PEDIATRICS Vol. 108 No. 4 October 2001, p. e59
ELECTRONIC ARTICLE:
Hemolytic-Uremic Syndrome and Escherichia coli
O121 at a Lake in Connecticut, 1999
Received Mar 30, 2001; accepted May 24, 2001.
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From the * Epidemic Intelligence Service, assigned to the
Connecticut Department of Public Health, Epidemiology Program Office,
Centers for Disease Control and Prevention, Atlanta, Georgia;
Objective. Non-O157 Shiga
toxin-producing Escherichia coli (STEC) have emerged as
an important public health problem. Outbreaks attributed to non-O157
STEC rarely are reported. In 1999, follow-up of routine surveillance
reports of children with hemolytic- uremic syndrome (HUS) identified a
small cluster of 3 cases of HUS, all of whom had spent overlapping time
in a Connecticut lake community in the week before onset of symptoms.
We conducted an investigation to determine the magnitude and source of
the outbreak and to determine risk factors associated with the
transmission of illness.
Methods. We conducted a cohort study and an environmental
investigation. The study population included all people who were at the
lake in a defined geographic area during July 16-25, 1999. This time and area were chosen on the basis of interviews with the 3 HUS case-patients. A case was defined as diarrhea ( Results. Information was obtained for 436 people from 165 (78%) households. Eleven (2.5%) people had illnesses that met the
case definition, including the 3 children with HUS. The attack rate was
highest among those who were younger than 10 years and who swam in the lake on July 17 or 18 (12%; relative risk [RR]: 7.3). Illness was
associated with swimming (RR = 8.3) and with swallowing water while swimming (RR = 7.0) on these days. No person who swam only after July 18 developed illness. Clinical characteristics of
case-patients included fever (27%), bloody diarrhea (27%), and severe
abdominal cramping (73%). Only the 3 children with HUS required
hospitalization. No bacterial pathogen was isolated from the stool of
any case-patient. Among lake residents outside the study area, E
coli O121:H19 was obtained from a Shiga toxin-producing
isolate from a toddler who swam in the lake. Serum was obtained from 7 of 11 case-patients. Six of 7 case-patients had E coli
O121 antibody titers that ranged from 1:320 to >1:20 480. E
coli indicative of fecal contamination was identified from
sediment and water samples taken from a storm drain that emptied into
the beach area and from a stream bed located between 2 houses, but no
Shiga toxin-producing strain was identified.
Conclusions. Our findings are consistent with a transient
local beach contamination in mid-July, probably with E
coli O121:H19, which seems to be able to cause severe illness.
Without HUS surveillance, this outbreak may have gone undetected by
public health officials. This outbreak might have been detected sooner
if Shiga toxin screening had been conducted routinely in HUS cases.
Laboratory testing that relies solely on the inability of an isolate to
ferment sorbitol will miss non-O157 STEC, such as E coli
O121. Serologic testing can be used as an adjunct in the diagnosis of
STEC infections. Lake-specific recommendations included education,
frequent water sampling, and alternative means for toddlers to use lake
facilities.
Connecticut Department of Public Health, Epidemiology Program,
Hartford, Connecticut; § East Haddam Health Department, East Haddam,
Connecticut;
Connecticut Department of Public Health, Laboratory
Division, Hartford, Connecticut; ¶ Connecticut Agricultural Experiment
Station, New Haven, Connecticut; and # National Center for Infectious
Disease, Centers for Disease Control and Prevention, Atlanta, Georgia.
3 loose stools/d for
3 days) in a person who was at the lake during July 16-25, 1999. Stool samples were requested from any lake resident with diarrheal
illness. Stools were cultured for Salmonella,
Shigella, Campylobacter, and E
coli O157. Broth cultures of stools were tested for Shiga
toxin. Case-patients were asked to submit a serum specimen for antibody
testing to lipopolysaccharides of selected STEC. Environmental samples
from sediment, drinking water, lake water, and ice were obtained and
cultured for E coli and tested for Shiga toxin. An
environmental evaluation of the lake was conducted to identify any
septic, water supply system, or other environmental condition that
could be related to the outbreak.




