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Expanded Summary Assessing the risk of infectious Cryptosporidium in drinking water Pa ul A. R o che lle , Anne M . J o hns o n, Ri car do De L e o n , a n d G e o rg e D. D i G io v a n n i http://dx.doi.org/10.5942/jawwa.2012.104.0063 Treated drinking water from 14 surface water treatment plants serving a combined population of approximately 9 million people was monitored for infectious Crypto sporidium oocysts using immunofluorescence microscopy to detect infections in cell culture. No infectious oocysts were detected in 349,053 L from 370 samples. The calculated risk of waterborne Cryptosporidium infection based on the lack of positives, total volume sampled, and assumptions about daily volume of water consumption was < 1 in 10,000. However, further study to establish more accurate risk assessments of the threat to public health posed by Cryptosporidium in drinking water is still needed, because results from 14 plants cannot be extrapolated to the entire United States. This study demonstrated that routine infectivity monitoring of large volumes of treated drinking water is feasible. Consequently, testing finished water for infectious Cryptosporidium should be considered during periods of regulatory monitoring, such as the second round of the Long Term 2 Enhanced Surface Water Treatment Rule (LT2ESWTR). Waterborne cryptosporidiosis is a serious public health concern, but after two decades of research and monitoring, the water industry still does not have an accurate assessment of the risk to public health from Cryptospo ridium oocysts in drinking water. Although correctly operating filtration plants usually remove oocysts, the risk of infection depends on several factors, and there is uncertainty about the true public health burden from Cryptosporidium oocysts in drinking water. During monitoring for the Information Collection Rule, 1% of treated water samples contained Cryptospo ridium oocysts. However, accurately assessing the risk of waterborne cryptosporidiosis requires quantifying the prevalence of infectious oocysts in drinking water. In vitro cell culture combined with polymerase chain reaction detected infectious Cryptosporidium oocysts in 1.4% of finished water samples from 82 conventional US treatment plants (Aboytes et al, 2004). The results translated to an annual cryptosporidiosis risk of 52 infections per 10,000 people, which is much higher than the 1 in 10,000 risk of infection goal set by the US Environmental Protection Agency. However, more data on the prevalence of infectious Cryptosporidium oocysts in drinking water are needed. The objective of this study was to assess the prevalence of infectious oocysts in large-volume samples of treated water using a cell culture assay. Three of these plants used lakes as source waters; the remainder used rivers. Filters were shipped to the two cell culture–processing laboratories by overnight courier in coolers containing ice packs. Samples were concentrated using method 1623 (USEPA, 2005) modified for large volumes of finished water and to allow for infectivity analysis by cell culture. The final magnetic bead–oocyst complex was dissociated in an acidified salt solution containing 1% trypsin. Concentrates were inoculated onto HCT-81 human cell culture monolayers and incubated at 37°C for 64–72 h in a 5% carbon dioxide–humidified incubator. Infections were detected by applying an antiCryptosporidium sporozoite antibody and observed by epifluorescence microscopy (Figure 1; Johnson et al, 2012). METHODS Treated drinking water samples from 14 plants throughout the United States were filtered onsite by utility personnel. A full report of this project, Detection of Infectious Cryptosporidium in Conventionally Treated Drinking Water (3021), is available for free to Water Research Foundation subscribers by logging on to www.waterrf.org. RESULTS AND DISCUSSION Two laboratories analyzed 370 samples of treated water over a two-year period. Sample volumes ranged from 84 to 2,282 L, with an average of 943 L for a total volume of 349,053 L. None of the treated water samples produced infections. Positive control infections, matrix spike recovery studies with samples from all participating utilities, blind matrix spikes, and infections with naturally occurring oocysts in wastewater all demonstrated that the oocyst recovery and cell culture procedures performed as expected and should have detected infectious oocysts if present. The mean recovery efficiency for matrix spikes using freshly shed infectious oocysts and processed through the entire procedure, including cell culture, was 80% (n = 51). The absence of infectious oocysts in these samples may reflect improved source water protection and optimization of treatment processes. Recruiting utilities for the study proved difficult because of concerns over the potential consequences of a ROCHELLE ET AL | 104:5 • JOURNAL AWWA | MAY 2012 2012 © American Water Works Association 79 positive result. The treated water survey was conducted during the period covered by Cryptosporidium monitoring under the LT2ESWTR for Schedule 1 utilities. Consequently, there was heightened sensitivity to Cryptospo ridium-related issues among utility personnel, highlighting the difficulty of conducting research studies when there are potential regulatory, public health, legal, and public relations consequences associated with a positive result. It is likely that the participating utilities did not anticipate many positive samples. A different group of utilities with a broader diversity of water quality characteristics, greater vulnerability of their source waters to contamination, and less rigorous treatment procedures and controls might have produced some positive samples. The 24 positive samples detected in the Aboytes et al (2004) study translated to an annual cryptosporidiosis risk of 52 infections per 10,000 people. In the current study, zero detection of infectious oocysts in 349,053 L equated to an annual risk of < 1 in 10,000, suggesting that the risk of Cryptosporidium infection from drinking water produced by correctly operating treatment plants may be lower than previously estimated. Much larger volumes were analyzed in the current study, but the earlier study examined many more samples, which may have increased the likelihood of capturing infectious oocysts. Therefore, the number of plants, number of samples, and total volume analyzed must be considered in any followup infectious Cryptosporidium monitoring programs to ensure statistically relevant results. The diversity of Cryptosporidium species and genotypes that can infect HCT-8 cells and be detected using immunofluorescence is unknown, although the cell culture–immunofluorescence procedure used in the current study detected infection of HCT-8 cells by C. parvum, C. hominis, and C. meleagridis oocysts. Therefore, from a public health perspective, the method detects the most important human-infectious species. infection (Aboytes et al, 2004). In the current study, using a similar oocyst recovery method but larger volumes of water from fewer treatment plants and a different infection-detection assay, no infectious oocysts were detected. This absence of infectious oocysts resulted in a calculated cryptosporidiosis risk of < 1 in 10,000. The results of this study highlight the difficulty of detecting rare events in treated drinking water that usually meets infection-risk goals. However, the results from 14 plants—treating source waters with low oocyst concentrations—cannot be extrapolated to the entire country. Clearly, better estimates are needed to accurately assess the threat to public health posed by Cryptosporidium in drinking water. Incorporating a cell culture–based infectivity method into routine and widespread monitoring programs for all utilities is not practical because of the low prevalence of infectious oocysts resulting in a high proportion of negative samples, and the labor and cost of analyzing samples. However, during the past decade, in vitro cell culture has gained wider acceptance as a practical method for assessing infectivity of Cryptosporidium. This study demonstrated that routine infectivity monitoring of large volumes of treated water is possible; therefore, the method could be used to analyze finished water from selected treatment plants during periods of regulatory monitoring such as the second round of monitoring under the LT2ESWTR. Monitoring is required to determine whether infectious oocysts are always present at low levels in all treated water, sometimes present in all treatment plant effluents, or only sometimes present in a fraction of plant effluents. Acknowledgment The authors gratefully acknowledge funding from the Water Research Foundation and thank all participating utilities that provided filtered samples, water quality data, and source water oocyst data. CONCLUSIONS FOOTNOTE A previous study on the prevalence of infectious Crypto sporidium in treated water concluded that conventional water treatment does not adequately control the risk of References FIGURE 1 Infectious foci (intracellular life stages) of Cryptosporidium hominis (part A) and Cryptosporidium parvum (part B) in HCT-8 cell cultures detected by immunofluorescence microscopy A B 1ATCC CCL-244 cell line, American Type Culture Collection, Manassas, Va. Aboytes, A.; Di Giovanni, G.D.; Abrams, F.A.; Rheinecker, C.; McElroy, W.; Shaw, N.; & LeChevallier, M.W., 2004. Detection of Infectious Cryptosporidium in Filtered Drinking Water. Jour. AWWA, 90:9:88. Johnson, A.M.; Di Giovanni G.D.; & Rochelle, P.A., 2012. Comparing Assays for Sensitive and Reproducible Detection of Cell Cultureinfectious Cryptosporidium parvum and Cryptosporidium hominis in Drinking Water. Appl. & Envir. Microbiol., 78:156.http://dx.doi. org/10.1128/AEM.06444-11. USEPA (US Environmental Protection Agency), 2005. Method 1623 for Detection of Cryptosporidium and Giardia in Water. EPA 815-R-05002, Ofce. of Water, Washington. Corresponding author: Paul A. Rochelle is the Source Water Microbiology Team manager, Metropolitan Water District of Southern California, 700 Moreno Ave., La Verne, CA 91750; [email protected]. Scale bar = 100 µm. 80 MAY 2012 | JOURNAL AWWA • 104:5 | ROCHELLE ET AL 2012 © American Water Works Association