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Enteric Viruses And Aquatic Environment

机译:肠病毒和水生环境

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Enteric viruses are mostly found in a variety of aquatic reservoirs including ground water, sewage water, streams, rivers and marine water. They are associated with health risks and responsible for variety of infections in humans. Enteric viruses existence varied greatly in the aquatic environment and also depends upon human activities. Traditional water quality indicators like bacterial coliforms provide no information regarding enteric viruses load in different types of water samples. Environmental water samples are analyzed by a variety of analytical methods for the detection and monitoring of enteric viruses. The virus particles in environment samples are concentrated by adsorption/elution protocols, ultrafiltration or ultra-centrifugation prior to isolation or detection. In spite of the limitations for each method traditional cell culture infectivity assay and molecular biology tools like nucleic acid amplification, microarray based assay or combination of cell culture and polymerase chain reaction are used as valuable informative tool to detect enteric viruses in aquatic environment. INTRODUCTION Water borne diseases have great socioeconomic impacts on public health all around the world. Natural water is a complex mixtures of inorganic, organic compounds and macro-organisms. Swage water comprises of different substance originates from industrial, commercial and residential activities. It also carries different chemicals toxic wastes and biological infectious agents of fungal, bacterial and viral origins. Enteric viral pathogens presence in waste water is important with public health perspective(Bosch, 1998). Enteric viruses commonly cause gastroenteritis and mostly transmitted through the fecaloral route. They include different group of viruses present in human intestinal tract and responsible for different illnesses like fever, meningitis, hepatitis, rashes and respiratory diseases. They are divided in to a number of different families including Picornaviridae (polioviruses, coxsackieviruses, echoviruses, enteroviruses and hepatitis A virus), Adenoviridae (adenoviruses), Reoviridae (reoviruses and rotaviruses), and Caliciviridae (noroviruses, caliciviruses, and astroviruses) (Wilhelmi et al., 2003).Although some enteric viruses have been found in the aquatic environments there is still a lack of comprehensive indicator system for monitoring of these organisms (Wyn Jones et al., 2011). These viruses have the ability to survive for a longer time (130) days and remain infectious at lower doses. They are discharged continuously to environment from their hosts (Fong and Lipp, 2005).The monitoring of enteric viruses in different aquatic environments would be helpful to assess the risk of human exposures. In aquatic environment the quantification of these viruses is difficult technically, requires a long time and is expensive. In fact, the viruses of primary concern are difficult or impossible to quantify. Therefore, many public agencies rely on bacterial indicator organisms to establish a quality However, they are not correlated with the occurrence of enteric viruses (Parkin et al., 2003). The main problems with bacterial indicators are, they do not reflect the presence for other pathogens, such as viruses and parasites, they do not depict the fact that many pathogens reproduce in the environment after being excreted by their host (Fong and Lipp, 2005). In some cases, where assays have been within the limits recommended for bacterial indicators in water, human enteric viruses have been found at dangerously high concentrations. Current microbial indicators (e.g. enterococci, fecal streptococci and fecal coliform bacteria) simply do not give information on the viral quality of water (Ehlers et al., 2005). Other studies suggest the use of alternative indicators of viral pathogens, such as bacteriophages, (Ogorzaly et al., 2009), or adenoviruses (Wyn Jones et al., 2011). But still there is no consensus on the best indicator for v
机译:肠道病毒主要存在于各种水库中,包括地下水,污水,溪流,河流和海水。它们与健康风险相关,并负责人类的各种感染。肠病毒在水生环境中的存在差异很大,并且还取决于人类的活动。传统的水质指标(如细菌大肠菌)无法提供有关不同类型水样中肠病毒负荷的信息。通过多种分析方法对环境水样进行分析,以检测和监测肠道病毒。在分离或检测之前,通过吸附/洗脱方案,超滤或超速离心浓缩环境样品中的病毒颗粒。尽管每种方法都有局限性,传统的细胞培养传染性测定和分子生物学工具(如核酸扩增,基于微阵列的测定或细胞培养与聚合酶链反应的结合)仍被用作检测水生环境中肠道病毒的有价值的信息工具。引言水传播疾病对全世界的公共卫生都具有巨大的社会经济影响。天然水是无机,有机化合物和大生物的复杂混合物。污水中的各种物质均来自工业,商业和住宅活动。它还携带各种化学有毒废料以及真菌,细菌和病毒来源的生物传染因子。从公共卫生的角度来看,废水中肠病毒病原体的存在很重要(Bosch,1998)。肠病毒通常引起肠胃炎,并且大多通过粪便途径传播。它们包括存在于人体肠道中的不同种类的病毒,这些病毒负责不同的疾病,例如发烧,脑膜炎,肝炎,皮疹和呼吸道疾病。它们分为多个不同的科,包括角膜病毒科(脊髓灰质炎病毒,柯萨奇病毒,回声病毒,肠病毒和甲型肝炎病毒),腺病毒科(腺病毒),呼肠孤病毒科(呼肠孤病毒和轮状病毒)和杯状病毒科(诺如病毒,杯状病毒和星形螺旋病毒)等人,2003年)。尽管在水生环境中发现了一些肠病毒,但仍然缺乏用于监测这些生物的综合指标系统(Wyn Jones等人,2011年)。这些病毒能够存活更长的时间(130)天,并以较低的剂量保持感染力。它们不断地从宿主处释放到环境中(Fong and Lipp,2005)。在不同水生环境中监测肠道病毒将有助于评估人类暴露的风险。在水生环境中,这些病毒的定量技术上很困难,需要很长时间并且很昂贵。实际上,主要关注的病毒很难或无法量化。因此,许多公共机构依靠细菌指示生物来确定其质量。然而,它们与肠病毒的发生无关(Parkin等,2003)。细菌指示剂的主要问题是,它们不能反映其他病原体的存在,例如病毒和寄生虫,它们不能描述许多病原体在被宿主排泄后在环境中繁殖的事实(Fong and Lipp,2005)。 。在某些情况下,如果测定的含量在水中细菌指标的推荐范围内,则发现人类肠病毒的浓度很高。当前的微生物指标(例如肠球菌,粪链球菌和粪大肠菌)根本无法提供水的病毒质量信息(Ehlers等,2005)。其他研究建议使用病毒病原体的替代指标,例如噬菌体(Ogorzaly等,2009)或腺病毒(Wyn Jones等,2011)。但是,关于v的最佳指标仍未达成共识

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