Cryptosporidiosis outbreak in Ireland linked to public water supply, 2002

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1 Cryptosporidiosis outbreak in Ireland linked to public water supply, 2002 Item type Authors Article Health Service Executive (HSE) Midland Department of Public Health Publisher Eurosurveillance Vol 6 (22) 30 May 2002 Journal Eurosurveillance Downloaded 7-Jun :12:10 Link to item Find this and similar works at -

2 Page 1 of 4 Back to Table of Contents Next Eurosurveillance, Volume 6, Issue 22, 30 May 2002 Articles Citation style for this article: Jennings P, Rhatigan A. Cryptosporidiosis outbreak in Ireland linked to public water supply. Euro Surveill. 2002;6(22):pii=2089. Available online: Cryptosporidiosis outbreak in Ireland linked to public water supply The Department of Public Health and Planning of the Midland Health Board in the Republic of Ireland noted an increase in the number of cases of Cryptosporidium reported by the laboratory in one region of the Board in April-May 2002 (this laboratory normally reports between zero and two cases each month). Of thirteen cases, eight were found to be linked to the same water supply. Pending investigations, and in consultation with the local authority who are responsible for the water supply, a boil water notice was issued (3 May 2002) to the users of the water. In addition, the Health Board directly contacted general practitioners, hospitals, nursing homes, pharmacists, dentists, food premises, public houses, and schools to inform them of the outbreak. All confirmed cases were interviewed using a questionnaire modified for the investigation of cryptosporidiosis. Analysis was performed using the computer programme Epi-Info (version 6.04d; Centers for Disease Control and Prevention, Atlanta). The case definition was an individual with laboratory confirmed cryptosporidiosis from 1 April 2002 onwards who lived in the area supplied by this water source. Environmental investigation The water source was a spring-fed lake, serving a population of about The water was chlorinated but not filtered. The area surrounding the lake is predominantly farmland. A risk assessment of the water distribution system, and laboratory testing of the water for contamination, were undertaken. Rainfall statistics were obtained from the local meteorological office. Microbiological investigation Doctors in the area were informed of the outbreak and encouraged to submit samples from patients with diarrhoea. Environmental Health and Area Medical Officers distributed stool sample kits to symptomatic individuals and to family members of patients with diarrhoea. Stools were examined by fluorescent microscopy (modified auramine phenol stain) and solid phase immunoassay (SPIA) and confirmed on cold Ziehl Nielsen stain. (The laboratory was carrying out a trial of an SPIA method.) Conflicting results were resolved using an immunofluorescence method. Eight positive samples were sent to the Public Health Laboratory Service's Cryptosporidium Reference Unit at Swansea in the United Kingdom (UK) for genotyping. Results

3 Page 2 of 4 Twenty nine cases of cryptosporidiosis were confirmed by 16 May Twenty four cases (50% male, 50% female) were in the catchment area of the lake, and thus fulfil the case definition. Ages of cases ranged from 11 months to 38 years. Five cases were from outside the catchment area. There were a further seven unconfirmed cases. Three confirmed cases were admitted to hospital. The date of onset of symptoms is shown in the figure below : Figure: date of onset of illness Environmental investigation Grab samples from the water distribution network were taken and sent for testing (2 May). Cryptosporidium oocysts were detected in one of the samples (domestic tap) (1 oocyst/10 litre). A 430 litre continuous filter sample was taken from the lake (4 May) - the filter was sent for analysis. This was positive for Cryptosporidium (1.4 oocysts/10 litre). A further filter sample (8 May) was also positive (2.4oocyst/10 litre). Water samples were sent for typing, and the results are awaited. A risk assessment of the water distribution system and surrounding area identified a number of farming practices which could have resulted in contamination of the water source with farmyard slurry and farmyard manure. Environmental samples taken at a number of sites were positive for Cryptosporidium. Examination of meteorological data showed a period of dry weather followed by very heavy rains. These heavy rains would have facilitated the ingress of animal excrement into the lake. Microbiological investigation Twenty four stool samples were positive for Cryptosporidium. Eighteen of 24 (75%) were from patients aged 5 years or under. Genotyping identified that seven of eight stool samples were type 2. We are awaiting the results of the eighth sample. Discussion Using an algorithm developed by the Public Health Laboratory Service in the UK, this outbreak of gastroenteritis can be graded as being strongly associated with water. Cryptosporidium oocysts were detected in the raw and treated water, and in the environment surrounding the lake. The weather conditions helped to further explain how the lake became contaminated, and the descriptive epidemiology demonstrates a link between drinking water and becoming ill (1). Cryptosporidium parvum is the main pathogen associated with mains water in England and Wales (2). The difficult detection of Cryptosporidium oocysts in water is due to the small size of the oocysts (4-6 mm) and their relatively low concentration (3). The number of oocysts in faecal

4 Page 3 of 4 specimens may fluctuate thus making it difficult to identify (4). The Bouchier report in the UK emphasised that outbreaks of waterborne cryptosporidiosis do not happen spontaneously but result from inadequacies in water treatment (3). Cryptosporidium is a coccidial protozoan parasite found in humans, in many animals and in birds and fish. The parasite multiplies in the gastrointestinal tract of the host, which then excretes the oocysts of the parasite in its faeces (5). The oocysts are shed in very large numbers. Infected calves, for example, can shed approximately 1010 oocysts daily for up to 14 days. As a result, contamination of the environment can reach a very high level in a short period of time (3). Although cryptosporidial infections are widespread in animals, outbreaks of the infection usually originate from calves or lambs, and these are likely to form the most important reservoir of infection for humans. In healthy individuals cryptosporidiosis is an important cause of self-limiting but unpleasant diarrhoeal disease. In patients with suppressed immune systems, the disease can be much more serious (5). It is thought that the number of oocysts needed to cause infection is small, possibly fewer than 10. Outbreaks have also been associated with drinking water, recreational use of water including waterslides, swimming pools and lakes (5) and contact with a pet farm (6). Waterborne transmission is important because if the mains water becomes contaminated, large numbers of people are exposed, and many cases of cryptosporidiosis may occur in the area of supply. Soil contaminated with human or animal faeces and the water that drains through it to rivers, streams and shallow underground wells are potential sources of cryptosporidial infection. Surface water is generally more vulnerable to faecal contamination than ground water. The oocysts of Cryptosporidium are very resistant to adverse factors in the environment and can survive dormant for months in cool, dark conditions in moist soil or in clean water (3). Cryptosporidia are not killed by chlorination (5). Physical removal of the parasite from contaminated water by filtration is an important part of the water treatment process (3). Ultraviolet or other radiation could prove helpful (3, 7). Linking cryptosporidiosis infection to drinking water can be difficult as the contamination event may be over by the time the illness comes to light (3). In the UK, water utilities are obliged to undertake risk assessments for cryptosporidiosis and if a treatment works or supply zone is assessed as being of moderate/high risk, continuous monitoring is required with water analysis being undertaken by an accredited laboratory. No numerical standard for Cryptosporidium is set in the revised EU Drinking Water Directive (98/83/EC). The Directive refers to Clostridium perfringens. If Clostridium is detected, the Member State must investigate the supply to ensure that there is no potential danger to human health arising from the presence of pathogenic microorganisms e.g. Cryptosporidium (8). Cryptosporidiosis is can also be transmitted by the faecal-oral route either from animal to human or person to person. The disease is most prevalent in children aged between one and five years, especially those in schools, nurseries, and other childcare facilities. Conclusion This is the first reported outbreak in the Republic of Ireland of cryptosporidiosis associated with a public water supply. Routine monitoring does not include testing for Cryptosporidium or a potential indicator organism, for example, Clostridium perfringens. A number of water supplies do not have filtration systems. The true incidence of cryptosporidiosis in Ireland is not known. Laboratories have different policies on the examination of stool specimens for Cryptosporidium. It is not listed as a notifiable disease. Gastroenteritis in children under two years is notifiable. The National Disease Surveillance Centre (NDSC) receives data on notifiable infectious diseases from around Ireland. Cryptosporidiosis accounts for approximately 8% of laboratory-confirmed cases notified in this age group to NDSC. Data from the Infoscan Laboratory Surveillance System, which covers three of the eight health boards/authorities and a population of approximately 1.2 million shows that there are an average of 121 reported cases per annum of cryptosporidiosis, a reported rate of 10.1/ population. Data from the Laboratory Surveillance System which covers one Regional Health Authority ( l ti i t l 1 3 illi ) h i id f t idi i f 1 0/

5 Page 4 of 4 (population approximately 1.3 million) shows an incidence for cryptosporidiosis of 1.0/ population, with the highest rate in the 0-4 year age group at 9.9/ This outbreak is still ongoing. Cases are still being reported. Water testing is continuing and remedial measures for farming practices have been undertaken in relation to the environmental findings. The local authority is planning to implement a filtration system. The work of the Area Medical Officers, Environmental Health Officers, Laboratory Staff, Surveillance Scientist, Specialist Registrar and staff of the Department of Public Health and Planning, Midland Health Board in the investigation of this outbreak is acknowledged. References : 1. CDSC. Strength of association between human illness and water: revised definitions for use in outbreak investigations. Commun Dis Rep CDR Wkly 1996; 6(8): 65. ( 2. CDSC. Waterborne cryptosporidiosis. Commun Dis Rep CDR Wkly 1998; 49: 434. ( 3. Bouchier I, et al. Cryptosporidium in water supplies. Third Report of the Group of Experts to: Department of the Environment, Transport and the Regions & Department of Health; ( 4. Murray PR, Rosenthal KS, Kobayashi GS, Pfaller MA. Medical microbiology. 4th ed. St Louis: Mosby; Chin J. Control of Communicable Diseases Manual. Washington: American Public Health Association; Sayers GM, Dillon MC, Connolly E, Thornton L, Hyland E, Loughman E, et al. Cryptosporidiosis in children who visited an open farm. Commun Dis Rep CDR Rev 1996; 6: R ( 7. Kosek M, Alcantara C, Lima AAM, Guerrant RL. Cryptosporidiosis: an update. Lancet Infectious Diseases 2001; 1: Council of the European Union. Directive 98/83/EC on the quality of water intended for human consumption. Official Journal of the European Communities 1998; 330: (5 December) (click here) Reported by Phil Jennings (phil.jennings@mhb.ie) and Annette Rhatigan, Department of Public Health and Planning, Midland Health Board, Ireland. back to top Back to Table of Contents Next To top Recommend this page Disclaimer:The opinions expressed by authors contributing to Eurosurveillance do not necessarily reflect the opinions of the European Centre for Disease Prevention and Control (ECDC) or the editorial team or the institutions with which the authors are affiliated. Neither ECDC nor any person acting on behalf of ECDC is responsible for the use that might be made of the information in this journal. The information provided on the Eurosurveillance site is designed to support, not replace, the relationship that exists between a patient/site visitor and his/her physician. Our website does not host any form of commercial advertisement. Eurosurveillance [ISSN] All rights reserved This site complies with the HONcode standard for trustworthy health information: verify here.

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