Kott Y
Sci Total Environ. 1981 Apr;18:13-23. doi: 10.1016/s0048-9697(81)80046-0.
Many of the enteric viruses which are transmitted from person to person by the fecal-oral route are found in raw and treated wastewater, and because of their persistence under adverse conditions may also be found in slightly polluted waters. There is no routine examination procedure of water and wastewater for enteroviruses, mainly because of the cumbersome isolation techniques, high cost and the need for highly skilled laboratory personnel. Phages are specific to single species of bacteria, are known for many enteric bacteria, and are very often used for final identification of enteric pathogenic bacteria. Coliphages are prevalent in raw and treated sewage as well as in polluted water, where enteric viruses may also be found. Coliphages were often mentioned as possible viral indicators in polluted water. To be a perfect indicator, they should comply with minimum criteria as follows: (a) they should be present wherever human enteric viruses are present; (b) the coliphage numbers recovered should be equal to or larger than those of enteric viruses recovered; (c) the coliphages should be at least as resistant as enteric viruses to adverse environmental conditions; (d) isolation and quantification of the coliphage should be faster and less expensive than isolation of the enteroviruses. Comparative studies show that the coliphage to enterovirus ratio in wastewater is about 10(3):1. Levels of poliovirus 1 (attenuated) to coliphage f2 remained stable for a few months in oxidation pond effluents. f2 coliphage exhibited higher resistance to chlorination than poliovirus 1 (attenuated). When the two strains were kept in water of different quality, f2 survived longer. In addition, all coliphage counts were completed within 24 h. while those of enteroviruses required about a week. Results indicate very strongly that coliphages can be used as viral indicators and this is already the practice in a few European and other countries.
许多通过粪-口途径在人与人之间传播的肠道病毒存在于未经处理和经过处理的废水中,并且由于它们在不利条件下的持久性,也可能存在于轻度污染的水体中。目前没有针对肠道病毒的水和废水常规检测程序,主要是因为分离技术繁琐、成本高且需要高技能的实验室人员。噬菌体对单一细菌物种具有特异性,已知许多肠道细菌都有对应的噬菌体,并且经常用于肠道病原菌的最终鉴定。大肠杆菌噬菌体在未经处理和经过处理的污水以及污染水中普遍存在,而污染水中也可能存在肠道病毒。大肠杆菌噬菌体经常被提及作为污染水中可能的病毒指示物。要成为一个完美的指示物,它们应符合以下最低标准:(a)在存在人类肠道病毒的任何地方都应存在;(b)回收的大肠杆菌噬菌体数量应等于或大于回收的肠道病毒数量;(c)大肠杆菌噬菌体对不利环境条件的抵抗力应至少与肠道病毒一样强;(d)大肠杆菌噬菌体的分离和定量应比肠道病毒的分离更快且成本更低。比较研究表明,废水中大肠杆菌噬菌体与肠道病毒的比例约为10(3):1。氧化塘出水的脊髓灰质炎病毒1(减毒株)与f2大肠杆菌噬菌体的水平在几个月内保持稳定。f2大肠杆菌噬菌体对氯化的抵抗力高于脊髓灰质炎病毒1(减毒株)。当将这两种毒株保存在不同质量的水中时,f2存活时间更长。此外,所有大肠杆菌噬菌体计数在24小时内完成,而肠道病毒计数则需要大约一周时间。结果非常有力地表明,大肠杆菌噬菌体可以用作病毒指示物,并且在一些欧洲和其他国家已经是这样做的。