessed by other authors. Chilled storage temperatures (2±8°C) typically retard respiration, senescence, product browning, moisture loss, and microbial growth in minimally processed fruits and vegetables, but may contribute to the survival and transmission of viruses to the human host. Speirs (1975b, 1976) described the potent antiviral properties of different fruit extracts at neutral pH, particularly strawberry. They found signi®cant differences in viral recovery on strawberries, cherries and peaches held in a humid atmosphere at 4°C. Recoveries of Coxsackievirus and echovirus were also greater than those of poliovirus and reovirus, although the authors did not offer an explanation for this result. Most of the aqueous fruit extracts and infusions demonstrated notable antiviral properties. Although the active compounds were not isolated, these agents could be phenolic in nature. In grapes, these chemicals are thought to be located primarily in the skin (Konowalchuk and Speirs 1977) . Fruits and vegetables are known to contain a vast array of antimicrobial substances, particularly organic acids, phenolic and sulphur compounds and small polypeptide proteins. Despite this, outbreaks of viral gastroenteritis and hepatitis A have been associated with fruits and fruit juices. In the absence of formal studies it could be inferred that the gastroenteritis and hepatitis A viruses are relatively resistant to these virucidal chemicals. In view of the increasing use of ready-to-eat vegetables sold in modi®ed atmosphere packaging (MAP), the survival of hepatitis A virus on lettuce in MAP, stored at room temperature and 4°C, has been investigated . Survival at 4°C was the same in MAP as under normal conditions of packaging. At room temperature viral survival was slightly better in MAP containing higher carbon dioxide levels. It was suggested that enhanced virus survival might be due to inhibition of ethylene by carbon dioxide, resulting in reduced physiological spoilage of vegetables such as lettuce and possibly less toxic effects on the virus. Studies have indicated that indigenous micro¯ora in the water environment are deleterious to survival of enteric viruses (Raphael et al. 1985) . These ®ndings highlight the importance of avoiding contamination of food items before packaging in MAP . Bardell (1997) studied the survival of herpes simplex virus type 1, suspended in saliva, on the skin of tomatoes and the upper surface of lettuce. Although storage times of only 1 h were studied, temperature was shown to have a signi®cant effect on virus titre. There was no loss of virus infectivity titre at 2°C compared to a 2-log reduction at room temperature (22±24°C). Although not an enteric virus and not a virus that comes to mind as a possible foodborne infection, herpes viruses could invade through the mucous membranes of the mouth. Most fruit and vegetable washing systems are designed to remove gross contamination such as dirt, insects, and foreign matter. However, they are reported to be less successful at removing microbial contaminants (Beuchat 1998; Seymour 1999) . Vigorous washing of fruits and vegetables with clean potable water typically reduces the number of micro-organisms by 10±100-fold (Beuchat 1998) and is often as effective as treatment with 100 mg l )1 chlorine, the current industry standard (Elphick 1998; Seymour 1999) . Raw materials are typically immersed in cooled sanitized water and then dewatered to remove surface moisture and fruit and vegetable juices from the product (Simons and Sanguansri 1997) . Product agitation is optimized by using water or air jets which enhance surface contact, carriage of product, and suspension of solids and vegetable debris (Simons and Sanguansri 1997) . There has been recent concern over the possible migration of bacterial pathogens into the core tissue of fruits and vegetables during washing. Zhang and Farber (1996) found that uptake of bacterial cells was associated with a negative temperature differential between the water and the product. However, the uptake of human viruses by fruits and vegetables under similar conditions has not been studied. Lodging or attachment of microorganisms in tissue crevices may protect cells from direct contact with disinfectants and consequently aid in their survival (Beuchat 1992) . Recent studies by Seo and Frank (1999) found that Escherichia coli O157:H7 could survive in the stomata and on cut edges of lettuce following chlorine treatment. Although there are no available data for viruses, cell surface structures are likely to offer some additional protection. Numerous authors have reported on the ef®cacy of disinfectants for the inactivation of readily culturable human viruses using standard suspension tests, but data for gastroenteritis viruses and hepatitis A virus are lacking. The authors of this review were unable to ®nd any data on the effectiveness of disinfectants and processing aids for the decontamination of enteric viruses on fruits and vegetables. The most commonly used sanitizers and processing aids for cleaning fruits and vegetables are chlorine, chlorine dioxide, organic acids and surfactants, while ozone is receiving renewed interest. The mechanism of action of these disinfectants on viruses and their interaction with plant materials is poorly understood and there are con¯icting reports on their ef®cacy. There are no positive lists of permitted processing aids in the United Kingdom or European Community, although an inventory has been produced by the Codex Alimentarius Commission (Codex Alimentarius General Requirements, volume 1 A, 2nd edition 1995. FAO/WHO ISBN 92±5-103762±0). Directive 98/8/EC of the European Parliament contains a list of biocidal products, which have been approved and authorized for use. Council Regulation (EEC) no. 2092/91 highlights the food additives, processing aids and other substances permitted for the organic production of agricultural products. The use of chlorine, for the treatment of organically grown fruits and vegetables, has recently been banned in the United Kingdom and the fresh produce industry is currently trying to ®nd viable and effective alternatives. Chlorine is the most widely used disinfectant for washing fresh produce because it is relatively cheap, easy to use and exhibits rapid microbiological action in aqueous solution (Elphick 1998) . The Food and Drug Administration (FDA) in the United States permits the use of chlorine as a disinfectant in wash, spray and¯ume waters in the raw fruit and vegetable industry (Garret 1992) . However, in certain EC countries, chlorine is not permitted as a wash water additive. Disinfectants such as chlorine and ozone have a strong af®nity for organic matter and are`used up' rapidly in wash tanks containing dirty produce. Therefore, for any washing system, it is important to monitor and control the level of disinfectant at all times, to ensure that it is optimal. It is also imperative to maintain chlorine disinfectants within a suitable pH range (Boyette et al. 1993) . Chlorine-based disinfectants are usually considered to be the most effective against enteric viruses. However, NLVs and hepatitis A virus appear to be relatively resistant to chlorine (Grabow et al. 1983; Peterson et al. 1983; Keswick et al. 1985) . NLVs are inactivated by 10 mg chlorine l )1 , which is the concentration used to treat a water supply after a contamination incident. In the United States a level of 5 mg chlorine l )1 with a contact time of 1 min is recommended for inactivation of hepatitis A virus. In recent studies (Doultree et al. 1999 ) feline calicivirus was shown to be surprisingly resistant to chlorine, requiring 1000 mg l )1 freshly reconstituted granular hypochlorite for complete inactivation. Clearly there is a need for further studies on disinfection of these persistent organisms. Chlorine dioxide is not as susceptible to pH changes or the presence of organic matter as chlorine (Simons and Sanguansri 1997) . Chlorine dioxide is unstable, must be generated on-site and can be explosive when concentrated. The oxidizing power of chlorine dioxide is reported to be about 2á5 times that of chlorine (Beuchat 1998) . However, Zhang and Farber (1996) found no signi®cant difference in decontamination ef®ciency between chlorine and chlorine dioxide. Several authors have reported the sensitivity of a range of animal viruses to chlorine dioxide (Harakeh 1987; Chen and Vaughn 1990) although there is no information for NLVs and hepatitis A virus. Organic acids can occur naturally in many fruits and vegetables and may retard the growth of some microorganisms and prevent the growth of others (Beuchat 1998) . Most of these acids behave primarily as fungistatic agents, while others are more effective at inhibiting bacterial growth. These include acetic, citric, succinic, malic, tartaric, benzoic, propanoic and sorbic acids. Due to recent changes in legislation, washes and sprays containing organic acids are becoming more popular for the processing of organically grown fruits and vegetables. A number of products are now commercially available. However, Scholtz et al. (1989) found that hepatitis A virus remained infectious for 90 min at pH 1. NLVs and hepatitis A virus survive exposure to acidity levels below pH 3, while rotavirus is inactivated below pH 3 and above pH 10 Palmer et al. 1977; Weiss and Clark 1987; Scholtz et al. 1989) . Viruses that infect via the gastrointestinal tract are acid stable since they have to survive the harsh low pH environment of the stomach. Organic acids are therefore unlikely to have a signi®cant effect on the viability of hepatitis A virus and NLVs during the typically short contact times used for washing fruits and vegetables (Seymour 1999) . Several authors have reported the action of surfactants (wetting agents) in combination with disinfectants (Adams et al. 1989; Zhang and Farber 1996) . However, these agents may reduce the antimicrobial effect of chlorine disinfectants and adversely affect product quality (Adams et al. 1989 ). Ozone is lethal to a wide variety of microorganisms, including enteric viruses (Finch and Fairbairn 1991) . It is a potent oxidizing agent, is very reactive and unstable, leaves no residues in water and naturally decomposes into ordinary oxygen. This absence of toxicity is one of its major advantages over chlorine disinfectants. Ozone has recently been approved as a disinfectant for food applications in the United States (Graham 1997) and industry suppliers are working to develop appropriate systems for fresh produce washing. Ozone is unstable, cannot be stored and must therefore be generated on-site. However, due to perceived safety problems and a lack of information on the ef®cacy of ozone, this technology has not yet been readily taken up in Europe. Although ozone can be used safely, it can cause irritation of the eyes, headache, dryness of the throat, and coughing at exposure levels in the range of 0á1±1á0 ppm (Boisrobert et al. 1998 ). The Occupational Safety and Health Administration (OSHA) has set the permissible exposure limit of workers to ozone at 0á1 ppm If ozone is to be used in aqueous or gaseous form it is essential that the air is monitored for ozone and that suitable control measures are in place to remove it. The control of foodborne viral infection was considered in the report of the Advisory Committee on the Microbiological Safety of Food (1998). Sewage pollution is a major factor in the contamination of food and water. This is particularly pertinent to fruits and vegetables that will not be cooked before consumption. Untreated or inadequately treated sewage discharged into natural waters can cause contamination of crops. Sewage sludge is applied to agricultural land, with the bene®t that useful plant nutrients are recycled to the soil. In April 2000, the Agricultural Development and Advisory Service (ADAS, UK) published the Safe Sludge Matrix (ADAS, 2000) . This document gives clear guidance on the minimum acceptable level of treatment for any sewage sludge applied to agricultural land and provides a framework to ensure microbiological safety. As from 31 December 1999 application of all untreated sludge on agricultural land used to grow food crops has been prohibited in the United Kingdom. Use on all agricultural land will be prohibited from the end of 2001. Untreated sludge is produced by either the primary settlement or secondary biological stages of sewage treatment. Further processing may be undertaken to produce treated sludge, resulting in improved stability and a reduction in health hazards and odour problems. (MAFF 1998) . Currently, treated sludge may be applied to land used for salad crops, but harvesting is not permitted for 30 months. Vegetables cannot be harvested for 12 months. A 10-month harvest interval is required if enhanced treated sludge is used. All applications must comply with the Sludge (Use in Agriculture) Regulations 1989 and DETR Code of Practice 1986. These controls may help to reduce the risks of microbiological contamination of fruits and vegetables in the UK, but still do not address the potential problem of imported produce from countries with different standards for organic fertilisers or irrigation water. The other major source of contamination is from infected people handling food. People with symptoms should be excluded from food handling. However, food-handlers with only very minimal symptoms have been implicated in transmission of viral gastroenteritis. Current recommendations state that food-handlers should be allowed to return to work 48 h after symptoms have ceased. (PHLS 1993) . These recommendations appear to work satisfactorily, but were based on the rapid decrease in virus excretion observed by electron microscopy. Using more sensitive PCR assays, NLVs can be detected for longer periods than electron microscopy and, in some instances, for up to a week after onset of symptoms. It is not clear if people shedding virus detectable by PCR are infectious, but recommendations on how long to exclude people from food-handling need to be kept under review. The main period of excretion for hepatitis A virus is before symptoms become apparent and therefore control is dif®cult. The wearing of disposable gloves is recommended if foods are to be manipulated by hand, but this does not prevent transfer of viruses to gloves by touching contaminated surfaces. If vomiting occurs, virus may be spread over a wide area in aerosol droplets. Uncovered food that is not to receive cooking should be discarded. The environment should be thoroughly cleaned, including work surfaces, sinks and door handles. Recent studies by the PHLS demonstrated the presence of virus on surfaces and materials that had been cleaned by recommended decontamination methods. This suggests that the current recommendations for the removal of NLVs from contaminated surfaces are inadequate (Barry-Murphy et al. 2000) . Cliver (1995) advised thorough cooking of virus-contaminated foods. However, ready-to-eat fruits and vegetables are unlikely to withstand such harsh treatment and may show deleterious changes in sensory quality. Larkin (1981) suggested a wash at 80°C for 2 min to ensure the microbiological safety of fresh produce. He concluded that this heat treatment does not affect the appearance and taste of most fruits and vegetables provided the food is eaten within 24 h. However, the majority of minimally processed fruits and vegetables require a shelf life in excess of 1 day and therefore this heating step is not applicable. Meticulous attention to good food handling practices and education is essential. There should be provision of adequate toilet and hand-washing facilities, not only in the catering and retail industry, but also for farm workers. There is an effective vaccine for hepatitis A and it has been suggested that food handlers should be vaccinated (Cliver 1997) . Epidemiological data currently suggest that food-handlers in the United Kingdom do not pose a signi®cantly greater risk of transmitting hepatitis A infec-tion than other people, and use of vaccine in this group may not be cost-effective. No vaccines have been developed for NLVs but research studies with NLV recombinant capsid antigens offer the potential for future development of vaccines. There are challenges, however, in designing effective vaccines in that ®rst, there are multiple types of NLVs and secondly, the mechanisms for inducing immunity to these agents is poorly understood (Estes et al. 2000) . Fresh produce contributes to the transmission of viral infections. There is a lack of information on the survival of viruses on fresh produce related to shelf life and types of packaging. Information is also lacking on the ef®ciency of current washing and decontamination processes for the removal of viruses. Studies are therefore required to provide this information for NLVs and hepatitis A virus in particular. There is a need for information on rotaviruses and astroviruses. Both these viruses have been implicated in foodborne and waterborne outbreaks in the United Kingdom, although only very infrequently. The role and extent of food or waterborne transmission needs to be more clearly de®ned for both these viruses. The infectivity of NLVs and hepatitis A virus is dif®cult to study in the laboratory. NLVs cannot be cultured in vitro and culture techniques for hepatitis A virus are timeconsuming. Other viruses that can be cultured readily have been used as models for these pathogens in a number of studies. Although only the use of speci®c human pathogenic viruses will give clear and unequivocal data on survival, inactivation and removal, this is not always safe and practical. Model systems using similar non-pathogenic human or mammalian viruses may be the most satisfactory alternative. For example, feline calicivirus has been used as a model system for NLVs in assessing the ef®cacy of commercially available disinfectants (Doultree et al. 1999) . Feline calicivirus was also used as a model for NLVs in another study on the heat treatment of shell®sh (Slomka and Appleton 1998) . This organism would appear to be a good candidate for virus studies on fresh produce. In order to undertake studies on the survival and removal of viruses, there is a need to develop better methods for inoculation and recovery of virus from a range of fresh produce items. There have been recent suggestions that faecal coliforms on fresh produce may be an indicator of the probable presence of enteric viruses. 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