Hepatitis E virus (HEV) is a non-enveloped single-stranded positive-sense RNA virus, belonging to the Hepeviridae family, resistant to environmental conditions, and transmitted by the consumption of contaminated water. This virus is responsible for both sporadic and epidemic outbreaks, leading to thousands of infections per year in several countries, and is thus considered an emerging disease in Europe and Asia. This study refers to a survey in Portugal during 2019, targeting the detection and eventual quantification of enteric viruses in surface and drinking water sources. Samples positive for HEV RNA were recurrently found by reverse transcription quantitative PCR (RT-qPCR), in both matrices. The infectivity of these samples was evaluated in cultured Vero E6 cells and RNA from putative viruses produced in cell cultures was subjected to RT-qPCR targeting HEV genomic RNA. Our results evidenced the existence of samples positive either for HEV RNA (77.8% in surface water and 66.7% in drinking water) or for infectious HEV (23.0% in surface water and 27.7% in drinking water). These results highlight the need of effective virological control of water for human consumption and activities.
Thirty-four concentrated samples from water collected in 2019, between January and August, and covering all sampling sites, were considered for infectivity assays in Vero E6 cultures. Only samples previously identified by RT-qPCR as positive for HEV RNA were selected, except when the related sample (collected on the same date in the associated water matrix) was positive.
Most cultures (19 in 32), each one inoculated with 0.5 mL of a water sample, did not develop cytopathic effects (CPEs) during the incubation period (15 days). Nevertheless, putative viral particles (pVPs) from this first passage were collected (supernatants of "infected" cultures) and used to "infect" new Vero E6 cultures. From these, 17 developed CPEs within 2–6 days post-inoculation; these second passage pVPs in the supernatants from cultures displaying, or not, CPEs, were collected, concentrated (for 6 h at 17,000× g, and 4 ⁰C) and subjected to RNA extraction and purification.
RNA extracted from pVPs produced as referred to above, was subjected to RT-qPCR, carried out with CeeramTools Hepatitis E kit (bioMérieux; Marcy-l’Etoile, France). HEV infectivity was confirmed by RT-qPCR positive results that met the quality criteria established by the mentioned kit.
From the samples evaluated, 18 were related samples from the river and WTP_R (eight from each) (Table 3), eight from the dam reservoir and WTP_D (four from each) (Table 4), and six were from the sampling point in the distribution network (Table 5). HEV infectivity was confirmed in samples from all matrices (globally 25%): 3/13 (23.0%) from surface water were positive (two from the river and one from the dam reservoir) as well as 5/18 (27.7%) from drinking water (three from WTP_R, one from WTP_D and one from the sampling point in the distribution network) (Table 3, Table 4 and Table 5).
From the samples evaluated, 18 were related samples from the river and WTP_R (eight from each) (Table 1), eight from the dam reservoir and WTP_D (four from each) (Table 2), and six were from the sampling point in the distribution network (Table 3). HEV infectivity was confirmed in samples from all matrices (globally 25%): 3/13 (23.0%) from surface water were positive (two from the river and one from the dam reservoir) as well as 5/18 (27.7%) from drinking water (three from WTP_R, one from WTP_D and one from the sampling point in the distribution network) (Table 1, Table 2 and Table 3).
Table 31.
Evaluation of related concentrated water samples (river and WTP_R) for the presence of HEV RNA and infectious particles.
Months | HEV RNA | HEV Reduction (%) after Treatment | HEV Infectivity (*) | ||||||||||||||
River | WTP_R | River | WTP_R |
February | 355.5 | 320.8 | 9.8 | Negative | Negative | ||||||||||||
February | 78.2 | 49.3 | 37 | Negative | Negative | ||||||||||||
March | 4,029.1 | 0 | 100 | Negative | Negative | ||||||||||||
April | 7,383.1 | 2,379.3 | 67.8 | Negative | Negative | ||||||||||||
May | 1,936.5 | 428 | 77.9 | Negative | Positive | ||||||||||||
June | 1,394.9 | 126 | 91 | Positive | Positive | ||||||||||||
July | 1,755 | 22 | 98.7 | Negative | Negative | ||||||||||||
August | 206.5 | 24.2 | 88.3 | Negative | Negative | ||||||||||||
August | 113.3 | 0 | 100 | Positive | Positive |
Table 42.
Evaluation of related concentrated water samples (dam reservoir and WTP_D) for the presence of HEV RNA and infectious particles.
Months | HEV RNA | HEV Reduction (%) after Treatment | HEV Infectivity (*) | ||||||||||||||
Dam Reservoir | WTP_D | Dam Reservoir | WTP_D |
February | 29.1 | 75.2 | NR | Negative | Negative | ||||||||||||
April | 109,687.5 | 5,617.1 | 94.9 | Negative | Negative | ||||||||||||
May | 2,412 | 0 | 100 | Negative | Negative | ||||||||||||
June | 0 | 58.7 | NR | Positive | Positive |
Table 53.
Evaluation of concentrated water samples from a sampling point in the distribution network, for the presence of HEV RNA and infectious particles.
Months |
HEV RNA |
HEV Infectivity (*) |
January |
46.9 |
Negative |
April |
8,926.6 |
Negative |
May |
1,473.5 |
Negative |
June |
133.3 |
Negative |
July |
221.4 |
Positive |
August |
186.6 |
Negative |
It was possible to determine that 1) most positive samples for HEV infectivity had also tested positive for HEV RNA (exceptions were WTP_R from August and dam reservoir from June) and 2) positive samples for HEV infectivity were frequently found in related samples, i.e., in river/WTP_R and dam reservoir/WTP_D sampled on the same date; one exception was found in river/WTP_R from May (only WTP_R was positive for infectious HEV) (Table 3, Table 4 and Table 5). Moreover, a relationship was not evidenced between the number of RNA copies detected in a water sample and its potential infectivity because, from the 11 samples presenting more than 1000 gc/L, only one (river from June) evidenced infectivity; values of gc/L between 0 and 428 had been found in all the others able to produce infectious HEV in Vero E6 cells.
It was possible to determine that 1) most positive samples for HEV infectivity had also tested positive for HEV RNA (exceptions were WTP_R from August and dam reservoir from June) and 2) positive samples for HEV infectivity were frequently found in related samples, i.e., in river/WTP_R and dam reservoir/WTP_D sampled on the same date; one exception was found in river/WTP_R from May (only WTP_R was positive for infectious HEV) (Table 1, Table 2 and Table 3). Moreover, a relationship was not evidenced between the number of RNA copies detected in a water sample and its potential infectivity because, from the 11 samples presenting more than 1000 gc/L, only one (river from June) evidenced infectivity; values of gc/L between 0 and 428 had been found in all the others able to produce infectious HEV in Vero E6 cells.
This study followed a complex approach to assess the presence of HEV, starting from high volumes of water (EPA Method 1615 of the United States Environmental Protection Agency [41][1]) and combining, in the same procedure, the possibility to detect viral RNA by RT-qPCR as well as evaluate infectivity. The use of cell cultures overcame the limitation of evaluations based only on RT-qPCR. In fact, RT-qPCR has been increasingly used to detect enteric viruses in water and food samples, with high specificity/sensitivity and the possibility of obtaining results in less than four hours [3,48,49][2][3][4]. However, this methodology does not allow assessing the infectivity associated with the viral genomes detected in the reaction [3,25,40][2][5][6]. Beyond the confirmation of viral genomes, it is crucial in the evaluation of risks to public health, to determine whether they correspond to viral particles with the ability to infect human cells [48,49,50,51][3][4][7][8]. Despite being expensive and time consuming, relying on cell cultures is the most used standard method for assessing the infectivity of viral particles [3,6,52][2][9][10].
This one-year survey evaluated the presence of HEV in concentrated samples from two bodies of water (a river and a dam reservoir) and from the drinking water sampled on their water treatment plants (WTP_R and WTP_D, respectively) at the end of the treatment process. A mammal cell line (Vero E6) derived from African green monkey (Cercopithecus aethiops) kidney was used, for the first time, to assay the potential infectivity of water samples where HEV RNA had been detected by RT-qPCR. The rationale for the utilization of this cell line was its capability to replicate many different viruses [46,53], also taking into account that HEV has a large host range [12,15]. This approach effectively resulted in the detection of infectious HEV in several samples, by more or less evident induction of CPEs in cultured cells and subsequent confirmation of HEV replication through RT-qPCR to RNA extracted from extracellular putative viral particles. Our results agree with a recent study [54] demonstrating that a wild-derived HEV strain replicated in Vero cells, the cell line from which Vero E6 was derived (46).
This one-year survey evaluated the presence of HEV in concentrated samples from two bodies of water (a river and a dam reservoir) and from the drinking water sampled on their water treatment plants (WTP_R and WTP_D, respectively) at the end of the treatment process. A mammal cell line (Vero E6) derived from African green monkey (Cercopithecus aethiops) kidney was used, for the first time, to assay the potential infectivity of water samples where HEV RNA had been detected by RT-qPCR. The rationale for the utilization of this cell line was its capability to replicate many different viruses [11][12], also taking into account that HEV has a large host range [13][14]. This approach effectively resulted in the detection of infectious HEV in several samples, by more or less evident induction of CPEs in cultured cells and subsequent confirmation of HEV replication through RT-qPCR to RNA extracted from extracellular putative viral particles. Our results agree with a recent study [15] demonstrating that a wild-derived HEV strain replicated in Vero cells, the cell line from which Vero E6 was derived (46).
HEV RNA was detected in concentrated samples from the two bodies of water and from drinking water (Entry _HEV genomic RNA detection), and in an infectious state in several of these samples.
Although the peak HEV RNA concentration was found in April, both in the river and in the dam reservoir, infectious HEV was only detected in June, when HEV RNA concentrations were high in the river (>1000 gc/L) and zero in the dam reservoir, suggesting inexistence of a direct association between the number of detected RNA copies and potential infectivity.
Out of the 18 concentrated drinking water samples selected for evaluation of HEV infectivity, five were positive. Drinking water from WTP_R presented the highest number of infectious samples (three), followed by WTP_D and the water from the point in the distribution network, both with only one infectious sample. Infectious HEV was detected in samples collected between May and August, after the peak of HEV RNA copies, as also observed in the bodies of water. Once again, no clear relationship was found between infectivity and number of HEV RNA copies detected per liter of sampled water.
Even though most of the results did not evidence contradictory aspects, a few should be discussed. One unexpected result was the infectivity of two samples (one from the dam reservoir and the other from WTP_R) originally identified as negative for HEV RNA. This may be explained by eventual mishaps during original RNA extraction procedures and emphasizes the relevance of evaluating results achieved by independent approaches. The detection of an infectious drinking water sample (WTP_R) was also unexpected, when the sampled water from its source (river) did not show infectivity. This may be explained by the large differences in the water volumes subjected to sampling: 1300 L in WTP_R and 152 L in the river. It should be noted that the positive result of infectivity in WTP_R means that HEV was also present in the river to such an extent that infectivity remained after treatment.
The results showing the presence of infectious HEV in concentrated samples of drinking water evidence the need to further investigate eventual threats to human health. It is worth noting that Vero E6 cultures were inoculated with 0.5 mL of concentrated (40×, in average) drinking water samples, equivalent to approximately 17.5 L of the sampled water (from a total of 1400 L, in average), while healthy individuals drink approximately two liters of water each day [60].
The results showing the presence of infectious HEV in concentrated samples of drinking water evidence the need to further investigate eventual threats to human health. It is worth noting that Vero E6 cultures were inoculated with 0.5 mL of concentrated (40×, in average) drinking water samples, equivalent to approximately 17.5 L of the sampled water (from a total of 1400 L, in average), while healthy individuals drink approximately two liters of water each day [16].
Finally, climate change will certainly increase the frequency of pathogens in water systems worldwide, whether due to the occurrence of floods, sewage contamination or the scarcity of safe drinking water sources [3]. In this context and considering the results obtained in this study, monitoring the presence of HEV and other viruses in water supply and distribution systems is strongly advisable. Similar approaches should be conducted in the future, increasing the sampling effort and implementing the application of the quantitative microbial risk assessment (QMRA) [69].
Below are references that still need be subjected to selection for this entry of Encyclopedia
ISO. International Standard-Microbiology of the Food Chain—Horizontal Method for Determination of Hepatitis A Virus and Norovirus; ISO Copyright Office: Geneva, Switzerland, 2017. [Google Scholar]
Teixeira, P.; Costa, S.; Brown, B.; Silva, S.; Rodrigues, R.; Valério, E. Quantitative PCR detection of enteric viruses in wastewater and environmental water sources by the Lisbon municipality: A case study. Water 2020, 12, 544. [Google Scholar] [CrossRef]
O’Brien, E.; Nakyazze, J.; Wu, H.; Kiwanuka, N.; Cunningham, W.; Kaneene, J.B.; Xagoraraki, I. Viral diversity and abundance in polluted waters in Kampala, Uganda. Water Res. 2017, 127, 41–49. [Google Scholar] [CrossRef]
Silva, A.M.; Vieira, H.; Martins, N.; Granja, A.T.S.; Vale, M.J.; Vale, F.F. Viral and bacterial contamination in recreational waters: A case study in the Lisbon bay area. J. Appl. Microbiol. 2009, 108, 1023–1031. [Google Scholar] [CrossRef] [PubMed]
Ammerman, N.; Beier-Sexton, M.; Azad, A. Growth and maintenance of Vero cell lines. Curr. Protoc. Microbiol. 2008, 1–10. [Google Scholar] [CrossRef] [PubMed]
Lee, J.H.; Lee, G.C.; Kim, J.I.; Yi, H.A.; Lee, C.H. Development of a new cell culture-based method and optimized protocol for the detection of enteric viruses. J. Virol. Methods 2013, 191, 16–23. [Google Scholar] [CrossRef]
Haramoto, E.; Kitajima, M.; Hata, A.; Torrey, J.R.; Masago, Y.; Sano, D.; Katayama, H. A review on recent progress in the detection methods and prevalence of human enteric viruses in water. Water Res. 2018, 135, 168–186. [Google Scholar] [CrossRef] [PubMed]
Rodríguez, R.A.; Pepper, I.L.; Gerba, C.P. Application of PCR-based methods to assess the infectivity of enteric viruses in environmental samples. Appl. Environ. Microbiol. 2009, 75, 297–307. [Google Scholar] [CrossRef]
Leifels, M.; Hamza, I.A.; Krieger, M.; Wilhelm, M.; Mackowiak, M.; Jurzik, L. From Lab to Lake – Evaluation of Current Molecular Methods for the Detection of Infectious Enteric Viruses in Complex Water Matrices in an Urban Area. PLoS ONE 2016, 11, 1–16. [Google Scholar] [CrossRef]
Hamza, I.A.; Jurzik, L.; Überla, K.; Wilhelm, M. Methods to detect infectious human enteric viruses in environmental water samples. Int. J. Hyg. Environ. Health 2011, 214, 424–436. [Google Scholar] [CrossRef]
Dilnessa, T.; Zeleke, H. Cell Culture, Cytopathic Effect and Immunofluorescence Diagnosis of Viral Infection. J. Microbiol. Mod. Tech. 2017, 2, 1–8. [Google Scholar] [CrossRef]
Format, P.; Properties, C.; Level, B.; Conditions, S. VERO C1008 [Vero 76, Clone E6, Vero E6] (ATCC®CRL-1586TM). Available online: https://www.lgcstandards-atcc.org/Products/All/CRL-1586.aspx?geo_country=pt (accessed on 1 April 2020).
Grigas, J.; Simkute, E.; Simanavicius, M.; Pautienius, A.; Streimikyte-Mockeliune, Z.; Razukevicius, D.; Stankevicius, A. Hepatitis e genotype 3 virus isolate from wild boar is capable of replication in non-human primate and swine kidney cells and mouse neuroblastoma cells. BMC Vet. Res. 2020, 16, 1–11. [Google Scholar] [CrossRef]
Instituto Português do Mar e da Atmosfera. Resumo Climatológico Preliminar 1 a 29 Abril de 2019. Available online: https://www.ipma.pt/resources.www/docs/im.publicacoes/edicoes.online/20190503/IsNqBQXrKBtUkblVoGQA/cli_20190401_20190430_pcl_mm_co_pt.pdf (accessed on 25 March 2020).
Jiang, S.C.; Chu, W. PCR detection of pathogenic viruses in southern California urban rivers. J. Appl. Microbiol. 2004, 97, 17–28. [Google Scholar] [CrossRef]
Pordata-Valor da Produção Agrícola: Total e Por Tipo. Available online: https://www.pordata.pt/Municipios/Valor+da+produção+agrícola+total+e+por+tipo-956 (accessed on 26 March 2020).
Dalton, H.R.; Seghatchian, J. Hepatitis E virus: Emerging from the shadows in developed countries. Transfus. Apher. Sci. 2016, 55, 271–274. [Google Scholar] [CrossRef] [PubMed]
Martin-latil, S.; Hennechart-collette, C.; Delannoy, S.; Guillier, L. Quantification of Hepatitis E Virus in Naturally-Contaminated Pig Liver Products. Front. Microbiol. 2016, 7, 1–10. [Google Scholar] [CrossRef] [PubMed]
Tsindos, S. What drove us to drink 2 litres of water a day? Aust. N. Z. J. Public Health 2012, 36, 205–207. [Google Scholar] [CrossRef] [PubMed]
Farkas, K.; Cooper, D.M.; McDonald, J.E.; Malham, S.K.; de Rougemont, A.; Jones, D.L. Seasonal and spatial dynamics of enteric viruses in wastewater and in riverine and estuarine receiving waters. Sci. Total Environ. 2018, 634, 1174–1183. [Google Scholar] [CrossRef]
Haramoto, E.; Katayama, H.; Oguma, K.; Ohgaki, S. Application of cation-coated filter method to detection of noroviruses, enteroviruses, adenoviruses, and torque teno viruses in the Tamagawa River in Japan. Appl. Environ. Microbiol. 2005, 71, 2403–2411. [Google Scholar] [CrossRef]
Da Silva, A.K.; Le Saux, J.C.; Parnaudeau, S.; Pommepuy, M.; Elimelech, M.; Le Guyader, F.S. Evaluation of removal of noroviruses during wastewater treatment, using real-time reverse transcription-PCR: Different behaviors of genogroups I and II. Appl. Environ. Microbiol. 2007, 73, 7891–7897. [Google Scholar] [CrossRef]
Hennechart-Collette, C.; Martin-Latil, S.; Guillier, L.; Perelle, S. Determination of which virus to use as a process control when testing for the presence of hepatitis a virus and norovirus in food and water. Int. J. Food Microbiol. 2015, 202, 57–65. [Google Scholar] [CrossRef]
Girones, R.; Carratalà, A.; Calgua, B.; Calvo, M.; Rodriguez-Manzano, J.; Emerson, S. Chlorine inactivation of hepatitis e virus and human adenovirus 2 in water. J. Water Health 2014, 12, 436–442. [Google Scholar] [CrossRef]
Guerrero-Latorre, L.; Gonzales-Gustavson, E.; Hundesa, A.; Sommer, R.; Rosina, G. UV disinfection and flocculation-chlorination sachets to reduce hepatitis E virus in drinking water. Int. J. Hyg. Environ. Health 2016, 219, 405–411. [Google Scholar] [CrossRef]
Shin, E.; Kim, J.S.; Oh, K.H.; Oh, S.S.; Kwon, M.J.; Kim, S.; Park, J.; Kwak, H.S.; Chung, G.T.; Kim, C.J.; et al. A waterborne outbreak involving hepatitis A virus genotype IA at a residential facility in the Republic of Korea in 2015. J. Clin. Virol. 2017, 94, 63–66. [Google Scholar] [CrossRef]
Lim, M.Y.; Kim, J.M.; Lee, J.E.; Ko, G. Characterization of ozone disinfection of murine norovirus. Appl. Environ. Microbiol. 2010, 76, 1120–1124. [Google Scholar] [CrossRef] [PubMed]
WHO. Quantitative Microbial Risk Assessment: Application for Water Safety Management. WHO Press: Geneva, Switzerland, 2016; pp. 1–187. [Google Scholar]
The article has been published on 10.3390/microorganisms8050761
Finally, climate change will certainly increase the frequency of pathogens in water systems worldwide, whether due to the occurrence of floods, sewage contamination or the scarcity of safe drinking water sources [2]. In this context and considering the results obtained in this study, monitoring the presence of HEV and other viruses in water supply and distribution systems is strongly advisable. Similar approaches should be conducted in the future, increasing the sampling effort and implementing the application of the quantitative microbial risk assessment (QMRA) [17].