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Applied and Environmental Microbiology, September 2007, p. 5968-5970, Vol. 73, No. 18
0099-2240/07/$08.00+0 doi:10.1128/AEM.00347-07
Copyright © 2007, American Society for Microbiology. All Rights Reserved.

David E. John,2 and
Joan B. Rose1*
Department of Fisheries and Wildlife, Michigan State University, East Lansing, Michigan,1 College of Marine Science, University of South Florida, St. Petersburg, Florida2
Received 12 February 2007/ Accepted 23 July 2007
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Two reservoir and two aquifer waters (Bill Evers Reservoir and Avon Park well, Bradenton, FL, and Clear Lake Reservoir and Lake Lytal Park well, West Palm Beach, FL) were sampled in the summer and used for the seeded experiments. Both wells tap the Upper Floridan aquifer. Wells were purged of at least three well volumes prior to sampling. Table 1 shows the physiochemical measurements of the source water. Twenty-milliliter samples were distributed to 50-ml centrifuge tubes for each water type and temperature combination and were equilibrated to 5, 22, and 30°C prior to seeding with C. parvum (prepared as previously described [2]; Iowa isolate; Sterling Parasitology Laboratory, University of Arizona, Tucson, AZ). In the seeded waters, oocyst concentrations were 107 oocysts ml–1 by hemocytometer count and the initial infectious concentrations were between 103 and 104 infective oocysts ml–1 by the cell culture method (described below). Experiments were performed concurrently with oocysts from the same lot number to minimize differences attributed to oocyst age after shedding. C. parvum oocysts were used within 60 days of shedding from a calf. Tubes were covered to exclude light and were maintained at 5, 22, or 30°C in a refrigerator or in water baths. One-milliliter samples were analyzed in replicate at various dilutions for oocyst infectivity at 0, 1, 3, 6, 10, 20, and 25 days for each water sample at each temperature. Oocysts were assayed for infectivity on human ileocecal adenocarcinoma (HCT-8) cells (CCL-224; ATCC, Manassas VA) by using an indirect antibody focus detection method as previously described (7, 10). An EPA most probable number (MPN) program was used (http://www.epa.gov/nerlcwww/other.htm), and values were converted to percent infectivity by the following equation: (MPN ml–1/hemacytometer oocyst count ml–1 stock) x 100. Series data points for each experimental trial were converted to log10 N/N0 ratios, where N indicates the percent infectivity at time t and N0 indicates the initial percent infectivity, and fit to equation 1 to obtain inactivation rates per day:
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TABLE 1. Physiochemical measurements of raw water from the sample sites
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Table 2 shows first-order inactivation rates and predicted number of days to achieve a 2-log reduction. Inactivation rates ranged from +0.0088 log10/day at 5°C to –0.20 log10/day at 30°C. At 5°C over 25 days, the mean across all water types showed a slight (insignificant) positive trend, possibly due to variability in the assay and oocyst maturation (2). Higher temperatures led to a decrease in the predicted number of days to achieve a 2-log reduction (Table 2). The inactivation rate at 22°C for Avon Park was found to be lower than the rate for Lake Lytal (which was similar to that observed in surface water at 22°C). This result may be due to differences in well water composition, but this possibility was not evaluated. At 5°C, native biological activity is expected to be low, as is the oocyst inactivation rate. Thus, no variability in oocyst survival is seen. At 30°C, oocyst inactivation rates are higher and temperature seems to dominate the inactivation effects. At 22°C, native biological activity or the native microbial population may be a contributing factor of oocyst inactivation. Thus, differences between waters may be seen, particularly at this temperature. At 30°C, days for a 2-log reduction of infectious oocysts were 17 and 18 days in aquifer waters and 10 and 11 days in reservoir waters. At 22°C in surface water, 30 and 45 days were estimated for a 2-log reduction. In a previous study that used cell culture methods to assess the effects of temperature on oocyst infectivity in river water, the infectivity of the oocysts in unfiltered river water at 21 to 23°C decreased 2.6 log units by 12 weeks (approximately –0.031 log10/day) (8), which was slightly lower than the rate of inactivation (–0.045 to 0.066 log10/day) predicted for surface waters here. Differences may be due to water composition or method differences, as the previous study did not use an MPN method and assessed infectivity at weekly intervals. In a previous study of longer experimental duration, 66.7% of cryptosporidia in reagent-grade water at 4°C appeared nonviable by dye exclusion after 176 days (9), an approximately 0.48-log reduction (–0.0027 log10/day). This result is similar to that of the present study, which predicts C. parvum inactivation rates of –0.0017 log10/day to –0.0037 log10/day in surface water at 5°C, and is lower than the –0.010 log10/day inactivation rate previously reported at 5°C using excystation and dye exclusion (5).
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TABLE 2. First-order inactivation rates and predicted number of days to a 2-log decline of C. parvum in natural water trials
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The results of this study have implications for aquifer storage and recovery projects. It has been suggested that untreated surface waters (possibly containing Cryptosporidium) could be stored via aquifers for later recovery. The specific conditions, particularly temperature, need to be evaluated in order to better predict attenuation during subsurface storage. Storage time and differences in surface water and groundwater temperatures will produce both a gradient of conditions as waters mix and a range of inactivation rates. Thus, stochastic models are needed to better predict attenuation rates during aquifer storage of untreated waters.
Published ahead of print on 3 August 2007. ![]()
Present address: Center for Limnology, University of Wisconsin, Madison, WI 53706. ![]()
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