van der Kooij Dick, Bakker Geo L, Italiaander Ronald, Veenendaal Harm R, Wullings Bart A
KWR Watercycle Research Institute, Nieuwegein, the Netherlands
Vitens NV, Zwolle, the Netherlands.
Appl Environ Microbiol. 2017 Feb 15;83(5). doi: 10.1128/AEM.02737-16. Print 2017 Mar 1.
in potable water installations poses a potential health risk, but quantitative information about its replication in biofilms in relation to water quality is scarce. Therefore, biofilm formation on the surfaces of glass and chlorinated polyvinyl chloride (CPVC) in contact with tap water at 34 to 39°C was investigated under controlled hydraulic conditions in a model system inoculated with biofilm-grown The biofilm on glass (average steady-state concentration, 23 ± 9 pg ATP cm) exposed to treated aerobic groundwater (0.3 mg C liter; 1 μg assimilable organic carbon [AOC] liter) did not support growth of the organism, which also disappeared from the biofilm on CPVC (49 ± 9 pg ATP cm) after initial growth. attained a level of 4.3 log CFU cm in the biofilms on glass (1,055 ± 225 pg ATP cm) and CPVC (2,755 ± 460 pg ATP cm) exposed to treated anaerobic groundwater (7.9 mg C liter; 10 μg AOC liter). An elevated biofilm concentration and growth of were also observed with tap water from the laboratory. The and and amoeba-resisting predominated in the clones and isolates retrieved from the biofilms. In the biofilms, the colony count correlated significantly with the total cell count (TCC), heterotrophic plate count, ATP concentration, and presence of This amoeba was rarely detected at biofilm concentrations of <100 pg ATP cm A threshold concentration of approximately 50 pg ATP cm (TCC = 1 × 10 to 2 × 10 cells cm) was derived for growth of in biofilms. is the etiologic agent in more than 10,000 cases of Legionnaires' disease that are reported annually worldwide and in most of the drinking water-associated disease outbreaks reported in the United States. The organism proliferates in biofilms on surfaces exposed to warm water in engineered freshwater installations. An investigation with a test system supplied with different types of warm drinking water without disinfectant under controlled hydraulic conditions showed that treated aerobic groundwater (0.3 mg liter of organic carbon) induced a low biofilm concentration that supported no or very limited growth of Elevated biofilm concentrations and colony counts were observed on surfaces exposed to two types of extensively treated groundwater, containing 1.8 and 7.9 mg C liter and complying with the microbial water quality criteria during distribution. Control measures in warm tap water installations are therefore essential for preventing growth of .
在饮用水设施中存在潜在健康风险,但关于其在生物膜中与水质相关的繁殖的定量信息却很少。因此,在接种了生物膜生长菌的模型系统中,在受控水力条件下,研究了34至39°C下与自来水接触的玻璃和氯化聚氯乙烯(CPVC)表面上的生物膜形成情况。暴露于经处理的好氧地下水(0.3毫克碳/升;1微克可同化有机碳[AOC]/升)的玻璃上的生物膜(平均稳态浓度,23±9皮克ATP/平方厘米)不支持该生物体生长,该生物体在初始生长后也从CPVC上的生物膜(49±9皮克ATP/平方厘米)中消失。在暴露于经处理的厌氧地下水(7.9毫克碳/升;10微克AOC/升)的玻璃(1,055±225皮克ATP/平方厘米)和CPVC(2,755±460皮克ATP/平方厘米)上的生物膜中,该菌达到了4.3 log CFU/平方厘米的水平。用实验室自来水也观察到生物膜浓度升高和该菌生长。从生物膜中回收的克隆和分离物中,该菌和抗变形虫菌占主导地位。在生物膜中,该菌的菌落计数与总细胞计数(TCC)、异养平板计数、ATP浓度以及该菌的存在显著相关。在生物膜浓度<100皮克ATP/平方厘米时很少检测到这种变形虫。得出生物膜中该菌生长的阈值浓度约为50皮克ATP/平方厘米(TCC = 1×10至2×10个细胞/平方厘米)。该菌是全球每年报告的10,000多例军团病病例以及美国报告的大多数与饮用水相关的疾病暴发的病原体。该生物体在工程淡水设施中暴露于温水的表面上的生物膜中增殖。在受控水力条件下,对供应不同类型无消毒剂温饮用水的测试系统进行的一项调查表明,经处理的好氧地下水(0.3毫克/升有机碳)诱导的生物膜浓度较低,不支持该菌生长或仅支持其非常有限的生长。在暴露于两种经过广泛处理的地下水的表面上观察到生物膜浓度升高和该菌菌落计数增加,这两种地下水含有1.8和7.9毫克碳/升,并且在分配过程中符合微生物水质标准。因此,温暖自来水设施中的控制措施对于防止该菌生长至关重要。