Previous Article | Next Article 
Applied and Environmental Microbiology, October 2002, p. 5167-5169, Vol. 68, No. 10
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.10.5167-5169.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Comparative Inactivation of Enteroviruses and Adenovirus 2 by UV Light
Charles P. Gerba,1* Dawn M. Gramos,1 and Nena Nwachuku2
Department of Soil, Water, and Environmental Science, University of Arizona, Tucson, Arizona 85721,1
Office of Water, Office of Science and Technology, U.S. Environmental Protection Agency, Washington, D.C. 204602
Received 15 March 2002/
Accepted 16 July 2002

ABSTRACT
The doses of UV irradiation necessary to inactivate selected
enteric viruses on the U.S. Environmental Protection Agency
Contaminant Candidate List were determined. Three-log reductions
of echovirus 1, echovirus 11, coxsackievirus B3, coxsackievirus
B5, poliovirus 1, and human adenovirus type 2 were effected
by doses of 25, 20.5, 24.5, 27, 23, and 119 mW/cm
2, respectively.
Human adenovirus type 2 is the most UV light-resistant enteric
virus reported to date.

INTRODUCTION
Under, the 1996 amendments to the Safe Drinking Water Act, the
U. S. Environmental Protection Agency is required to publish
a list of unregulated contaminants that are known or expected
to occur in public water systems and whose presence in drinking
water may pose a health risk. The first of these lists, published
in 1998, identified 10 microbiological contaminants, including
echoviruses, coxsackieviruses, and adenoviruses. All of these
viruses have been associated with outbreaks involving drinking
water (
1,
10,
12). UV light disinfection is being increasingly
used in the treatment of both wastewater and potable drinking
water since such treatment does not produce disinfectant by-products
and is effective against
Cryptosporidium oocysts (
2). The goal
of this study was to compare the ways inactivation by UV light
varies among the enteroviruses and a nonenteric adenovirus.
Human adenovirus type 2 Adenoid 6 (ATCC VR-846) was propagated and assayed in the PLC/PRF/5 cell line (6). Coxsackievirus B5 HA (ATCC VR-688), coxsackievirus B5 Faulkner (ATCC VR-185), echovirus 1 Farouk (ATCC VR-31), echovirus 11 Gregory (ATCC VR-41), and poliovirus 1 LSC-2ab were propagated in the BGM cell line. The viruses were grown in serum-free medium, and after the production of cytopathogenic effects in the cell monolayer, the medium was frozen and thawed once at -20°C to release the virus. This was followed by centrifugation at 2,800 x g for 12 min, addition of polyethylene glycol (9%) and sodium chloride (5.8%), and stirring overnight at 4°C. The virus suspension was then subjected to high-speed centrifugation (10,000 x g for 30 min). The resulting virus pellet was resuspended in 0.01 M phosphate-buffered saline to 18% of the original volume. Resuspension was followed by chloroform extraction in which equal parts of virus suspension and chloroform were mixed and shaken for 10 min. The virus-chloroform suspension was then centrifuged at low speed (2,500 x g for 5 min), and the upper aqueous layer was collected, the titers were determined, and the material was stored at -80°C.
Viruses were assayed in 24-well plastic cell culture plates by the most-probable-number method. Six wells were used for each dilution, and the titers of the viruses were determined by using a general-purpose program adapted from the method described by Hurley and Roscoe (9). The production of cytopathogenic effects was used as an indication of a viable virus. All experiments were performed at least four times, with the exception of that for poliovirus 1 (performed twice), which was included as a control.
A collimated beam incorporating an 8-W low-pressure mercury UV lamp (Sankyo Denki model G8T5.2N), as previously described, was used (14). An IL-2000 radiometer (International Light, Newburyport, Mass.) set with a model 254 photodetector (catalog no. SED 240/NS254/W) was utilized to measure the UV light intensity. A viral suspension was added to a glass petri dish, which was placed on a magnetic stir plate, and continuously stirred. For ease of calculation, it was determined that the petri dish must contain 14 ml of solution in order to achieve a 1-cm distance from the bottom of the petri dish to the surface of the viral suspension. This experimental design allows for an accurate irradiance measurement when low-pressure UV lamps are used (2). A different petri dish was used for each exposure period. Five to six different exposure times were used for each virus. In addition, a control petri dish containing virus was held under the same conditions to assess whether any viral decay occurred during the experiment. UV intensity was calculated as described by Meng and Gerba (14).
Statistical analysis of the inactivation kinetics for each of the viruses was performed by using SYSTAT (version 9) and EXCEL (Microsoft Office 97). The P values were computed and compared at the confidence level of 95%, or 0.05.
Figure 1 shows the dose versus log survival data for the viruses studied, and Table 1 indicates the UV light doses needed to inactivate different amounts of the studied viruses. The doses in Table 1 were interpolated from the linear-regression lines for each of the respective viruses. An analysis of variance indicated that there was a significant difference between the dose required to inactivate the enteroviruses and that needed to inactivate adenovirus 2 (P = 3.3 x 10-6). Poliovirus 1 was used as a control in this study, and the results indicate that the dose required to achieve a 99.9% inactivation was similar to that previously reported in the literature (16).
The guidance manual published by the U.S. Environmental Protection
Agency (
7) recommends a UV light dose of 21 mW/cm
2 for a 2-log
10 inactivation and a dose of 36 mW/cm
2 for a 3-log
10 inactivation
of enteric viruses for drinking water treatment. The results
of this study indicate that this would be adequate for enteroviruses
but not for adenovirus type 2. The enteroviruses showed little
variability in resistance to UV light, and some were slightly
more sensitive than previously reported (
15). In the present
study, adenovirus type 2 demonstrated more resistance than adenovirus
types 40 and 41 did in a previous study (
14). The greater resistance
of adenovirus type 2 may have been due to genetic differences,
its structure, or the way in which the virus was prepared. Meng
and Gerba (
14), in an effort to release as many viral particles
as possible from the host cells, performed the cell culture
freeze-thaw procedure five times, compared to only once in the
present study. It is possible that multiple freezing-thawing
procedures damage the viral particle, making it more susceptible
to disinfection. The greater resistance of adenovirus type 2
may also have been due to the fact that it has only one fiber
projection at each penton capsomere whereas adenovirus type
40 has two fibers; this fiber projection may cause a shadowing
effect or a disruption in the adsorbance by the viral nucleic
acids. However, it is more likely that adenoviruses display
greater resistance than either enteric viruses or spore-forming
bacteria (
15) because they contain double-stranded DNA and are
able to use the host cell enzymes to repair damages in the DNA
caused by UV irradiation. Adenoviruses have been used to measure
the occurrence of repair enzymes in normal cells and cancer
cells (
4,
5). The presence and availability of these enzymes
affect the ability of the virus DNA to be repaired. Thus, it
is possible that the assay of adenovirus in different cell lines
after UV light exposure may provide different results, i.e.,
the greater availability of repair enzymes may result in a greater
number of viral particles surviving UV treatment.
The results of this study suggest that double-stranded DNA viruses are likely the most resistant viruses to UV light disinfection. These viruses have been responsible for both drinking water and recreational waterborne disease outbreaks (9, 12). The enteric adenoviruses, types 40 and 41, cause mortalities as great as 50% in immunocompromised individuals (8). Adenoviruses are believed to occur in greater concentrations than other enteric viruses (11) and have been detected in treated drinking water (13). The use of UV light in the disinfection of drinking water and wastewater has increased rapidly in recent years (3). Consideration should be given to the resistance of adenoviruses to UV light disinfection when appropriate doses for the control of waterborne viruses are being determined.

ACKNOWLEDGMENTS
This work was supported by the Office of Water, Office of Science
and Technology, U.S. Environmental Protection Agency, under
contract 68-C-99232.
The opinions expressed here are those of the authors and not necessarily those of the U.S. Environmental Protection Agency.

FOOTNOTES
* Corresponding author. Mailing address: Department of Soil, Water, and Environmental Science, University of Arizona, Tucson, AZ 85721. Phone: (520) 621-6906. Fax: (520) 621-6366. E-mail:
gerba{at}ag.arizona.edu.


REFERENCES
1 - Amvrosieva, T. V., L. P. Titov, M. Mulders, T. Hovi, O. V. Dyakonova, V. L. Votyakov, Z. B. Kvacheva, V. F. Eremin, R. M. Sharko, S. V. Orlova, O. N. Kazinets, and Z. F. Bogush. 2001. Viral water contamination as the cause of aseptic meningitis outbreak in Belarus. Cent. Eur. J. Public Health 9:154-157.[Medline]
2 - Clancy, J. L., Z. Bukhari, T. H. Hargy, J. R. Bolton, B. W. Dussert, and M. M. Marshall. 2000. Using UV to inactivate Cryptosporidium. J. Am. Water Works Assoc. 90(9):97-104.
3 - Cotton, C. A., D. M. Owen, G. C. Cline, and T. P. Brodeur. 2001. UV disinfection costs for inactivating Cryptosporidium. J. Am. Water Works Assoc. 93(4):82-94.
4 - Day, R. S., III. 1993. Deoxyguanosine reverses inhibition by hydroxyurea of repair of UV-irradiated adenovirus 5. Mutat. Res. 293:215-297.[Medline]
5 - Day, R. S., III, A. S. Giuffrida, and C. W. Dingman. 1975. Repair by human cells of adenovirus 2 damaged by psoralen plus near ultraviolet light treatment. Mutat. Res. 33:311-320.[CrossRef][Medline]
6 - Enriquez, C. E., C. J. Hurst, and C. P. Gerba. 1995. Survival of enteric adenoviruses 40 and 41 in tap, sea, and wastewater. Water Res. 29:2546-2553.
7 - Gerba, C. P., J. B. Rose, and C. N. Haas. 1996. Sensitive populations: who is at the greatest risk? Int. J. Food Microbiol. 30:113-123.[CrossRef][Medline]
8 - Hunter, P. R. 1997. Water borne disease. Wiley, Chichester, United Kingdom.
9 - Hurley, M. A., and M. E. Roscoe. 1983. Automated statistical analysis of microbial enumeration by dilution series. J. Appl. Bacteriol. 55:159-164.
10 - Kapadia, C. R., P. Bhat, S. J. Baker, and V. I. Mathan. 1984. A common-source epidemic of mixed diarrhea with secondary transmission. Am. J. Epidemiol. 120:743-749.[Abstract/Free Full Text]
11 - Krikelis, V., N. Spyrou, P. Markoulatos, and C., Serie. 1985. Seasonal distribution of enteroviruses and adenoviruses in domestic sewage. Can. J. Microbiol. 31:24-25.[Medline]
12 - Kukkula, M., P. Arstila, M. L. Klossner, L. Manula, C. H. Bonsorff, and P. Jaatinen. 1997. Waterborne outbreak of viral gastroenteritis. Scand. J. Infect. Dis. 29:415-418.[Medline]
13 - Lee, S. H., and S. J. Kim. 2002. Detection of infectious enteroviruses and adenoviruses in tap water in urban areas in Korea. Water Res. 36:248-256.[Medline]
14 - Meng, Q. S., and C. P. Gerba. 1996. Comparative inactivation of enteric adenoviruses, poliovirus, and coliphage by ultraviolet irradiation. Water Res. 30:2665-2668.[CrossRef]
15 - Roessler, P. F., and B. F. Severin. 1996. Ultraviolet light disinfection of water and wastewater, p. 313-368. In C. J. Hurst (ed.), Modeling disease transmission and its prevention by disinfection. Cambridge University Press, Cambridge, United Kingdom.
16 - U.S. Environmental Protection Agency. 1990. Guidance manual for compliance with the filtration and disinfection requirements for public water systems using surface water sources. U.S. Environmental Protection Agency, Washington, D.C.
Applied and Environmental Microbiology, October 2002, p. 5167-5169, Vol. 68, No. 10
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.10.5167-5169.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
This article has been cited by other articles:
-
Parmegiani, L., Cognigni, G. E., Filicori, M.
(2009). Ultra-violet sterilization of liquid nitrogen prior to vitrification. Hum Reprod
24: 2969-2969
[Full Text]
-
Symonds, E. M., Griffin, D. W., Breitbart, M.
(2009). Eukaryotic Viruses in Wastewater Samples from the United States. Appl. Environ. Microbiol.
75: 1402-1409
[Abstract]
[Full Text]
-
Eischeid, A. C., Meyer, J. N., Linden, K. G.
(2009). UV Disinfection of Adenoviruses: Molecular Indications of DNA Damage Efficiency. Appl. Environ. Microbiol.
75: 23-28
[Abstract]
[Full Text]
-
Sirikanchana, K., Shisler, J. L., Marinas, B. J.
(2008). Effect of Exposure to UV-C Irradiation and Monochloramine on Adenovirus Serotype 2 Early Protein Expression and DNA Replication. Appl. Environ. Microbiol.
74: 3774-3782
[Abstract]
[Full Text]
-
Linden, K. G., Thurston, J., Schaefer, R., Malley, J. P. Jr.
(2007). Enhanced UV Inactivation of Adenoviruses under Polychromatic UV Lamps. Appl. Environ. Microbiol.
73: 7571-7574
[Abstract]
[Full Text]
-
Hundesa, A., Maluquer de Motes, C., Bofill-Mas, S., Albinana-Gimenez, N., Girones, R.
(2006). Identification of Human and Animal Adenoviruses and Polyomaviruses for Determination of Sources of Fecal Contamination in the Environment. Appl. Environ. Microbiol.
72: 7886-7893
[Abstract]
[Full Text]
-
Brownell, S. A., Nelson, K. L.
(2006). Inactivation of Single-Celled Ascaris suum Eggs by Low-Pressure UV Radiation.. Appl. Environ. Microbiol.
72: 2178-2184
[Abstract]
[Full Text]
-
Nwachuku, N., Gerba, C. P., Oswald, A., Mashadi, F. D.
(2005). Comparative Inactivation of Adenovirus Serotypes by UV Light Disinfection. Appl. Environ. Microbiol.
71: 5633-5636
[Abstract]
[Full Text]
-
Fong, T.-T., Lipp, E. K.
(2005). Enteric Viruses of Humans and Animals in Aquatic Environments: Health Risks, Detection, and Potential Water Quality Assessment Tools. Microbiol. Mol. Biol. Rev.
69: 357-371
[Abstract]
[Full Text]
-
He, J.-W., Jiang, S.
(2005). Quantification of Enterococci and Human Adenoviruses in Environmental Samples by Real-Time PCR. Appl. Environ. Microbiol.
71: 2250-2255
[Abstract]
[Full Text]
-
Sano, D., Omura, T.
(2005). Construction of a Cloning System for the Mass Production of a Virus-Binding Protein Specific for Poliovirus Type 1. Appl. Environ. Microbiol.
71: 2608-2615
[Abstract]
[Full Text]
-
Fong, T.-T., Griffin, D. W., Lipp, E. K.
(2005). Molecular Assays for Targeting Human and Bovine Enteric Viruses in Coastal Waters and Their Application for Library-Independent Source Tracking. Appl. Environ. Microbiol.
71: 2070-2078
[Abstract]
[Full Text]
-
Gerba, C. P., Smith, J. E. Jr.
(2005). Sources of Pathogenic Microorganisms and Their Fate during Land Application of Wastes. J. Environ. Qual.
34: 42-48
[Abstract]
[Full Text]
-
Lee, C., Lee, S.-H., Han, E., Kim, S.-J.
(2004). Use of Cell Culture-PCR Assay Based on Combination of A549 and BGMK Cell Lines and Molecular Identification as a Tool To Monitor Infectious Adenoviruses and Enteroviruses in River Water. Appl. Environ. Microbiol.
70: 6695-6705
[Abstract]
[Full Text]
-
Duizer, E., Bijkerk, P., Rockx, B., de Groot, A., Twisk, F., Koopmans, M.
(2004). Inactivation of Caliciviruses. Appl. Environ. Microbiol.
70: 4538-4543
[Abstract]
[Full Text]
-
Sano, D., Matsuo, T., Omura, T.
(2004). Virus-Binding Proteins Recovered from Bacterial Culture Derived from Activated Sludge by Affinity Chromatography Assay Using a Viral Capsid Peptide. Appl. Environ. Microbiol.
70: 3434-3442
[Abstract]
[Full Text]
-
Esfandiarei, M., Luo, H., Yanagawa, B., Suarez, A., Dabiri, D., Zhang, J., McManus, B. M.
(2004). Protein Kinase B/Akt Regulates Coxsackievirus B3 Replication through a Mechanism Which Is Not Caspase Dependent. J. Virol.
78: 4289-4298
[Abstract]
[Full Text]