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Applied and Environmental Microbiology, February 2003, p. 1325-1326, Vol. 69, No. 2
0099-2240/03/$08.00+0 DOI: 10.1128/AEM.69.2.1325-1326.2003
Copyright © 2003, American Society for Microbiology. All Rights Reserved.
U.S. Environmental Protection Agency, Cincinnati, Ohio 45268,1 Sterling Parasitology Laboratory, University of Arizona, Tucson, Arizona 857212
Received 27 February 2002/ Accepted 13 November 2002
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E. cuniculi (ATCC 50502), E. hellem (ATCC 50451), and E. intestinalis (ATCC 50603) were propagated in monolayers of RK-13 (ATCC CCL-37) rabbit kidney cells incubated at 35°C in a humid atmosphere of 5% CO2 as previously described (7). The spores were harvested by removing the culture medium from the cell monolayers and concentrated by centrifugation at 1,000 x g for 10 min. The supernatant was removed by aspiration, and the spore pellet was further purified by differential density gradient centrifugation by using an isopycnic Percoll (Amersham Pharmacia Biotech, Piscataway, N.J.) gradient and a final wash step using reagent grade water (7). The concentration of spores was determined by counting with a hemacytometer, and the stock preparations were stored at 4°C in reagent grade water. Spore preparations were used within 1 week of harvesting. Spores from individual species were used in the inactivation experiments.
TCID50s were determined by using a logit dose-response model (5) to describe the dose-response relationship between the tissue culture wells and the Encephalitozoon sp. spores. Briefly, the response logit (RL) value was calculated for each inoculum of spores as the natural logarithm (ln) of the proportion of infected tissue culture wells (P) divided by 1 minus the proportion of inoculated wells {RL = ln[P/(1 - P)]}. The RL values were treated as dependent variables (y) for linear regression analysis with the logarithm (log10) of the number of spores in each dose serving as the independent variable (x). Regression analysis was then used to perform a least-squares regression to calculate the regression model and parameters. The logit models were used to calculate the TCID50 for each species and to determine the number of infective spores remaining in each inoculum after disinfectant treatment.
Inactivation experiments were conducted at 23 ± 2°C in chlorine demand-free (CDF) 0.05 M potassium dihydrogen phosphate buffer adjusted to pH 7.0 as previously reported (4). The reaction vessels used were 400-ml beakers containing 90 ml of CDF buffer. Reagent grade sodium hypochlorite was added to each beaker to achieve the desired level of chlorine prior to the addition of spores. An inoculum (10 ml) containing 107 spores was added to each reaction vessel at time zero. During the course of the experiments, the reaction vessel contents were continuously mixed with a magnetic stirring device. Ten-milliliter samples were removed from the reaction vessels at the desired exposure times, and the chlorine was immediately neutralized by the addition of 0.1 ml of 10% (wt/vol) sodium thiosulfate. Chlorine levels were determined initially and at each exposure time by the N,N-dimethyl-p-phenylenediamine colorimetric method (1). Vessels containing CDF buffer without chlorine served as controls for the unexposed spores and were treated in the same manner as the chlorine-exposed samples. Addition of sodium thiosulfate to the control vessel did not have a deleterious effect on the spores. The logit dose-response regression model (5) was used to determine the number of viable spores after chlorine treatment. The log10 reduction (LR) was determined by subtracting the number (log10) of viable spores remaining after treatment (N) from the total number (log10) of spores in the initial inoculum (N0) (LR = log10N - log10N0).
The TCID50 shown in Table 1 were determined by using the mean number of infected tissue culture wells at the various dilutions. Since the logit expressions for 0 and 100% infectivity are undefined, they were not used in the calculations. The calculated TCID50 for E. cuniculi was 15 spores; for E. hellem, it was 68 spores, and for E. intestinalis, it was 27 spores. The results of the chlorine inactivation experiments are shown in Table 2. The chlorine level at the beginning of each experiment was 2.5 ± 0.2 mg liter-1. The spore preparations exerted an initial rapid chlorine demand, and the residual chlorine level at the end of each exposure time was 2.0 ± 0.2 mg liter-1. E. hellem showed a greater degree of resistance than the other two species at the shorter exposure times. However, all three species were inactivated by 4 orders of magnitude or more after an exposure time of 6 to 8 min, equating to a simple Ct value (Ct = disinfectant concentration [milligrams per liter] x exposure time [minutes]) of 16 mg-min liter-1.
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TABLE 1. Infectivity of spores of Encephalitozoon spp. inoculated on monolayers of rabbit kidney cells (RK-13)
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TABLE 2. Chlorine inactivation of spores of Encephalitozoon spp.a
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