DEVELOPMENT OF RAPID QPCR APPROACHES FOR MEASUREMENT OF E' COLI AND ENTEROCOCCUS IN ENVIRONMENTAL WA - PowerPoint PPT Presentation

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DEVELOPMENT OF RAPID QPCR APPROACHES FOR MEASUREMENT OF E' COLI AND ENTEROCOCCUS IN ENVIRONMENTAL WA

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Title: DEVELOPMENT OF RAPID QPCR APPROACHES FOR MEASUREMENT OF E' COLI AND ENTEROCOCCUS IN ENVIRONMENTAL WA


1
DEVELOPMENT OF RAPID QPCR APPROACHES FOR
MEASUREMENT OF E. COLI AND ENTEROCOCCUS IN
ENVIRONMENTAL WATERS THE FUTURE FOR ROUTINE
MONITORING?
  • Rachel T. Noble, A. Denene Blackwood, and Seth Yu
  • National Monitoring Conference
  • May 9, 2006
  • UNC Chapel Hill Institute of Marine Sciences
  • Morehead City, NC

2
Bacterial indicator testing
  • Routine monitoring in US costs gt10 M USD annually
  • Majority of money spent in sampling and analysis
    time
  • California alone responsible for more than half
    of the monitoring in the US
  • Aim Protect public health
  • Impacts Public perception, economy, tourism,
    recreational water usage
  • Need Rapid, quantitative methods that can be
    used to accurately manage beaches and shellfish
    harvesting waters

3
Routine methods bacterial indicators
  • Total coliforms (TC) heterogeneous group composed
    of Escherichia, Citrobacter, Enterobacter,
    Salmonella, Shigella, Yersinia, and Aeromonas
    genera
  • Fecal coliforms or E. coli thermotolerant (44.5
    C) subset of TC (FC can include Klebsiella),
    freshwater
  • Enterococci, (gt 20 species, e.g. faecalis,
    faecium, casseliflavus, durans, avium,
    gallinarum), marine waters
  • Membrane filtration, Chromogenic substrate
    (IDEXX), and Multiple Tube Fermentation
  • Require from 18-96 hours for results
  • Inaccurate management of recreational and
    shellfish harvesting waters because of delay

4
The need for faster results
  • Allow accurate management of beaches (keep open
    when clean and close immediately when not safe
    for swimming)
  • Faster results better tracking down sources of
    contamination
  • Tracking sources down reducing sources (or
    prioritizing reduction of human sources)
    reduction of potential risks to the public

5
Immediate future real world example
  • 700 AM Beach water sample collected
  • 800 AM Return to lab, process using rapid
    method and routine method (MF, MTF, IDEXX)
  • 1000 AM
  • 1) E. coli gt 400/100 ml and/or Enterococcus
    gt104/100 ml or Return and close beach, sample
    on periodic basis until clean
  • 2) Enterococci lt104/100 ml or E. coli lt 400/100
    ml Keep beach open and sample again (or wait
    until next morning to repeat)

6
Longer term future
  • Same time-scale (or maybe more rapid)
  • Measure pathogens instead of indicators (i.e.
    conduct epidemiology studies)
  • Real time measurements on deployed systems could
    provide hourly indications of water quality
  • Technology applicable to shellfish harvesting
    waters, aquaculture effluents, stormwater runoff,
    NPDES permits etc.

7
Criteria for rapid methods
  • Time required for result
  • Threshold exceedance
  • Numerical result
  • Accuracy, Variability, Reproducibility
  • Portability
  • Specificity and usefulness of result for
    mitigation or protecting public health
  • Training required
  • Data accessibility
  • Maintenance required of system (Deployable in
    situ, unattended?)
  • Cost (initial buy in, and per sample)
  • Equivalent results to classical indicator
    bacteria data/historical data

8
Developing Rapid Detection Technologies for
Environmental Waters
  • Most currently developed technologies utilize
    sample collection and filtration approaches
    similar to routine methods
  • Capture is dependent upon approach
  • Detection fluorescence, electrochemical, etc.
  • Data transfer and real-time access
  • Combination of available applications limited
    only by imagination and
  • Noble and Weisberg 2005

9
Capture nucleic acid priming
  • PCR Based methods
  • Transcription mediated amplification (TMA)
  • Microarrays
  • NASBA
  • Highly specific/sensitive
  • Based upon known sequence complementarity
  • Can be used to type specific types of pathogens

10
Rapid microbial detection assays
  • Developing technology using QPCR in conjunction
    with Cepheid, Inc.
  • QPCR- quantification of E. coli ( 2.0 hr)
  • QPCR- quantification of Enterococcus sp. ( 2.0
    hr)
  • QRTPCR-quantification of human enteroviruses ( 4
    hr)
  • QPCR and QRTPCR- Rapid assays for a wide range of
    other viral pathogens (noroviruses, Vibrio
    vulnificus) and fecal marker bacteria
    (Bacteroides, Enterococcus species)
  • Apply technology in all types of water samples
    (estuarine, coastal, freshwater, brackish,
    wastewater, shellfish harvesting waters,
    shellfish harvesting meats)

11
QuantitativePCR (or RTPCR)
  • Primer/probe set design
  • PCR for amplification of DNA
  • No gels needed

Cepheid Smart Cycler II
  • Increase in fluorescence is directly proportional
    to the amount of target cDNA in sample and
    indicated by cycle threshold
  • Standard curve generated by plotting threshold
    cycle vs. log concentration and unknown values
    interpolated

12
QPCR Assay Details
  • 100 ml through PC filter to capture bacteria
  • 0.45 µm pore size with vacuum needs same as for
    MF analysis
  • DNA purification (bead beating or full
    extraction)
  • Assay features SmartMixTM Beads (all PCR
    reagents) SmartBeadsTM contain primers, probes,
    and internal controls (lyophilized)
  • Reduces pipetting steps and errors, interanalyst
    variability, increases quality of standard curves
  • Assay also incorporates the use of innovative
    QPCR chemistry developed by DsX Limited
    (Manchester, UK) called SCORPIONS
  • Scorpions give lower background, lower LOD
  • Licensing fees not prohibitive in cost to WQ
    agencies

13
Specificity and Ubiquity
14
SCCWRP Study
  • June 2005 study to compare rapid detection
    methods for Enterococcus and E. coli to routine
    methods (MF and either Enterolert or
    Colilert-18)
  • 3 day study
  • 54 blind samples
  • Seawater, stormwater runoff, blanks, coastal
    water unseeded and seeded with cultured bacteria
  • Verification and speciation of isolates on plates
    and in quantitrays
  • QPCR and TMA-based assays both fared well in the
    comparison
  • Routine methods roughly 85-90 percent agreement
  • QPCR Enterococcus roughly 80 accurate
  • QPCR E. coli results 90 accurate
  • QPCR had low variability compared to other methods

15
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17
Summary of results
  • Fully quantitative, wide dynamic range
  • LOD for both assays is 1 cell per reaction, for
    assay with DNA extraction step is 10 cells/100 ml
  • 90 correct response rate for E. coli and 80-85
    correct response rate for Enterococcus
  • Strong correlation to routine methods (r2 values
    range from 0.70 to 0.95 depending upon comparison
    to MF or DS)
  • ENT assay captures at least 10 known species of
    Enterococcus (including faecium, faecalis,
    caselliflavus, pseudoavium, gallinarum, etc.)
  • Working towards ability to conduct filtration in
    the field
  • Internal controls and matrix controls in place
    for quantitative sample analysis
  • Currently beta-testing assay at OCSD and
    exploring use in drinking water (E. coli)

18
Preliminary results of beta testing at OCSD
  • Roughly 40 samples
  • Enterococcus and E. coli assay being tested by in
    house WQ personnel
  • Results good to date
  • Open beaches and storm samples
  • Stay tuned!

19
AcknowledgementsSteve Weisberg and John
Griffith, SCCWRP Denene Blackwood and Jason
Gregory (UNC Chapel Hill) State of California,
esp. Robin McGraw and Shakoora Azimi-Gaylon United
States Department of Agriculture Cepheid, Inc.
R. Schaller, C. Wilkins, N. Beckwith and S.
Yu Orange County Sanitation District Rich
Haugland, USEPA
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