Adenovirus-associated health risks for recreational activities in a multi-use coastal watershed based on site-specific quantitative microbial risk assessment

We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with primary contact, children with primary contact, and secondary contact regardless of age. Human enteroviruses and adenoviruses were monitored b...

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Published inWater research (Oxford) Vol. 47; no. 16; pp. 6309 - 6325
Main Authors Kundu, Arti, McBride, Graham, Wuertz, Stefan
Format Journal Article
LanguageEnglish
Published Kidlington Elsevier Ltd 15.10.2013
Elsevier
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Abstract We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with primary contact, children with primary contact, and secondary contact regardless of age. Human enteroviruses and adenoviruses were monitored by qPCR in a multi-use watershed and Adenovirus type 40/41 was detected in 11% of 73 samples, ranging from 147 to 4117 genomes per liter. Enterovirus was detected only once (32 genomes per liter). Seven of eight virus detections occurred when E. coli concentrations were below the single sample maximum water quality criterion for contact recreation, and five of eight virus detections occurred when fecal coliforms were below the corresponding criterion. We employed dose-harmonization to convert viral genome measurements to TCID50 values needed for dose–response curves. The three scenarios considered different amounts of water ingestion and Monte Carlo simulation was used to account for the variability associated with the doses. The mean illness risk in children based on adenovirus measurements obtained over 11 months was estimated to be 3.5%, which is below the 3.6% risk considered tolerable by the current United States EPA recreational criteria for gastrointestinal illnesses (GI). The mean risks of GI illness for adults and secondary contact were 1.9% and 1.0%, respectively. These risks changed appreciably when different distributions were fitted to the data as determined by Monte Carlo simulations. In general, risk was at a maximum for the log-logistic distribution and lowest for the hockey stick distribution in all three selected scenarios. Also, under default assumptions, the risk was lowered considerably when assuming that only a small proportion of Adenovirus 40/41 (3%) was as infectious as Adenovirus type 4, compared to the assumption that all genomes were Adenovirus 4. In conclusion, site-specific QMRA on water-borne adenoviruses in this watershed provided a similar level of protection against public health risks as would be obtained by enumeration of fecal indicator bacteria under the new U.S. EPA guidelines. Importance of site-specific risk assessment in recreational waters. • Children – recreational users; • Primary users – adult (standing in the water) in this scenario; • Primary contact – incidental ingestion of water; • Secondary user – child playing in the sand on beach. [Display omitted] •Illness risks modeled in adults and children with primary contact and secondary users regardless of age.•We model assuming that only a small proportion of detected Adenovirus 40/41 is as infectious as Adenovirus type 4.•Dose-harmonization for qPCR data reduces pathogen dose of enteric virus.•Significant changes in mean estimated risk from different distributions fitted to concentrations of water-borne pathogens.•First report of site-specific QMRA in freshwater in the United States.
AbstractList We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with primary contact, children with primary contact, and secondary contact regardless of age. Human enteroviruses and adenoviruses were monitored by qPCR in a multi-use watershed and Adenovirus type 40/41 was detected in 11% of 73 samples, ranging from 147 to 4117 genomes per liter. Enterovirus was detected only once (32 genomes per liter). Seven of eight virus detections occurred when E. coli concentrations were below the single sample maximum water quality criterion for contact recreation, and five of eight virus detections occurred when fecal coliforms were below the corresponding criterion. We employed dose-harmonization to convert viral genome measurements to TCID50 values needed for dose-response curves. The three scenarios considered different amounts of water ingestion and Monte Carlo simulation was used to account for the variability associated with the doses. The mean illness risk in children based on adenovirus measurements obtained over 11 months was estimated to be 3.5%, which is below the 3.6% risk considered tolerable by the current United States EPA recreational criteria for gastrointestinal illnesses (GI). The mean risks of GI illness for adults and secondary contact were 1.9% and 1.0%, respectively. These risks changed appreciably when different distributions were fitted to the data as determined by Monte Carlo simulations. In general, risk was at a maximum for the log-logistic distribution and lowest for the hockey stick distribution in all three selected scenarios. Also, under default assumptions, the risk was lowered considerably when assuming that only a small proportion of Adenovirus 40/41 (3%) was as infectious as Adenovirus type 4, compared to the assumption that all genomes were Adenovirus 4. In conclusion, site-specific QMRA on water-borne adenoviruses in this watershed provided a similar level of protection against public health risks as would be obtained by enumeration of fecal indicator bacteria under the new U.S. EPA guidelines.
We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with primary contact, children with primary contact, and secondary contact regardless of age. Human enteroviruses and adenoviruses were monitored by qPCR in a multi-use watershed and Adenovirus type 40/41 was detected in 11% of 73 samples, ranging from 147 to 4117 genomes per liter. Enterovirus was detected only once (32 genomes per liter). Seven of eight virus detections occurred when E. coli concentrations were below the single sample maximum water quality criterion for contact recreation, and five of eight virus detections occurred when fecal coliforms were below the corresponding criterion. We employed dose-harmonization to convert viral genome measurements to TCID₅₀ values needed for dose–response curves. The three scenarios considered different amounts of water ingestion and Monte Carlo simulation was used to account for the variability associated with the doses. The mean illness risk in children based on adenovirus measurements obtained over 11 months was estimated to be 3.5%, which is below the 3.6% risk considered tolerable by the current United States EPA recreational criteria for gastrointestinal illnesses (GI). The mean risks of GI illness for adults and secondary contact were 1.9% and 1.0%, respectively. These risks changed appreciably when different distributions were fitted to the data as determined by Monte Carlo simulations. In general, risk was at a maximum for the log-logistic distribution and lowest for the hockey stick distribution in all three selected scenarios. Also, under default assumptions, the risk was lowered considerably when assuming that only a small proportion of Adenovirus 40/41 (3%) was as infectious as Adenovirus type 4, compared to the assumption that all genomes were Adenovirus 4. In conclusion, site-specific QMRA on water-borne adenoviruses in this watershed provided a similar level of protection against public health risks as would be obtained by enumeration of fecal indicator bacteria under the new U.S. EPA guidelines.
We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with primary contact, children with primary contact, and secondary contact regardless of age. Human enteroviruses and adenoviruses were monitored by qPCR in a multi-use watershed and Adenovirus type 40/41 was detected in 11% of 73 samples, ranging from 147 to 4117 genomes per liter. Enterovirus was detected only once (32 genomes per liter). Seven of eight virus detections occurred when E. coli concentrations were below the single sample maximum water quality criterion for contact recreation, and five of eight virus detections occurred when fecal coliforms were below the corresponding criterion. We employed dose-harmonization to convert viral genome measurements to TCID50 values needed for dose–response curves. The three scenarios considered different amounts of water ingestion and Monte Carlo simulation was used to account for the variability associated with the doses. The mean illness risk in children based on adenovirus measurements obtained over 11 months was estimated to be 3.5%, which is below the 3.6% risk considered tolerable by the current United States EPA recreational criteria for gastrointestinal illnesses (GI). The mean risks of GI illness for adults and secondary contact were 1.9% and 1.0%, respectively. These risks changed appreciably when different distributions were fitted to the data as determined by Monte Carlo simulations. In general, risk was at a maximum for the log-logistic distribution and lowest for the hockey stick distribution in all three selected scenarios. Also, under default assumptions, the risk was lowered considerably when assuming that only a small proportion of Adenovirus 40/41 (3%) was as infectious as Adenovirus type 4, compared to the assumption that all genomes were Adenovirus 4. In conclusion, site-specific QMRA on water-borne adenoviruses in this watershed provided a similar level of protection against public health risks as would be obtained by enumeration of fecal indicator bacteria under the new U.S. EPA guidelines. Importance of site-specific risk assessment in recreational waters. • Children – recreational users; • Primary users – adult (standing in the water) in this scenario; • Primary contact – incidental ingestion of water; • Secondary user – child playing in the sand on beach. [Display omitted] •Illness risks modeled in adults and children with primary contact and secondary users regardless of age.•We model assuming that only a small proportion of detected Adenovirus 40/41 is as infectious as Adenovirus type 4.•Dose-harmonization for qPCR data reduces pathogen dose of enteric virus.•Significant changes in mean estimated risk from different distributions fitted to concentrations of water-borne pathogens.•First report of site-specific QMRA in freshwater in the United States.
Author Kundu, Arti
McBride, Graham
Wuertz, Stefan
Author_xml – sequence: 1
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  fullname: Kundu, Arti
  organization: Department of Civil and Environmental Engineering, University of California, Davis, One Shields Avenue, Davis, CA 95616, USA
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  givenname: Graham
  surname: McBride
  fullname: McBride, Graham
  organization: National Institute of Water and Atmospheric Research (NIWA), P.O. Box 11-115, Hillcrest, Hamilton 3216, New Zealand
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  surname: Wuertz
  fullname: Wuertz, Stefan
  email: swuertz@ucdavis.edu
  organization: Department of Civil and Environmental Engineering, University of California, Davis, One Shields Avenue, Davis, CA 95616, USA
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IsPeerReviewed true
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Issue 16
Keywords Recreational waters
Human health
Adenovirus
Risk assessment
Adenoviridae
Microbiology
Picornaviridae
Enterovirus
Coastal zone
Adenovirus 4
Adenovirus 3
Health and environment
Human adenovirus
Pathogenic
Watershed
Bacteria
Feces
Biological contamination
Public health
Monte Carlo method
Quality criterion
Biological indicator
Coliforms
Real time system
Virus
Polymerase chain reaction
Surveillance
DNA
Water quality
Health hazards
Mastadenovirus
Bathing water
Language English
License CC BY 4.0
Copyright © 2013 Elsevier Ltd. All rights reserved.
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Elsevier
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– name: Elsevier
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Snippet We used site-specific quantitative microbial risk assessment (QMRA) to assess the probability of adenovirus illness for three groups of swimmers: adults with...
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SubjectTerms Adenoviridae
Adenoviridae - genetics
Adenoviridae - physiology
Adenovirus
adults
Applied sciences
Bacteria
children
coliform bacteria
Computer simulation
Contact
Criteria
Enterovirus
Enterovirus - genetics
Enterovirus - physiology
Escherichia coli
Exact sciences and technology
gastrointestinal system
genome
Genomes
guidelines
Human enterovirus
Human health
Humans
Illnesses
indicator species
ingestion
microbiological risk assessment
Monte Carlo method
Pollution
primary contact
public health
quantitative polymerase chain reaction
Recreation
Recreational waters
Risk
Risk Assessment
secondary contact
viruses
Water Microbiology
water quality
Water treatment and pollution
Watersheds
Title Adenovirus-associated health risks for recreational activities in a multi-use coastal watershed based on site-specific quantitative microbial risk assessment
URI https://dx.doi.org/10.1016/j.watres.2013.08.002
https://www.ncbi.nlm.nih.gov/pubmed/24045212
https://search.proquest.com/docview/1443418666
https://search.proquest.com/docview/1647012686
https://search.proquest.com/docview/1651406715
Volume 47
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