E. coli and bacteriophage MS2 disinfection by UV, ozone and the combined UV and ozone processes

Frontiers of Environmental Science & Engineering - Tập 8 - Trang 547-552 - 2013
Jingyun Fang1,2, Huiling Liu1, Chii Shang3, Minzhen Zeng4, Mengling Ni2, Wei Liu2
1State Key Laboratory of Urban Water Resources and Environment, Harbin Institute of Technology, Harbin, China
2School of Environmental Science and Technology, Sun Yat-Sen University, Guangzhou, China
3Department of Civil and Environmental Engineering, The Hong Kong University of Science and Technology, Hong Kong, China
4Water & Urban Development, AECOM Asia Co. Ltd., Hong Kong, China

Tóm tắt

The combination of low-dose ozone with ultraviolet (UV) irradiation should be an option to give benefit to disinfection and reduce drawbacks of UV and ozone disinfection. However, less is known about the disinfection performance of UV and ozone (UV/ozone) coexposure and sequential UV-followed-by-ozone (UV-ozone) and ozone-followed-by-UV (ozone-UV) exposures. In this study, inactivation of E. coli and bacteriophage MS2 by UV, ozone, UV/ozone coexposure, and sequential UV-ozone and ozone-UV exposures was investigated and compared. Synergistic effects of 0.5–0.9 log kill on E. coli inactivation, including increases in the rate and efficiency, were observed after the UV/ozone coexposure at ozone concentrations as low as 0.05 mg·L−1 in ultrapure water. The coexposure with 0.02-mg·L−1 ozone did not enhance the inactivation but repressed E. coli photoreactivation. Little enhancement on E. coli inactivation was found after the sequential UV-ozone or ozone-UV exposures. The synergistic effect on MS2 inactivation was less significant after the UV/ozone coexposure, and more significant after the sequential ozone-UV and UV-ozone exposures, which was 0.2 log kill for the former and 0.8 log kill for the latter two processes, at ozone dose of 0.1 mg·L−1 and UV dose of 8.55 mJ·cm−2 in ultrapure water. The synergistic effects on disinfection were also observed in tap water. These results show that the combination of UV and low-dose ozone is a promising technology for securing microbiological quality of water.

Tài liệu tham khảo

Fawell J, Robinson D, Bull R, Birnbaum L, Boorman G, Butterworth B, Daniel P, Galal-Gorchev H, Hauchman F, Julkunen P, Klaassen C, Krasner S, Orme-Zavaleta J, Reif J, Tardiff R. Disinfection by-products in drinking water: critical issues in health effects research. Environmental Health Perspectives, 1997, 105(1): 108–109 Mac Kenzie W R, Hoxie N J, Proctor M E, Gradus M S, Blair K A, Peterson D E, Kazmierczak J J, Addiss D G, Fox K R, Rose J B, Davis J P. A massive outbreak in Milwaukee of cryptosporidium infection transmitted through the public water supply. The New England Journal of Medicine, 1994, 331(3): 161–167 Linden K G, Shin G A, Faubert G, Cairns W, Sobsey M D. UV disinfection of Giardia lamblia cysts in water. Environmental Science & Technology, 2002, 36(11): 2519–2522 Shin G A, Linden K G, Arrowood M J, Sobsey M D. Low-pressure UV inactivation and DNA repair potential of Cryptosporidium parvum oocysts. Applied and Environmental Microbiology, 2001, 67(7): 3029–3032 von Gunten U. Ozonation of drinking water: part II. Disinfection and by-product formation in presence of bromide, iodide or chlorine. Water Research, 2003, 37(7): 1469–1487 Jung Y J, Oh B S, Kang J W. Synergistic effect of sequential or combined use of ozone and UV radiation for the disinfection of Bacillus subtilis spores.Water Research, 2008, 42(6-7): 1613–1621 Labatiuk C W, Belosevic M, Finch G R. Inactivation of Giardiamuris using ozone and ozone-hydrogen peroxide. Ozone Science and Engineering, 1994, 16(1): 67–78 Meunier L, Canonica S, von Gunten U. Implications of sequential use of UV and ozone for drinking water quality. Water Research, 2006, 40(9): 1864–1876 Wang X, Hu X, Wang H, Hu C. Synergistic effect of the sequential use of UV irradiation and chlorine to disinfect reclaimed water. Water Research, 2012, 46(4): 1225–1232 Walker G C. Mutagenesis and inducible responses to deoxyribonucleic acid damage in Escherichia coli. Microbiological Reviews, 1984, 48(1): 60–93 Friedberg E C, Walker G C, Siede W. DNA Repair and Mutagenesised. Washington, D C: ASM Press, 1995 Reisz E, Schmidt W, Schuchmann H P, von Sonntag C. Photolysis of ozone in aqueous solutions in the presence of tertiary butanol. Environmental Science & Technology, 2003, 37(9): 1941–1948 von Sonntag C. The Chemical Basis of Radiation Biology. London: Taylor & Francis, 1987 Wolfe R L, Stewart M H, Scott K N, McGuire M J. Inactivation of Giardia-muris and indicator organisms seeded in surface-water supplies by peroxone and ozone. Environmental Science & Technology, 1989, 23(6): 744–745 Cho M, Chung H, Choi W, Yoon J. Linear correlation between inactivation of E. coli and OH radical concentration in TiO2 photocatalytic disinfection. Water Research, 2004, 38(4): 1069–1077 Shang C, Cheung L M, Ho C M, Zeng M Z. Repression of photoreactivation and dark repair of coliform bacteria by TiO2-modified UV-C disinfection. Applied Catalysis B: Environmental, 2009, 89(3–4): 536–542 APHA-AWWA-WEF. Standard Methods for the Examination of Water and Wastewater. 20th ed. Washington, D C, USA: American Public Health Association/American Water Works Association/ Water Environment Federation, 1998 Shang C, Cheung LM, Liu W. MS2 coliphage inactivation with UV irradiation and free chlorine/monochloramine. Environmental Engineering Science, 2007, 24(9): 1321–1332 USEPA. Method 1602: Male-Specific (F +) and Somatic Coliphage in Water by Single Agar Layer (SAL) Procedureed. Washington, D C: United States Environmental Protection Agency, 2001 Rahn R O. Potassium iodide as a chemical actinometer for 254 nm radiation: use of iodate as an electron scavenger. Photochemistry and Photobiology, 1997, 66(4): 450–455