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Current Technologies for Identification and Measurement of fecal Pollution in Water

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E. coli ISOLATES FROM TWO CATTLE FECAL SAMPLES ... Cattle (particularly in streams) contribute substantially to water pollution ... – PowerPoint PPT presentation

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Title: Current Technologies for Identification and Measurement of fecal Pollution in Water


1
Current Technologies for Identification and
Measurement of fecal Pollution in Water
  • C.A. Carson
  • University of Missouri

2
EXAMPLES OF URGENCY OF FECAL POLLUTION PROBLEM
  • Increased numbers of impaired waterways
  • Closure of coastal shellfish beds
  • Swimming beach closures
  • Impact on public health, revenue, commerce

3
FECAL BACTERIA
  • Intestinal tracts are anaerobic
  • Normal flora are anaerobic or facultative
    anaerobes
  • Anaerobes are in larger numbers Bacteroides,
    Faecalibacterium, Clostridium
  • Facultative anaerobes examples are Escherichia
    and Klebsiella thousand fold (plus) fewer

4
COLIFORMS
  • Gram (-), lactose fermenting, enteric rods
    normal gut flora
  • Long used as indicators of drinking water safety
  • Aerobes/facultative anaerobes examples are
    Escherichia (eg. E. coli), Enterobacter,
    Klebsiella
  • Coliforms (now E. coli) EPA indicator for fresh
    water

5
WATER-BORNE FECAL PATHOGENS (Examples)
Bacteria Viruses Protozoa
Escherichia Coxsackievirus
Crystosporidium Salmonella
Poliovirus Giardia Campylobacter
Hepatitis Entamoeba Yersinia
Adenovirus Toxoplasma
Aeromonas Reovirus Clostridium
Calicivirus Norovirus
Coronavirus
6
HUMAN HEALTH RISK
  • EPA standards for recreational waters based on
    1984 fecal coliform/bather illness correlation
  • Total fecal coliforms NMT 200/100 ml
    (fresh)
  • E. coli NMT 126/100 ml (fresh) 8
    ill/1000 bathers
  • Enterococci NMT 33/100 ml (marine) 16
    ill/1000
  • Correlation of indicator organisms with presence
    of pathogens and health risk (?)
  • Question of relative risk of host source of
    pollution human vs cattle vs geese FC counts
    not indicate hosts of origin
  • Current studies and surveys by SCCWRP

7
EXAMPLES OF POTENTIAL SOURCES OF
FECAL POLLUTION
  • Human sewage treatment systems - private,
    collective (aging urban utilities)
  • CAFO s
  • Pastured animals
  • Pet animals
  • Migratory birds
  • Wild animals

8
TARGETING FECAL POLLUTION
  • Non-pathogenic bacteria-large numbers of harmless
    bacteria usually present for normal intestinal
    function
  • Pathogenic (disease-producing) bacteria-normally
    absent or in low numbers
  • Looking for pathogens (the real concern) in water
    samples resembles looking for a needle in a
    haystack
  • Finding the haystack is easier
  • Fecal coliforms E. coli Enterococcus are
    common/plentiful useful as indicators

9
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10
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11
PROKARYOTIC BACTERIAL CELL
From Principles of Microbiology by Atlas. W.C.
Brown Co. 2nd Ed. 1997.
12
GENERAL APPROACH TO MST
  • Routine water sampling shows unacceptable levels
    of sentinel indicator(s) indicative of fecal
    pollution
  • MST test(s) are chosen to provide evidence of
    host source(s)
  • An associated intensified (serial) water sampling
    plan is formulated data will be derived-
    followed by conclusions and action

13
TIERED CONCERNS
  • Human vs. nonhuman sources (public health risk)
  • Identification of human and various nonhuman
    sources via E. coli or other common indicator
    organisms

14
BASIS OF MST METHODS
  • Particular strains of enteric bacteria (eg. E.
    coli) inhabit intestinal tracks of humans,
    animals and birds
  • These various host-specific strains can be
    distinguished by their different functions /
    biochemistry (phenotype) or different genetic/DNA
    structure (genotype)
  • MST can be performed using either of these
    qualities

15
Fecal Source Tracking MethodsCulture,
Phenotypic, Genotypic, Reference Library,
Non-Library
  • Antibiotic resistance profiles specificity
  • Carbon source utilization specificity
  • Ribotyping based on rRNA gene probe specific
    requires 8 days
  • rep-PCR position of repeat elements specific
    somewhat more rapid
  • PFGE highly specific (excessive)
  • All above require culture and libraries

16
DATABASE / REFERENCE LIBRARY
  • Representative of environmental bacteria
  • Subject to temporal and geographic variation
  • Watershed specific
  • Library size-(?) 200 isolates / host class
  • Expensive - cost / fingerprint pattern

17
METHODS (Cont.)
  • Host-specific PCR Bacteroides/Prevotella
    species culture-and library independent
  • F phage typing accurate may not be present
  • Enterovirus/adenovirus accurate may not be
    present
  • Pathogen ID eg. Pathogenic E. coli, Salmonella,
    hepatitis virus pathogens scarce in nature
  • Chemical methods caffeine, laundry detergents,
    etc. inexpensive may not be present

18
COMPARISON OF SELECTED MST METHODS
19
BACTERIAL FINGERPRINTING / rep-PCR(First Example)
  • Multiple copies of target repeat elements per E.
    coli genome
  • Repeat numbers and locations vary per bacterial
    strain
  • Primers amplify segments of DNA between
    repeats/signature of strain
  • E. coli strains generally associated with gut
    flora of particular host species (human, nonhuman)

20
rep PCR TEST BASED ON LOCATION OF TARGET GENE
IN E. coli
E. coli
rep genes
DNA chromosome
1
1
2
1
2
3
2
3
3
Human
Cow
Dog
PCR Multiply 1,2,3
PCR Multiply 1,2,3
PCR Multiply 1,2,3
Different DNA Fingerprint patterns
21
MATERIALS AND METHODS
rep PCR
PCR BOX A1R primer
Lyse cells
Select/Grow pure fecal E. coli isolates
  • Bionumerics software
  • Similarity coefficients of patterns calculated by
    dice method with fuzzy logic option.
  • Discriminant analysis via cross validation of
    database

Pattern analysis by computer program
22
FECAL E. coli ISOLATES FROM TWO INDIVIDUAL HUMAN
SAMPLES
(Bp)
(Bp)
10000
5000
3000
2000
1500
1000
800
600
400
200
23
E. coli ISOLATES FROM TWO CATTLE FECAL SAMPLES
24
FECAL E. coli ISOLATES FROM ONE LITTLE SAC RIVER
WATER SAMPLE
25
PATTERN ANALYSIS
  • Fecal E. coli isolates compiled in known-host
    database/library (human and non-human hosts)
  • Environmental (water) E. coli isolates
    host-associated by comparison with database
    isolates maximum similarity with particular
    library pattern
  • Arbitrary cutoff for unknown patterns at
    least 80 similarity with library pattern A-C
    quality factor

26
Human E. coli Isolates
27
Cattle E. coli Isolates
28
Cattle and Human E. coli Isolates
29
SECOND EXAMPLE METHODHost Specific/Gene Specific
Targeting Non library-based Procedure
  • Bacteroides are most numerous human intestinal
    bacteria
  • Different hosts have different species and strains

30
MICROBIAL GENE - SPECIFIC/HOST SPECIFIC PCR
Target DNA
Microbe
Electrophoresis
PCR Multiply Target
Specific product size
___
___
Fecal pollution
No pollution
31
GENE-SPECIFIC PCR INDICATIVE OF HOST SOURCE OF
FECAL POLLUTION
Unknown based on metagenomics
32
FIELD APPLICATION OF MICROBIAL SOURCE TRACKING
METHODS UPPER SHOAL CREEK WATERSHED
  • 3 county area in extreme SW part of MO Newton,
    McDonald, Barry Counties
  • One of most agriculturally productive areas in MO
  • 91,000 acres in the watershed 90 is pasture
    land grazed by over 300,000 head of cattle and
    fertilized by spreading poultry litter
  • 50-80 million poultry produced here yearly
  • 13 miles of Shoal Creek are designated as
    impaired due to high fecal coliform (FC) levels

33
SHOAL CREEK MST DATA
34
Seasonal Fecal E.Coli Sources (Average
Contribution)
SUMMER
WINTER
35
Fecal E. Coli Sources and Flow
SUMMER STORM FLOWS
SUMMER BASE FLOWS
Wildlife
36
STUDY CONCLUSIONS
  • Cattle (particularly in streams) contribute
    substantially to water pollution
  • Waste from pastured animals and spread poultry
    litter also contribute via runoff to streams
  • There are multiple host sources of feces that
    combine for the total contribution
  • Studies usually reveal multiple host sources,
    rather than a single host source
  • Results from routine water quality monitoring,
    fecal source tracking and visual inspection can
    all combine to analyze problems and suggest
    solutions

37
BOTTOM LINE
  • MST methods are powerful tools to resolve
    questions of host sources of fecal pollution and
    associated high bacterial counts in water
  • Current consensus is to use a combination of
    methods with different targets
  • Results must be interpreted carefully, combined
    with local observations and based on multiple
    samples collected over a period of time

38
ACKNOWLEDGMENT OF TEAM
MEMBERS
  • Food and Agricultural Policy Research Institute
  • U.S. Environmental Protection Agency
  • U.S. Geological Survey
  • College of Agriculture and Natural Resources
  • Department of Agriculture Engineering
  • Department of Agriculture Economics
  • College of Veterinary Medicine
  • U.S. Department of Agriculture
  • Missouri Department of Natural Resources
  • University of Missouri Extension Services
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