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E' coli Facts Beach Monitoring

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States having coastal recreational waters must adopt new/revised ... Member of the fecal coliform group. Fresh water quality standard. Advantages/Disadvantages ... – PowerPoint PPT presentation

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Title: E' coli Facts Beach Monitoring


1
E. coli Facts Beach Monitoring
  • Julie Kinzelman, City of Racine
  • Beach Management Workshop
  • April 14 15, 2005, Egg Harbor, WI

2
USEPA BEACH Act of 2000
  • States having coastal recreational waters must
    adopt new/revised water quality standards
  • Must use approved indicator organisms E. coli
    or enterococci
  • Must use approved testing methods mTEC or
    modified mTEC agar, Colilert, Colisure
  • Prompt public notification

3
Approved Indicator Organisms
  • E. coli or enterococci

4
What is an Indicator Organism?
  • Found in feces of humans and other animals
  • Act as a warning that human pathogens may be
    present
  • SURROGATES for pathogenic micro-organisms
  • NOT pathogens
  • Provide no information about source of
    contamination

5
Why not just test water for pathogens?
  • Too many possibilities Salmonella, Shigella,
    Campylobacter, viruses
  • Too slow.
  • Too expensive.

6
What makes a good indicator?
  • Their density in water (without proliferation)
    gives a reasonable estimate of pathogen presence
    and can be positively correlated with the
    potential health risks associated with exposure
  • Their presence is consistently and exclusively
    associated with the source of the pathogens
  • Their ability to demonstrate similar resistance
    to environmental stress as the most resistant
    pathogens present at significant levels
  • Their constant characteristics provide for
    accurate quantification which can be achieved
    through simple and inexpensive detection methods
  • Their presence must be harmless to humans and
    animals
  • Their ability to be detected by laboratory
    methods in the shortest amount of time consistent
    with providing accurate results (WHO 1997)

7
E. coli
  • Normal intestinal flora of humans and animals
    (about 0.1 of humans)
  • Member of the fecal coliform group
  • Fresh water quality standard

8
Advantages/Disadvantages
  • High numbers have been associated with an
    increased frequency of GI illness in bathers
  • Simple and inexpensive to detect
  • Can get results in less than 24-hours
  • Present in high number in non-human sources such
    as seagulls
  • If environmental persistence or replication
    occurs it may lack relevance

9
Sample Collection
  • Racine, WI

10
Surface Water Sampling
  • Fixed monitoring stations
  • Fixed sampling frequency
  • Sampled at same time each day
  • Collected at consistent depth
  • Record ambient conditions

11
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12
Racine Sampling Protocol
  • One station every 200m
  • Monitored M F (more if advisory/closure)
  • Samples collected between 1130 1300
  • Collected at a depth of 3 ft _at_ 1 ft below surface
  • Record ambient conditions (air/water temp, wave
    height, wind speed/direction, rainfall, bathers,
    gulls, algae, and other notables)

13
Testing Protocol
  • Approved Methods (Racine)

14
Membrane Filtration
  • M-TEC or modified m-TEC agar
  • Results available in approximately 24 hours
  • Good technique if you will be using the results
    for source tracking
  • Requires personnel trained in microbiology
  • Labor intensive
  • Plates can be overcrowded if not diluted properly

15
E. coli using MF/m-TEC agar
16
E. coli colonies on m-TEC
17
Chemical Substrate Tests
  • Colilert, Colilert-18, Colisure
  • Results in as little as 18 hours
  • Would require plating to additional media for
    source tracking
  • Easy to use
  • Requires little hands on time
  • Can quantify up to 2419.2 MPN/100 ml without
    diluting
  • Less interference from background organisms

18
E. coli using Colilert-18
19
E. coli Life Cycle
  • Persistence or replication may influence
    monitoring results

20
Sources of E. coli
  • Storm water discharge
  • Sanitary systems
  • Algae
  • Animal feces

21
E. coli in Sand (Whitman, 2002)
22
Poor Estimation of Health Risk
  • Type I errors occur when an advisory is posted
    but the level of bacterial indicator organisms do
    not exceed recommended standards or guidelines
  • Type II errors occur when no advisory is posted
    in the presence of elevated bacterial indicator
    levels

23
Racine Data 2002 - 2004
24
Whats on the Horizon?
  • Alternative indicators
  • Real-time testing technology
  • New epidemiological studies (USEPA)
  • Pathogen studies
  • Research designed to determine replication/persist
    ence and host source of bacterial indicators

25
Acknowledgements
  • WI DNR
  • Richard Whitman, USGS
  • UWM Great Lakes Water Institute
  • S.C. Johnson, A Family Company
  • City of Racine Health Department
  • University of Surrey, RCPEH
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