Genogroup distribution of F-specific coliphages in wastewater and river water in the Kofu basin in Japan

Aims: To determine the genogroup distribution of F‐specific coliphages in aquatic environments using the plaque isolation procedure combined with genogroup‐specific real‐time PCR. Methods and Results: Thirty water samples were collected from a wastewater treatment plant and a river in the Kofu basin in Japan on fine weather days. F‐specific coliphages were detected in all tested samples, 187 (82%) of 227 phage plaques isolated were classified into one of the 4 F‐specific RNA (F‐RNA) coliphage genogroups and 24 (11%) plaques were F‐specific DNA coliphages. Human genogroups II and III F‐RNA coliphages were more abundant in raw sewage than animal genogroups I and IV, excluding one sample that was suspected to be heavily contaminated with sporadic heavy animal faeces. The secondary‐treated sewage samples were highly contaminated with genogroup I F‐RNA coliphages, probably because of different behaviours among the coliphage genogroups during wastewater treatment. The river water samples were expected to be mainly contaminated with human faeces, independent of rainfall effects. Conclusions: A wide range of F‐specific coliphage genogroups were successfully identified in wastewater and river water samples. Significance and Impact of the Study: Our results clearly show the usefulness of the genogroup‐specific real‐time PCR for determining the genogroups of F‐specific coliphages present in aquatic environments.     

Inactivation of murine norovirus, feline calicivirus and echovirus 12 as surrogates for human norovirus (NoV) and coliphage (F+) MS2 by ultraviolet light (254 nm) and the effect of cell association on UV inactivation

Aims: To determine inactivation profiles of three human norovirus (NoV) surrogate viruses and coliphage MS2 by ultraviolet (UV) irradiation and the protective effect of cell association on UV inactivation. Methods and Results: The inactivation rate for cell‐free virus or intracellular echovirus 12 was determined by exposure to 254‐nm UV light at fluence up to 100 mJ cm^?2. The infectivity of murine norovirus (MNV), feline calicivirus (FCV) and echovirus 12 was determined by cell culture infectivity in susceptible host cell lines, and MS2 infectivity was plaque assayed on Escherichia coli host cells. The UV fluencies to achieve 4‐log₁₀ inactivation were 25, 29, 30 and 70 (mJ cm^?2) for cell‐free FCV, MNV, echovirus 12 and MS2, respectively. However, a UV fluence of 85 mJ cm^?2 was needed to inactivate intracellular echovirus 12 by 4 log₁₀. Conclusions: Murine norovirus and echoviruses 12 are more conservative surrogates than FCV to predict the UV inactivation response of human NoV. Intracellular echovirus 12 was 2·8‐fold more resistant to UV irradiation than cell‐free one. Significance and Impact of the Study: Variation in UV susceptibilities among NoV surrogate viruses and a likely protective effect of cell association on virus susceptibility to UV irradiation should be considered for effective control of human NoV in water.     

Estimation of bioaerosol risk of infection to residents adjacent to a land applied biosolids site using an empirically derived transport model

AIM: The purpose of this study was to develop an empirically derived transport model, which could be used to predict downwind concentrations of viruses and bacteria during land application of liquid biosolids and subsequently assess microbial risk associated with this practice. METHODS AND RESULTS: To develop the model, coliphage MS-2 and Escherichia coli were aerosolized after addition to water within a biosolids spray application truck, and bioaerosols were collected at discrete downwind distances ranging from 2 to 70 m. Although coliphage were routinely detected, E. coli did not frequently survive aerosolization. Data on aerosolized coliphage was then used to generate a virus transport model. Risks of infection were calculated for various ranges of human virus concentrations that could be found in biosolids. CONCLUSIONS: A conservative estimate at 30.5 m (assumed to be nearest adjacent residences) downwind, resulted in risks of infection of 1 : 100,000, to the more realistic 1 : 10,000,000 per exposure. Conservative annual risks were calculated to be no more than 7 : 100,000 where as a more realistic risk was no greater than 7 : 10,000,000. Overall, the viral risk to residences adjacent to land application sites appears to be low, both for one time and annual probabilities of infection. SIGNIFICANCE AND IMPACT OF THE STUDY: This study demonstrated a simple approach towards modelling viral pathogens aerosolized from land applied liquid biosolids, and offers insight into the associated viral risk.     

Compact form of DNA induced by DNA-binding protein HU.

Interaction of DNA-binding protein HU from Bacillus stearothermophilus (HUBst) with coliphage T2 DNA was investigated by means of a single-duplex DNA chain visualization method using fluorescence microscopy. Fluorescence microscopic images of coliphage T2 DNA molecules were observed as a function of HUBst concentration. The average fluorescence image size of T2 DNA decreased with increase in HUBst concentration to a size comparable to that of a DNA globule induced by polyethylene glycol (PEG) and multivalent cation (MVC). The change to globule-like DNA proceeded gradually and monotonously, in contrast to the coil-globule transition of DNA induced by PEG and MVC. The histogram of the fluorescence image length was essentially a single-modal one throughout the process of conformational change. These results indicate that the process of shrinking of DNA from a random coil to a globule-like one is not of a transitional nature. The interaction of HUBst with DNA and the mechanism of shrinkage are concluded to be different from those of PEG-induced and MVC-induced coil-globule transition of DNA.     

Inactivation of indicator micro-organisms from various sources of faecal contamination in seawater and freshwater

AIM: The survival of indicator micro-organisms in aquatic systems is affected by both biotic and abiotic factors. Much of the past research on this topic has been conducted using laboratory-generated cultures of indicator bacteria. For this study, we used natural sources of faecal contamination as inoculants into environmental water samples, thereby representing the wide diversity of organisms likely to be found in faecal contamination. METHODS AND RESULTS: Rates of inactivation of water quality indicators, total coliforms (TC), Escherichia coli, enterococci (EC) and F+-specific coliphage were studied in three experiments using inoculants of sewage influent, sewage effluent and urban storm drain run-off. Effects of temperature, nutrients, total suspended solids, bacterial load and solar irradiation were studied in fresh and seawater matrices. Results demonstrated that temperature and solar irradiation had significant effects upon rates of inactivation (anova, P < 0.001). Inactivation rates were similar, regardless of the inoculant type. EC degraded the slowest in the dark with T90s of 115-121 and 144-177 h at 20 and 14 degrees C, respectively. When incubated in sunlight, EC was inactivated significantly more rapidly than either E. coli or F+-specific coliphage (P < 0.001). CONCLUSIONS: Inactivation of indicator bacteria is not dependent upon the original source of contamination. Inactivation rates of indicator bacteria were similar in fresh and seawater matrices. However, EC degraded more rapidly in sunlight than E. coli. SIGNIFICANCE AND IMPACT OF THE STUDY: This study suggests that the source of faecal contamination is not an important factor to inactivation rates of indicator bacteria. However, rates of inactivation of indicator bacteria are likely system specific.     

PCR detection of pathogenic viruses in southern California urban rivers

AIMS: To investigate human viral contamination in urban rivers and its impact on coastal waters of southern California, USA. METHODS AND RESULTS: Three types of human viruses (adeno, entero and hepatitis A) were detected using nested- and RT-PCR from 11 rivers and creeks. Faecal indicator bacteria as well as somatic and F-specific coliphage were also tested. Approximately 50% of the sites were positive for human adenoviruses. However, there was no clear relationship between detection of human viruses and the concentration of indicator bacteria and coliphage. Both faecal indicator bacteria and human viral input at beaches near river mouths were associated with storm events. The first storm of the wet season seemed to have the greatest impact on the quality of coastal water than following storm events. CONCLUSIONS: This study provides the first direct evidence that human viruses are prevalent in southern California urban rivers. Urban run-off impacts coastal water quality most significantly during the storm season. SIGNIFICANCE AND IMPACT OF THE STUDY: To protect human health during water recreational activities, it is necessary to develop effective strategies to manage urban run-off during storm events.     

Ecology of coliphages in southern California coastal waters

Aims: This study aims to investigate the ecology of coliphages, an important microbial pollution indicator. Specifically, our experiments address (i) the ability of environmental Escherichia coli (E. coli) to serve as hosts for coliphage replication, and (ii) the temporal and spatial distribution of coliphages in coastal waters. Methods and Results: Water samples from three locations in California’s Newport Bay watershed were tested for the presence of coliphages every 2 weeks for an entire year. A total of nine E. coli strains isolated from various sources served as hosts for coliphage detection. Coliphage occurrence was significantly different between freshwater, estuarine and coastal locations and correlated with water temperature, salinity and rainfall in the watershed. The coliphages isolated on the environmental hosts had a broad host‐range relative to the coliphages isolated on an E. coli strain from sewage and a US EPA recommended strain for coliphage detection. Conclusions: Coliphage occurrence was related to the temperature, rainfall and salinity within the bay. The adaptation to a broad host‐range may enable the proliferation of coliphages in the aquatic environment. Significance and Impact of the Study: Understanding the seasonal variation of phages is useful for establishing a background level of coliphage presence in coastal waters. The broad host‐range of coliphages isolated on the environmental E. coli host calls for investigation of coliphage replication in the aquatic environment.