Human adenoviruses (HAdV) are non-enveloped viruses with an icosahedral capsid and a linear double-stranded DNA genome. These viruses belong to the family Adenoviridae and genus Mastadenovirus. An important property of the HAdV is that it is non-enveloped making it highly resistant to detergents and harsh environmental conditions. This virus is grouped in seven species (A-G) with more than 88 genotypes. These seven species are associated with several diseases, such as, respiratory infections, keratoconjunctivitis, urinary infections, hepatitis and gastrointestinal infections. The HAdV is one of the etiological causes of acute gastroenteritis, mainly caused by HAdV-F40 and HAdV-F41. The virus can be transmitted via the faecal-oral route, inhalation of respiratory droplets and direct contact with contaminated environments. The virus is known to be ubiquitous in environments where human contamination is likely to occur such as wastewater treatment plants. These human contaminations could occur through contaminated secretion and excretions within aqueous environments. There is currently a limited amount of information on the HAdV in water Molecular characterisation of human adenoviruses from environmental environments, particularly in Tshwane, Gauteng. Therefore, the aim of the study was to investigate the presence and genotypes of human adenovirus in environmental samples namely raw sewage and treated effluent, using molecular methods. For genotypic characterisation, Sanger sequencing was used on amplicons from 12 HAdV positive samples and next generation sequencing were used on all the amplicons from HAdV positive samples. A total of 150 environmental samples (75 raw sewage and 75 effluent) were collected from two wastewater treatment plants in Tshwane over the study period of 18 months. These environmental samples comprised of 1 L raw sewage and 10 L treated effluent samples. The primary viral recovery for the 1 L raw sewage and 10 L treated effluent samples were performed using skimmed milk flocculation procedure and glass wool adsorption elution technique, respectively. For secondary viral recovery, both environmental samples were subjected to polyethylene glycol/sodium chloride precipitation. Manual extraction was used to extract the nucleic acids from the virus concentrate with mengovirus (MV) used as an extraction control. For the quantification of HAdV, standard curves prepared from known dilutions of HAdV and MV were used. Human adenovirus was detected in 140/150 (93%) of the environmental samples comprising of 69/75 (92%) being raw sewage and 71/75 (95%) being effluent samples. The HAdV concentrations detected in wastewater treatment plant 1 (WWTP 1) ranged from 1.38x105 gc/L to 4.50 x 109 gc/L for raw sewage and 5.08x103 gc/l to 4.30x108 gc/L for effluent. The HAdV concentrations detected in WWTP 2 ranged from 6.84x104 gc/L to 1.69x1012 gc/L for raw sewage and 5.27x103 gc/L to 1.16x108 gc/L for effluent. The HAdV hexon amplification success rate from the nucleic acids was 43/140 (31%). Eighteen HAdV genotypes were successfully characterised using Sanger sequencing. The HAdV-D was the most predominant species in both WWTPs, follow by HAdV-B and HAdV-F. The HAdV-A and HAdV-E species were the least identified. Next generation sequencing identified four times as many genotypes as Sanger sequencing (77 different genotypes). The HAdV-D (types 8, 9, 13, 17, 19, 20, 23, 24, 28, 29, 32, 33, 36, 42, 44, 47, 49, 51, 56, 60, 62, 64, 67 and 81) and HAdV-B (types 2, 3, 7, 11 and 66) were the most predominant species followed by HAdV-F (types 40 and 41), HAdV-A (types 12 and 76), HAdV-E ( type 4) and HAdV-C (type 1). Testing wastewater treatment plants is advantageous as it allows for the detection and identification of HAdV types circulating in the surrounding communities. Due to the large number of species identified using NGS, it is the superior typing method and should be used for future studies. These include strains causing symptomatic and asymptomatic infections. Human adenovirus was detected at comparable frequencies in raw sewage and treated effluent wastewater, with slightly higher detection in effluent samples. However, the viability of these viruses is unknown and should be investigated in further studies. The detection of viruses in wastewater treatment plants are a public health concern as the treated effluent is discharged into rivers, which may be used by communities for domestic and recreational purposes. / Dissertation (MSc (Medical Virology))--University of Pretoria, 2020. / NRF, PRF / Medical Virology / MSc (Medical Virology) / Restricted

Diss. (sammanfattning) Stockholm : Karolinska institutet, 2006. / Härtill 4 uppsatser.

Human adenoviruses (HAdVs) are non-enveloped DNA viruses, currently comprising 52 serotypes which are divided into seven species, designated A to G. The HAdVs are associated with a number of diseases affecting respiratory, urinary, gastrointestinal tracts and the eye. Human AdVs have increasingly been recognized as important pathogens in immunocompromised individuals. Human AdVs are ubiquitous in the environment resulting in the possible contamination of treated and untreated drinking water supplies by human secretions and excretions. As AdVs do not have an envelope, they are extremely resistant to inactivation, allowing for prolonged survival in the environment. The presence of AdVs in water sources is considered important, as they are exceptionally resistant to selected water treatment processes. Precise typing of HAdVs is, therefore, essential for epidemiological surveillance and the understanding of infection chains. The aim of this study was to determine the prevalence and genetic heterogeneity of HAdVs circulating in communities in selected regions of Africa compared to the rest of the world. It is also important to determine the genetic relationship between HAdVs strains occurring in water sources and those detected in human clinical specimens, as this may give some indication as to whether or not water sources are a potential source of infection. As part of ongoing surveillance in southern Africa of treated and untreated water sources for enteric viruses, 765 water samples were tested using a nested polymerase chain reaction (nPCR) for HAdVs. Of these samples, 65 (8.6%) water samples were positive for HAdVs, and selected samples were characterised. In the untreated water, HAdV-F was the dominant species (65.6%) and HAdV-D was second-most common (21.9%) species identified. Species HAdV–B, -A and –C were identified amongst the rest of the strains. From treated water, HAdV-D and –F were identified in one isolate each. Analysis of diarrhoeal stool specimens for HAdVs identified HAdV-F as the predominant species, comprising 77.8% of the identified strains, with species HAdV-C and –A less common, identified in 11.1% specimens. In the respiratory specimens from the same region, HAdV-C was identified in 28.6% of the specimens. Comparative genetic analysis of HAdVs from water sources and clinical specimens showed genetic relatedness between the strains. Water may therefore play an important role as source of infection in the surrounding communities. In developing countries, diarrhoea is a major cause of morbidity and mortality and after rotaviruses HAdVs are considered to be the second-most important cause of viral infantile diarrhoea. Samples also were available from Kenya, where there are very little data on the prevalence and distribution of HAdV serotypes associated with diarrhoea in paediatric patients. From Kenya, 278 stool specimens were analysed, of which 104 (43 diarrhoea; 61 non-diarrhoea) were from an urban hospice for human immunodefiency virus (HIV)-seropositive children, 94 from selected urban clinics and 80 from the rural setting. From these, the detection of HAdVs in diarrhoeal and non-diarrhoeal stool specimens was 43.3% and 16.4%, respectively. In the urban hospice setting, 43.3% of the stool specimens from HIV-seropositive children tested positive for HAdV. The overall detection of HAdVs species and genotypes in the stool specimens showed HAdV-D to predominate, being detected in 36.1% of specimens with HAdV-C (29.5%), HAdV-F (16.4%), HAdV-B (13.1%), and HAdV-A (6.5%) present in lower numbers. This study provided valuable new data on the prevalence and distribution of HAdV genotypes in diarrhoeal stool specimens in Africa. In this study where nucleotide sequence comparison was used to determine the genetic relatedness of African HAdVs to those from the rest of the world, it was noted that in most cases the African strains differed from those from the rest of the world. The use of molecular techniques for the detection and characterisation of HAdVs, especially in Kenyan cohorts, was of importance, as it provided new baseline data for further burden of disease studies which are necessary for future prevention and treatment programmes. / Dissertation (MSc)--University of Pretoria, 2010. / Medical Virology / unrestricted

Submitted by Renata Lopes (renatasil82@gmail.com) on 2017-03-13T17:29:42Z No. of bitstreams: 1 andressasilvinoferreiraassis.pdf: 3364177 bytes, checksum: ff9c20080e11e36f28daf805d56ecc7e (MD5) / Approved for entry into archive by Adriana Oliveira (adriana.oliveira@ufjf.edu.br) on 2017-03-13T19:33:58Z (GMT) No. of bitstreams: 1 andressasilvinoferreiraassis.pdf: 3364177 bytes, checksum: ff9c20080e11e36f28daf805d56ecc7e (MD5) / Made available in DSpace on 2017-03-13T19:33:58Z (GMT). No. of bitstreams: 1 andressasilvinoferreiraassis.pdf: 3364177 bytes, checksum: ff9c20080e11e36f28daf805d56ecc7e (MD5) Previous issue date: 2016-12-19 / O tratamento de esgoto pode ser insuficiente para a completa eliminação de vírus entéricos, tais como adenovírus humanos (HAdV) e rotavírus do grupo A (RVA). Portanto, o retorno do lodo e do efluente tratado ao ambiente pode representar riscos à saúde pública. Este estudo foi conduzido para otimizar um protocolo de floculação orgânica para recuperação viral a partir de lodo de esgoto e efluente tratado, bem como realizar um monitoramento de HAdV e RVA na estação de tratamento de esgoto (ETE) de Juiz de Fora, MG. Nos estudos de otimização, foram propostas adaptações no protocolo de floculação com leite desnatado para lodo e efluente tratado, com modificações no tempo de agitação da amostra, na concentração final de leite desnatado e/ou na etapa de centrifugação. No estudo de monitoramento, esgoto bruto (P1), esgoto primário (P2), lodo (P3) e efluente tratado (P4) foram coletados bimensalmente em 2014 (durante as épocas seca e chuvosa), totalizando 96 amostras (simples e compostas). As cargas virais foram determinadas por PCR quantitativo e o bacteriófago PP7 foi usado como controle interno. Amostras de HAdV e RVA foram submetidas ao sequenciamento e a viabilidade das partículas de HAdV foi avaliada em amostras de P4. Os parâmetros físico-químicos e a contagem de coliformes termotolerantes (CT) foram determinados em cada ponto. Nos estudos de otimização, foram selecionadas duas condições que apresentaram as maiores taxas de recuperação viral no lodo (menor tempo de agitação e maior concentração de leite desnatado) e no efluente tratado (sem primeira etapa de centrifugação e com maior concentração de leite desnatado). Ambas provaram ser ferramentas úteis para pesquisa viral em amostras de campo, inclusive para a pesquisa de vírus gigantes. No monitoramento, o HAdV foi detectado em 85,4% (82/96) dos concentrados, com cargas virais variando de 3,27 x 102 a 2,42 x 106 cópias do genoma por mililitro (cg/mL), ao longo do ano. A presença de RVA foi observada em 52,1% (50/96) dos concentrados (1,38 x 103 a 3,65 x 105 cg/mL), com maior detecção na época seca. A carga viral não foi influenciada pelo tipo de amostra, sendo detectada tanto em amostras simples, quanto em amostras compostas. Todas as amostras de HAdV sequenciadas pertenciam à espécie F tipo 41 e as amostras de RVA pertenciam ao genótipo I1. O tratamento de esgoto reduziu a quantidade de matéria orgânica e sólidos, bem como a contagem de CT e as cargas virais. No entanto, a presença de HAdV e RVA foi observada mesmo após o tratamento, inclusive em amostras de efluente tratado consideradas adequadas pelas legislações atuais, com detecção de partículas infecciosas de HAdV. Foram observadas correlações positivas entre a carga viral e a demanda bioquímica de oxigênio, os sólidos sedimentáveis e sólidos suspensos totais. Os dois protocolos otimizados neste estudo podem ser facilmente adequados para uso em laboratório de rotina, podendo impulsionar o monitoramento viral nos subprodutos gerados na ETE. A carga viral detectada na ETE salienta a disseminação ambiental de RVA e HAdV e aponta o potencial do HAdV como um marcador viral de contaminação em ambientes aquáticos. / Sewage treatment may be insufficient for the complete elimination of enteric viruses such as human adenoviruses (HAdV) and group A rotaviruses (RVA). Thus, the return of sewage sludge and treated effluent to the environment poses concerns potential for public health. This study was conducted to optimize an organic flocculation procedure for viral recovery from sludge and treated effluent, and carry out a surveillance of HAdV and RVA in a wastewater treatment plant (WWTP) at Juiz de Fora, MG. In optimization studies, conditions were proposed for sludge and treated effluent with changes in the stirring time, in the final concentration of skimmed-milk and/or in the centrifugation step. In surveillance study, raw sewage (P1), primary sewage (P2), sludge (P3) and treated effluent (P4) were collected bimonthly in 2014 (during the dry and the rainy season), totaling 96 samples (simple and composite). Quantitative PCR determined viral loads and PP7 bacteriophage was used as internal control. HAdV and RVA strains were selected for sequencing, and the HAdV viability was evaluated in P4 samples. Physicochemical parameters and thermotolerant coliforms (TC) counting were determined at each point. After the optimization studies, two conditions were selected: the ones that showed the highest viral recovery rates in sludge (lower stirring time and higher concentration of skimmed-milk) and treated effluent (without the first centrifugation step and with a higher concentration of skimmed-milk). These conditions proved to be a useful tool for viral search in the field samples, including for the research of giant virus. In surveillance study, HAdV was detected in 85.4% (82/96) of the concentrated, with viral loads ranging from 3.27 x 102 to 2.42 x 106 genome copies per milliliter (gc/mL), throughout the year. RVA presence was observed in 52.1% (50/96) of the samples (1.38 x 103 to 3.65 x 105 gc/mL) with detection greater in the dry season. Viral load was not influenced by the type of sample being detected both in single samples, as in composite samples. All the sequenced HAdV strains belonged to species F type 41, and RVA strains belonged to genotype I1. Sewage treatment reduced the content of organic matter and solids, as well as the TC counts and the viral loads. However, the presence of HAdV and RVA was observed after treatment, even in samples considered adequate by current laws with detection of infectious HAdV particles. Positive correlations were observed between viral load and biochemical oxygen demand, sedimented solids and total suspended solids. Two optimized protocols in this study are easily suitable for routine laboratory use and can boost viral monitoring in by-products generated in the WWTP. Viral load detected in WWTP stress the environmental dissemination of HAdV and RVA and addressed the potential of HAdV as a virological marker of contamination in aquatic environments.