What Dynamic Simulation Can Add to Water Utility Risk Assessment Mohamed A. Hamouda, Jared Best, William B. Anderson, and Peter M. Huck 2014 OWWA/OMWA Joint Annual Conference & OWWEA Trade Show May 4 th - 7 th , 2014
What Dynamic Simulation Can Add to Water Utility Risk Assessment
Mohamed A. Hamouda, Jared Best, William B. Anderson, and Peter M. Huck
2014 OWWA/OMWA Joint Annual Conference &
OWWEA Trade Show May 4th - 7th, 2014
Ensuring Product Quality
Product Quality Control (QC) monitors compliance with standards • QC tells us that something has gone wrong after
it has happened
Process Quality Assurance (QA) uses risk
management • QA tries to stop that something before it goes
wrong
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Preparation1. Assemble the WSP Team
System Assessment2. Describe the water supply system3. Identify hazards, hazardous events, and assess risks4. Determine and validate control measures, reassess and prioritize risks5. Develop, implement, and maintain an improvement / upgrade plan
Operational Monitoring6. Define monitoring of the control measures
7. Verify the effectiveness of the WSP
Management and Communication8. Prepare management procedures9. Develop supporting programs
UpgradeInvestment required for major system modifications
Feedback11. Revise the WSP following an incident
10. Plan and carryout periodic review of the WSP
Incident (emergency)
Water Safety Plan
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Risk Assessment: State-of-the-art
Define Scope
• Know the system: flow, quality, and operating parameters • Define failure: quality, quantity, economic, environmental impact,
and/or customer trust
Identify Hazards
• An existing or possible/probable event that could cause failure • Methods: FTA, FMEA, Checklists, HAZOP, HACCP (e.g. CWWA) etc.
Estimate Risk
• Qualitative: ordinal scale likelihood x consequence (e.g. AB DWSP) • Quantitative: stochastic/probabilistic analysis
Evaluate Risk
• Define thresholds or tolerability criteria, or ranking method • Identify risk reduction methods and evaluate/rank them
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Score N/A Insignificant Minor Moderate Severe Catastrophic
N/A 0 1 2 4 8 16 Most Unlikely 1 1 2 4 8 16
Unlikely 2 2 4 8 16 32 Medium 4 4 8 16 32 64 Probable 8 8 16 32 64 128
Almost Certain 16 16 32 64 128 256
Qualitative Risk Assessment
A
D
E
C
B
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Acceptable Risk ALARP (As Low As Reasonably Possible)
Unacceptable Risk
Identify and rank target events causing unacceptable risks
Identify and rank risk-reduction options
Quantitative Risk Assessment: e.g. QMRA
QMRA
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1. Hazard Assessment: System description, indicators, failures
2. Exposure Assessment: Pathogen concentrations (% infectious),
Treatment (Log reduction), Consumption (L/d)
3. Dose-response Analysis: Impact of Exposure (Pinf, Pill,
#Illnesses/Yr, DALY*)
4. Risk Characterization and Alleviation: Compare to
acceptable risk levels and outline risk reduction measures
Risk Assessment
Qualitative Quantitative
Relatively easy and fast Cumbersome
Easy to communicate, decision is clear, common
Easily comparable
“Comprehensive” “Rigorous” and specific
Abstracting/obscuring data
Data input is explicit
High subjectivity, overlooking combined effects
Less subjective and transparent (for experts)
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Dynamic Simulation
In dynamic simulation models, events occur sequentially over time. Specialized software is required
Time series data are used explicitly and the output is also displayed in time series
In a dynamic simulation, stochastic variables may be discrete or continuous
Different from static simulation (simple Monte Carlo)
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Dynamic Simulation for Risk Assessment
Objectives: Review existing water treatment dynamic
simulation platforms Select a water treatment simulation platform to
be used in conducting risk assessment Outline changes to the risk assessment
framework resulting from the use of dynamic simulation
Demonstrate the use of dynamic simulation in hazard identification
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Dynamic Simulation: State-of-the-art
Water treatment simulators have existed since the 1990s: • OTTER (WRc) • Stimela (TU-Delft) • Metrex (TU-Duisburg) • WTP (US EPA) • WatPro (Hydromantis)
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Dynamic Simulation: State-of-the-art
However they have had poor uptake • Design and performance evaluation is mainly
driven by pilot trials and rules of thumb. • Extensive data required for calibration, and
models have restricted validity outside calibration range, why?
• Focus on building an accurate simulator rather than tailoring it to a particular use.
• One more thing to learn! Bugs are frustrating!
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SimEAU
SimEAU was developed as part of the EU Fifth Framework project, TECHNEAU
To replace WRc’s OTTER & TU Delft’s Stimela Greater emphasis on calibration using routine
data, and theory based process models Modelling process dependence on downstream or
upstream processes and consequences on performance
Open framework designed to simplify adding new water treatment process models
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How SimEAU Compares?
Process METREX STIMELA OTTER SimEAU Coagulation + Flocculation
Combined Sedimentation Rapid Filtration Biological Filtration Ozonation Adsorption Softening Chlorination Membrane Filtration
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Risk Assessment Framework + Dynamic Simulation
Define Scope
• - Limitations set by data and simulation model
Identify Hazards
• + Simulations help identify hazards • + Hazard impact scenarios (what if…)
Estimate Risk
• + Accepts discrete and continuous parameters • - To be comprehensive dramatically increases complexity
Evaluate Risk
• + Probability of failure: non compliance, health risk, etc. • + Risk alleviation measures scenarios
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SimEAU Demonstration : Hazard Identification Baseline simulation
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SimEAU Demonstration : Hazard Identification
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SimEAU Demonstration : Hazard Identification
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SimEAU Demonstration : Hazard Identification
Filter to waste
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Filter to waste
SimEAU Demonstration : Hazard Identification Hazard what-if scenarios: e.g. flocs of lower mass
density increased filter-to-waste period
Filter to waste19
Filter to waste
Benefits of Dynamic Simulation
More explicitly represent the timing and sequencing of events, their impact, and response
Data is used rather than assuming distributions Directly calculate the impact of variations of raw
water quality, operating parameters and process performance on the plant model
Capable of capturing complex interdependencies System success criteria is more realistic as opposed
to conservative criteria used in less rigorous assessments
Risk alleviation measures can be directly simulated
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Conclusions
Dynamic simulation can potentially enhance risk assessment by introducing transparent, explicit, and real use of raw data
Water simulators can be tailored for use in risk
assessment, to increase uptake
Dynamic simulation requires extensive data, and can help shape the future of data collection and monitoring in WTP
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Future Work
Developing simulation models to assess the risk of producing non-compliant water for certain contaminants of concern
Integrating QMRA in SimEAU, the analysis will then rely on simulated performance of the treatment plant rather than estimating performance based on previous studies
Exploring other uses of dynamic simulation
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Acknowledgements
Special thanks to Jeremy Dudley, WRc UK, for providing a copy of SimEAU and for answering questions regarding the use of SimEAU and identified bugs in the program.
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Thank you to our NSERC Chair partners
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