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Chlorine Inactivation of Escherichia coli O157:H7.

We analyzed isolates of Escherichia coli O157:H7 (which has recently caused waterborne outbreaks) and wild-type E. coil to determine their sensitivity to chlorination. Both pathogenic and nonpathogenic strains were significantly reduced within 1 minute of exposure to free chlorine. Results indicate that chlorine levels typically maintained in water systems are sufficient to inactivate these organisms.

Escherichia coli O157:H7 is becoming increasingly recognized as a waterborne pathogen. Two recent outbreaks during summer 1998, one involving a drinking water supply in Wyoming (1) and another involving recreational water exposure at a water park in Georgia (2), have underscored the role of water in transmission. Contaminated drinking water (3,4) and recreational water have been associated with outbreaks of hemorrhagic colitis caused by E. coli O157:H7 (5-7). Chlorination of water is one of the primary public health measures used to ensure that both potable water and water used in recreational settings are free of microbial pathogens. Our study was undertaken to determine the chlorine resistance of E. coli O157:H7 and compare this resistance with that of wild-type E. coli.

Seven strains of E. coli O157:H7, isolated from cattle from geographically distinct areas (Florida, Idaho, Illinois, Missouri, Texas, Washington, and Wisconsin), were obtained from the U.S. Department of Agriculture (D. Miller, Ames, IA). The isolates exhibited the characteristic phenotypic traits: sorbitol-negative, [Beta]-glucuronidase-negative, lactose-positive, indolepositive, and positive for glutamate decarboxylase (8). All enterohemorrhagic isolates were active toxin producers, as determined by in vitro enzyme immunoassay (Meridian Diagnostics, Inc., Cincinnati, OH). These cattle isolates were chosen as representative strains that might contaminate water supplies after surface run-off from pastures and fields. Four wild-type E. coli isolates from cattle manure from a local dairy farm (Ohio) were characterized by biochemical test kits (bioMerieux Vitek, Hazelwood, MO). All bacterial cultures used in the disinfection experiments were grown for 18 to 20 hours at 35 [degrees] C in brain heart infusion broth, concentrated by centrifugation, and washed three times in phosphate buffer (9) before testing.

The results of the disinfection experiments, including the rates of inactivation, are shown in the Table. Initial levels for all isolates were 5.52 to 5.79 [log.sub.10] CFU/ml. The mean chlorine levels at each exposure time were 1.1 mg/L free chlorine and 1.2 mg/L total chlorine. For both the pathogenic and the wild-type strains, exposure to these levels of chlorine for 1 minute reduced the viable populations by approximately four orders of magnitude.

The inactivation rates and corresponding correlation coefficient ([r.sup.2]) values are listed in the Table. Little difference was observed in the rates of inactivation for the pathogenic and wild-type organisms.

Table. Chlorine inactivation of Escherichia coli O157:H7 and wild-type E. coli(a)
 [Log.sub.10]CFU/ml

 After exposure time of

 Initial 120
Isolate inoculum 30 sec 60 sec sec

E. coli
O157:H7
 N009-6-1 5.63 2.60 1.88 0.82
 N6001-8-10 5.78 2.52 1.44 0.72
 N6021-5-1 5.78 2.54 1.52 0.66
 N60049-26-1 5.68 2.35 1.40 0.54
 N6059-7-2 5.72 2.42 1.74 0.86
 N6104-5-9 5.62 2.40 1.69 0.72
 N6114-7-2 5.63 2.52 1.66 0.89
 Mean 5.69 2.48 1.62 0.74
E. coli (wild
type)
 A 5.53 2.66 1.80 1.52
 B 5.79 2.60 1.48 0.81
 C 5.68 2.48 0.92 0.84
 D 5.52 2.34 0.95 0.39
 Mean 5.63 2.52 1.28 0.89

 Inactivation
 rate
Isolate ([sec.sup.-1]) [r.sup.2]

E. coli
O157:H7
 N009-6-1 -2.96 0.82
 N6001-8-10 -3.06 0.68
 N6021-5-1 -3.06 0.54
 N60049-26-1 -3.00 0.86
 N6059-7-2 -3.02 0.72
 N6104-5-9 -2.96 0.89
 N6114-7-2 -2.96 0.82
 Mean -2.93 0.82
E. coli (wild
type)
 A -2.51 0.61
 B -2.68 0.60
 C -2.61 0.61
 D -2.50 0.61
 Mean -2.93 0.71


(a) In chlorine demand-free chlorinated (CDF) buffer, 5 [degrees]C, pH 7.0, 1.1 mg/L free chlorine, 1.2 mg/L total chlorine. Duplicate chlorine inactivation experiments were conducted in CDF buffer at pH 7.0. All experiments were conducted at 5 [degrees] C in a recirculating, refrigerated water bath. The chlorinated buffer was prepared by the addition of reagent-grade sodium hypochlorite (Fisher Scientific, Fair Lawn, NJ). Reaction vessels were continuously mixed (250 rpm) by using an overhead stirring apparatus equipped with sterile stainless steel paddles. Chlorine concentrations were determined by the N,N-dimethyl-p-phenylenediamine colorimetric method (9). Samples were removed from the reaction vessels at the desired exposure times, and the chlorine was immediately neutralized by the addition of 0.5 ml of 10% (wt/vol) sodium thiosulphate. Vessels containing CDF buffer without chlorine served as controls for determining unexposed concentrations of the bacteria. Initial levels and the number of survivors after chlorine exposure were determined by the membrane filtration procedure using mT7 agar incubated for 22 to 24 hours at 35 [degrees] C. This medium was chosen because of its ability to recover oxidant-stressed organisms (9). Levels of bacteria were determined by duplicate filtrations of appropriate dilutions for each exposure time. The [log.sub.10]-transformed data were used to determine the levels of inactivation for each isolate. The means for the inactivation data for the E. coli O157:H7 isolates and for the wild-type E. coli isolates at each exposure time were used to compare the inactivation rates between the pathogenic and the wild-type organisms. The following first order model was used to described the inactivation rate: y = [y.sub.10][10.sup.-at], where t = time in seconds, y = CFU/ml at any time t, [y.sub.10] = CFU/ml at time zero, and a = the inactivation rate in [sec.sup.-1]. The log transformation of this equation was used to calculate the inactivation rate. A regression analysis using least squares was conducted for experiments with each individual isolate and for the mean values for each of the two types of isolates (serotype O157 and wild-type) to determine the inactivation rates ("a" values).

These results indicate that the E. coli O157:H7 isolates used in this study were sensitive to chlorination and were similar in resistance to that of wild-type E. coli isolates. The biocidal activity of chlorine decreases with decreasing temperature (not done in this study). The 5 [degrees] C temperature we used represents a worst-case condition for both ground water or winter surface-water temperature. A survey of disinfection practices in the United States found that water utilities maintain a median chlorine residual of 1.1 mg/L and a median exposure time of 45 minutes before the point of first use in the distribution system (10). At this level of chlorination, E. coli O157:H7 is unlikely to survive conventional water treatment practices in the United States. E. coil O157:H7 survives at a similar rate to that of wild-type E. coli in nondisinfected drinking water (11). Survival patterns and sensitivity to chlorination previously observed for the strains used in this study suggest that wild-type E. coli could serve as an adequate indicator organism for fecal contamination of water. Using wild-type E. coli to indicate E. coli O157:H7 would be useful because most analytical procedures for detecting E. coli in drinking water (e.g., assays for lactose fermentation at 44 [degrees] C to 45 [degrees] C or production of the enzyme [Beta]-glucuronidase) cannot detect pathogenic E. coli O157:H7 strains (8).

Although chlorination appears to adequately control this pathogen, not all municipal water supplies use chlorine disinfection. In addition, chlorine residual can dissipate under adverse conditions, and exposure to sunlight or organic chlorine-demand substances can greatly diminish chlorine levels. Protection of organisms associated with particulate matter, such as fecal material, can also readily decrease the biocidal activity of chlorine. These considerations are particularly important in determining the efficacy of chlorination in a recreational water setting. The results of this study indicate that the isolates studied were sensitive to chlorination. Evaluation of other isolates under differing environmental conditions would be worthy of further consideration.

Acknowledgment

We thank Dr. Robert V. Tauxe for his encouragement and guidance regarding this project.

References

(1.) Olsen J, Miller G, Breuer T, Kennedy M, Higgins C, McGee G, et al. A waterborne outbreak of E. coli O157:H7 infections: evidence for acquired immunity. In: Program and Abstracts of the 36th Annual Meeting of Infectious Diseases Society of America, Denver, Colorado; 1998 Nov 12-15; [abstract 782]. Alexandria (VA): Infectious Disease Society of America; 1998. p. 62.

(2.) Blake P. Escherichia coli O157:H7 outbreak among visitors to a water park. In: Program and Abstracts of the 36th Annual Meeting Infectious Diseases Society of America, Denver, Colorado; 1998 Nov 12-15; [abstract 537]. Alexandria (VA): Infectious Diseases Society of America; 1998. p. 178.

(3.) Swerdlow DL, Woodruff BA, Brady RC, Griffin PM, Tippen S, Donnell HD, et al. A waterborne outbreak in Missouri of Escherichia coli O157:H7 associated with bloody diarrhea and death. Ann Int Med 1992;117:812-19.

(4.) Dev VJ, Main M, Gould I. Waterborne outbreak of Escherichia coli O157. Lancet 1991;337:412.

(5.) Ackman D, Marks S, Mack P, Caldwell M, Root T, Birkhead G. Swimming-associated hemorrhagic colitis due to Escherichia coli O157:H7 infection: evidence of prolonged contamination of a fresh water lake. Epidemiol Infect 1997; 119:1-8.

(6.) Brewster DH, Brown MI, Robertson D, Houghton GL, Bimson J, Sharp JCM. An outbreak of Escherichia coli O157 associated with a children's paddling pool. Epidemiol Infect 1994; 112:441-7.

(7.) Keene WE, McAnulty JM, Hoesly FC, Williams LP Jr, Hedberg K, Oxman GL, et al. A swimming-associated outbreak of hemorrhagic colitis caused by Escherichia coli O157:H7 and Shigella sonnei. N Engl J Med 1994;331:579-84.

(8.) Rice EW, Johnson CH, Reasoner DJ. Detection of Escherichia coli O157:H7 in water from coliform enrichment cultures. Lett Appl Microbiol 1996;23:179-82.

(9.) American Public Health Association. Standard methods for the examination of water and wastewater. 19th ed. Washington: The Association; 1995.

(10.) Water Quality Disinfection Committee. Survey of water utility disinfection practices. J Am Water Works Assoc 1992;84:121-8.

(11.) Rice EW, Johnson CH, Wild DK, Reasoner DJ. Survival of Escherichia coli 0157:H7 in drinking water associated with a waterborne disease outbreak of hemorrhagic colitis. Lett Appl Microbiol 1992; 15:38-40.

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This page last reviewed July 1, 1999

Emerging Infectious Diseases Journal National Center for Infectious Diseases Centers for Disease Control and Prevention

URL: http://www.cdc.gov/ncidod/eid/vol5no3/rice.htm

Eugene W. Rice, Robert M. Clark, and Clifford H. Johnson U.S. Environmental Protection Agency, Cincinnati, Ohio, USA

Dr. Rice is a microbiologist in the Microbial Contaminants Control Branch, Water Supply and Water Resources Division, National Risk Management Research Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio. His research focuses on detection and inactivation of waterborne pathogens and microbial indicator organisms.

Address for correspondence: Eugene W. Rice, U.S. Environmental Protection Agency, 26 West M.L. King Dr., Cincinnati, OH 45268, USA; fax: 513-569-7328; e-mail: rice.gene@epa.gov.
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Author:Johnson, Clifford H.
Publication:Emerging Infectious Diseases
Geographic Code:1USA
Date:May 1, 1999
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