Article Information

Lorena da Graça Pedrosa de Macena^1*, Carmen Baur Vieira², Adriana Gonçalves Maranhão¹, Fernando César Ferreira¹, Elba Regina Sampaio Lemos³, Marize Pereira Miagostovich¹

¹Laboratory of Comparative and Environmental Virology, Oswaldo Cruz Institute, Oswaldo Cruz Foundation, Rio de Janeiro, RJ 21040-360, Brazil

²Department of Microbiology and Parasitology, Biomedical Institute, Fluminense Federal, University (UFF), Niterói, RJ 24210-130, Brazil

³Laboratory of Hantaviruses and Rickettsiosis, Oswaldo Cruz Institute, Oswaldo Cruz Foundation, Rio de Janeiro, RJ 21040-360, Brazil

^*Corresponding Author: Lorena da Graça Pedrosa de Macena, Laboratory of Comparative and Environmental Virology, Oswaldo Cruz Institute, Oswaldo, Cruz Foundation, Rio de Janeiro, RJ 21040-360, Brazil

Received: 29 September 2021; Accepted: 06 October 2021; Published: 06 November 2021

Citation:

Lorena da Graça Pedrosa de Macena, Carmen Baur Vieira, Adriana Gonçalves Maranhão, Fernando César Ferreira, Elba Regina Sampaio Lemos, Marize Pereira Miagostovich. Genetic Diversity and Quantification of Human Adenoviruses and JC Polyomaviruses in Wastewater Samples. International Journal of Plant, Animal and Environmental Sciences 11 (2021): 614-626.

Abstract

Keywords

Genetic diversity; HAdV; JCPyV; Wastewater-based monitoring

Article Details

1. Introduction

The investigation of pathogens in untreated sewage represents an advantageous tool to determine the epidemiology and prevalence of infectious agents at the population level in a specific geographic region [1]. This approach, allows the assessment of the circulation of endemic, emerging and re-emerging pathogens shedding by infected individuals [2]. In this context, the wastewater-based monitoring has been useful for research, prevention, treatment and control of known and even unknown infectious diseases, complementing epidemiological surveillance and guiding public health action [3]. Several studies have been used this approach to monitor virus assessing virus circulation including those excreted by symptomatic and asymptomatic infected individuals [4-7]. Human adenoviruses (HAdV) and JC human polyomaviruses (JCPyV) commonly found in high concentrations of wastewater around the world [8], are both DNA viruses presenting specificity with the human host stability, persistence and wide distribution in different environmental matrices, being detected in sewage samples without seasonality [9, 10].

HAdV belong to the Adenoviridae family, genus Mastadenovirus. They are non- enveloped viruses, with a capsid of icosahedral symmetry, 90nm in diameter and double- stranded DNA of approximately 35 kb [11]. Currently, more than 49 HAdV serotypes, grouped into six species (A–F) are described based on neutralizing antibody assays and the ability to agglutinate red blood cells [12]. Adenoviruses A, F and G are related to gastrointestinal infections, B and C to respiratory infections and D to keratoconjunctivitis [13]. They can establish latent and persistent infections, with the virus being excreted for weeks after infection and regardless of the primary site of infection [14]. In addition, enteric (HAdV-F40 and 41) and non-enteric HAdV serotypes replicate in the intestine and are potentially capable of being transmitted by contaminated water [9].

JCPyV belong to the Poliomaviridae family, genus Poliomavirus, and together with the twelve virus (BKPyV, WUPyV, KIPyV, MCPyV, HPyV6, HPyV7, TSPyV, HPyV9, HPyV10, STLPyV, HPyV12 and HPyV13) constitute the polyomavirus that infects humans [15]. They are non-enveloped viruses, measuring about 40-45 nm in diameter, containing a genome composed of double-stranded circular DNA of approximately 5.1 kb [16]. Eight genotypes (JCPyV 1 to 8) and several JCPyV subtypes are described until the present study [17]. These viruses are prevalent in more than 80% of the world population, detected in environmental samples and excreted in urine, indicating the possibility of transmission from person to person and / or urine-fecal-oral in contact with contaminated surfaces, food and water [18]. Genotypic distribution seems to follow a defined pattern, determined by the excretion of a specific genotype according to the ethnic origin of each individual and not by the geographic region in which that individual is found [19, 20]. JCPyV commonly causes persistent subclinical renal lesions, but can infect secondary sites such as bone marrow, lymphoid tissue, and brain and establish latent infection [21]. Viral reactivation can occur in cases of profound impairment of cellular immunity and progressive multifocal leukoencephalopathy (PML), a rare and fatal disease, manifests itself causing multiple foci of demyelination in the brain [18]. This study aimed to assess the genetic diversity and concentration of HAdV and JCPyV in raw samples from domestic and hospital sewage in the during the Olympic Games, due to the expected large influx of people during this mass gathering event.

2. Materials and Methods

2.1 Study area and sampling site

This study was carried out in Barra da Tijuca, located on the west coast of the city of Rio de Janeiro (Brazil), from August to December 2016. Wastewater samples were collected from domestic (Residential village) and hospital (Public Health Units) sewage pipes and stored at 4°C until further processing. Residential Village consists of seven condominiums, 31 buildings and 3,604 apartments [22, 23]. General and Maternity Hospital are important Regional Emergency Centers in the West Zone of Rio de Janeiro and offer free clinical, surgical, pediatrics and obstetric care to residents and tourists [24-26].

2.2 Concentration method and virus quantification, and nucleic acids extraction and qPCR for HAdV and JCPyV

Sewage samples (42 mL) were concentrated using skim milk elution and flocculation method as previously described [27]. Briefly, before flocculation, sewage samples were previously treated with 0.25 N glycine buffer, pH 9.5 (1:2, v/v), stirred for 30min on ice, centrifuged at 8000 ×g for 30min at 4°C and added skimmed-milk solution (0.01%, w/v) to the supernatant adjusted to pH 3.5. The samples were flocculated with agitation for 8h at room temperature and the skimmed milk flakes were sedimented by centrifugation at 8000 ×g for 30min at 4°C. Finally, the pellet was resuspended with 1mL of phosphate buffer (pH 7.5).

Commercial QIAmp viral RNA Mini kit (Qiagen™, Valencia, USA) was used for nucleic acids extraction using Automatic QIAcube System according to the manufacturer’s instructions. The negative control composed of DNase/RNase-free water and positive controls were also included in each assay. Quantitative polymerase chain reaction (qPCR) was performed for quantification of HAdV and JCPyV as previously described [28, 29], using the ABI PRISM 7500 Real Time TaqMan System and TaqMan Universal Master Mix II (Applied Biosystems™, Foster City, CA).

Negative and positive (faecal suspension) controls, as well as NTC, were also included in all procedures. All samples were tested in duplicate using undiluted and 1:10 diluted nucleic acid to assess qPCR inhibitions. Samples that showed signs crossing the threshold line up to Ct ≤ 38 in both replicates and with a characteristic sigmoidal curve were considered positive. The gBlock Gene (Integrated DNA Technologies ™, Coralville, Iowa, USA) was used as standard curves for each virus analysed. Standard curves were serially diluted from 1x107 to 1x100 genomic copies per reaction and showed average values of -3.563 and -3.460 of slope, of 0.998 and 0.999 of square regression coefficient (r²) and 91% and 95% of reaction efficiencies for HAdV and JCPyV qPCRs, respectively.

2.3 Molecular characterization of HAdV and JCPyV

Conventional PCR assays were used for gene amplification of HAdV and JCPyV qPCR positive samples. HAdV positive samples were amplified in the coding region of the hexon gene         using the two oligonucleotide primer pairs hex1deg/hex2deg (301pb)     and hex1deg/nehex4deg (245pb) adapted from [30]. The intergenic region (VP1 and large T) was amplified in JCPyV positive samples using two oligonucleotide primer pairs EP1A/EP1A (737bp) and P1A/P2A (668bp), according to Boffil-Mas and Girones [31].

Amplicons were visualized using gel electrophoresis on a 1.5% agarose gel (UltraPure™ Agarose, Life Technologies™, Carlsbad, CA, USA) with 10mg/mL of UltraPure™ Ethidium Bromide (Life Technologies™, Carlsbad, CA, USA). Amplified DNA fragments were sequenced by the Sanger method using the ABI Prism Big Dye Terminator Cycle Sequencing Ready Reaction Kit 1 (version 3.1) and the ABI Prism 3730 Genetic Analyzer (Applied Biosystems ™, Foster City, CA, USA). Nucleotide sequences were edited and aligned using the Clustal W method in Bio Edit Software 7.2.6 [32]. Sequences of HAdV and JCPyV, with size of 224bp and 624bp respectively, were compared with those available in the National Centre for Biotechnology Information (GenBank, http://www.ncbi.nlm.nih.gov/) database using the BLAST (Basic Local Alignment Search Tool).

Using the MEGA X [33], the evolutionary history was inferred using the Maximum Likelihood method to analyse sequences of both viruses. Kimura 2-parameter [34] and Tamura 3-parameter [35] were the models used for the construction of the phylogenetic HAdV and JCPyV trees, respectively. Initial trees for the heuristic search were obtained by applying the Neighbour-Joining method to a matrix of pairwise distances estimated using the Maximum Composite Likelihood (MCL) approach. Confidence values of the internal nodes were calculated by performing bootstrap analyses with 2,000 replicates. The nucleotide sequence data reported in this study was submitted to the GenBank and received the accession numbers for HAdV (MT250569 - MT250586) and JCPyV (MT253712 - MT253728).

3. Results

HAdV and JCPyV were detected in 95% (18/19) of the samples, with minimum and maximum concentrations of 1.7x10³ to 9.2x10⁶ copies of genomics/litter (GC/L) and 2.8x10⁴ to 1.3x10⁸ GC/L, respectively. The results of the average concentration in all sewers showed an average load of JCPyV with 1 log more than HAdV. The logarithmic mean concentration remained stable when comparing the quantification of HAdV in domestic and hospital sewage.

In contrast, JCPyV presented 10⁷ GC/L in hospital sewage and a concentration of approximately 10⁶ GC/L in domestic sewage.

Nucleotide sequencing characterization detected three HAdV species (B, D and F), totalizing eight serotypes (HAdV B, D, D10, D17, D19, D22, F40 and F41). HAdV-F (44%) and HAdV-D (33%) were the species prevalent, being HAdV F species prevalent in hospital sewage samples while the HAdV B and D species were prevalent in domestic sewage. Regarding to JCPyV nucleotide analysis, were characterized seven genotypes and nine subtypes (JCPyV-1B, 2A, 3A, 3B, 4, 6, 7A, 8A and 8B) in 18 JCPyV positive raw sewage samples (Table 1, Figure 1 and 2).

*GC/L= genome copies/Litre; SD=standard deviation

Table 1: Detection, quantification, and serotypes/genotypes of human adenovirus (HAdV) and JC polyomavirus (JCPyV) according to collection sampling sites.

Figure 1: Human adenovirus phylogenetic tree based on hexon region gene (224 base pair) showing eighteen strains found in raw sewage from Residential Village (triangle), General Hospital (circle) and Maternity Hospital (square). Maximum Likelihood method and Kimura 2-parameter model was used with 2,000 bootstrap replicates.

Figure 2: JC human polyomavirus phylogenetic tree based on intergenic region gene (624 base pair) showing seventeen strains in raw sewage found in raw sewage from Residential Village (triangle), General Hospital (circle) and Maternity Hospital (square). Maximum Likelihood method and Tamura 3-parameter model was used with 2,000 bootstrap replicates.

4. Discussion

Wastewater-based monitoring approach, even in a short period as conducted in this study, was successful for describing the occurrence of HAdV-22 and 17 and, JCPyV-7 and -8 genotypes for the first time in the country. The prevalence and quantification of both HAdV and JCPyV observed are in agreement with the findings obtained in samples of domestic and hospital sewage throughout the world [36-39]. The viral load of JCPyV, about one log higher than HAdV, was higher than that observed in previous studies carried out by our group in raw sewage (average concentration of 2.55x10⁴ GC/L) from an urban wastewater treatment plant (WTTP) in Rio de Janeiro between 2009 and 2010 [40]. The small number of samples collected is a limiting factor in this study, not allowing a comparative assessment between sewage from different sources. According Arkhipova et al. (2018) the fact that the samples were collected during a mass event, where a large influx of individuals is expected could explain not only the possibility of an eventual introduction of a new virus in the region as well as a greater contribution of population density and transmission of infectious diseases, especially of waterborne etiological agents [41]. In this context, it is possible that the increase in the mean concentration of observed viruses, the profile of viral diversity and the pathogen-host dynamics circulating in sewage may have been influenced by the mass event [41]. Once the study area evaluated, the Barra da Tijuca neighborhood on the west coast of the city of Rio de Janeiro, housed the athletes in the Olympic Village and received 300,000 people at the Olympic Park, in addition to receiving up to 292,000 visitors at the sites of Live streaming of the Games [42].

Look upon molecular viral characterization, it was observed a similar diversity of HAdV species and serotypes between samples previously collected in the region as raw hospital sewage samples [38] and brackish from a Lagoon System samples [43] collected in 2008 and 2016, respectively. Except by HAdV-D17 and HAVdV-22, first described in the country in this study. HAdV-17 was described in sewage and mussel samples in South Africa [44], while HAdV-D22 detected in WWTP samples in Canada [45]. Both serotypes of the HAdV-D species are reported to cause outbreaks of epidemic keratoconjunctivitis (EKC) in humans on the Asian continent [46, 47].

The intraspecies co-circulation capacity of HAdV in the population and its spread in the environment was previously demonstrated [48]. Thus, depending on the number of viral infections and the immunity of the population, it is possible that one species is more detectable than another [49]. Recently, sequencing of the hypervariable regions (HVR) of the hexon gene and the long fibre gene of HAdV demonstrated the occurrence of variations in F-species circulating in India [50]. Unfortunately, the hexon region sequenced in this study did not allow us to assess the occurrence of these variants of circulating F strains. Regarding JCPyV diversity, it is remarkable the first detection of JCPyV-7 and -8 genotypes during the Olympic Games, specifically because JCPyV is used as an anthropological biomarker [51]. The detection of JCPyV-7 and -8 genotypes evidenced the presence of Asian, African, Melanesian and Polynesian ethnic and geographic ancestry foreigners. JCPyV-7A (SC strain) in Brazil was notable as it is generally identified in ethnic ancestors in East and Southeast Asia and West Africa, while JCPyV-8 (subtypes 8A and 8B) come from ancestral peoples of Melanesia (Papua New Guinea) and Polynesia [17].

Among the other genotypes detected and representatives of the Old World [52], the European (JCPyV-1 and -4), the African (JCPyV-3 and -6) and the Asian (JCPyV-2A) were characterized in the domestic and hospital sewage from different sources evaluated. These genotypes have been reported in the North, Northeast, Southeast and South of Brazil since 2000, in cerebrospinal fluid, urine from healthy kidney transplant patients and from patients with PML, as well as in wastewater from the WWTP [40, 51, 53-56]. Overall, of the eight JCPyV genotypes already described in the literature, only JCPyV-5 was not found in all the evaluated sewage samples [17]. Previously, Fumian et al (2010) demonstrated greater circulation of JCPyV-3 (Af2) genotypes, of African and Asian origin, in Rio de Janeiro [57].

5. Conclusion

The success in demonstrating populational-level infection change by detecting a new etiological agent in a given geographic region demonstrates the importance of environmental surveillance as a non-invasive, complementary approach that can support epidemiological studies.

Acknowledgements

The authors thank technical and field staff Márcia Maria Araújo Pimenta, Sérgio de Silva e Mouta Júnior (Oswaldo Cruz Foundation, RJ, Brazil), Fábio Valadão Araújo and Arnaldo Levy Lassance Cunha (Rio de Janeiro City Hall employees) for assisting in field collection and samples processing. PDTIS DNA Sequence Platform staff at FIOCRUZ for technical support in sequencing reactions.

Funding

This work was funded by Instituto Oswaldo Cruz (PAEF), Fundação de Amparo à Pesquisa do Rio de Janeiro (Faperj-E-26/202.821/2018), Conselho de Desenvolvimento Científico e Tecnológico (CNPq-Universal-406414/2016-5), Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - Brasil (CAPES) - Finance Code 001.

This research study is under the scope of the activities of the Oswaldo Cruz Foundation (FIOCRUZ) as a Collaborating Centre of PAHO/WHO of Public and Environmental Health.

Conflict of Interest

The authors declare that they have no conflict of interest.

Authors’ Contributions

All authors critically reviewed the article for important intellectual content and approved all components of the final version. Pedrosa de Macena, L.G. contributed to the execution of the development and design of the methodology, data visualization and writing of the original sketch. Vieira, C.B. conceptualized and designed the methodology. Maranhão, A.G. and Ferreira, F.C. contributed to the realization and investigation of molecular analyses and field collection. Lemos, E.R.S. contributed resources, supervision and funding acquisition. Miagostovich, M.P. contributed to writing - review and editing, visualization, supervision, project administration and funding acquisition.

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