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CCS Risk Analysis 
Neil Wildgust, Global CCS Institute 
Advanced Workshop for CO2 Storage 
August 26-17, 2014 
DF IPN ESIA Ticomán Auditorium 
SUPPORTED BY:
Structure of presentation 
1. Introduction to risk assessment 
2. Properties of CO2 
3. Risks associated with CO2 capture 
4. Risks associated with CO2 transport 
5. CO2 geological storage risks 
o Performance assessment/predictive modeling 
o Potential impacts 
o Risk management (monitoring, mitigation) 
6. Case Study 
SUPPORTED BY:
1. Risk assessment 
• Technical meaning of risk 
(probability, magnitude of impact) 
• Risk assessments provide a structured approach to 
project evaluation 
• Part of a wider risk management process 
• Widely applied to industrial projects, environmental 
assessments, etc 
SUPPORTED BY:
Fundamental RA considerations 
• Context 
• Purpose 
• Scope and Objectives 
• Methodology 
SUPPORTED BY:
Example: UK landfills 
SUPPORTED BY:
UK landfill approach 
• Conceptual model 
• Screening assessment: Source-pathway-receptor 
analysis 
• Simple risk assessment 
• Complex risk assessment (probabilistic) 
SUPPORTED BY:
Landfill conceptual model 
SUPPORTED BY:
2. Properties of CO2 and associated substances 
SUPPORTED BY: 
CO2 
H2S 
SO2
Impairment 
• CO2 can be tolerated in quite high concentrations 
without permanent risk to health. 
• BUT if those exposed have key tasks to execute 
their response may be impaired. 
• THUS need to consider effects during emergency 
situations. 
Atmosphere in submarines is typically 4000ppm CO2!! 
Just below the TLV. Crews should not be impaired. 
However levels up to 10,000ppm are reported. 
SUPPORTED BY:
3. CO2 capture risks 
• The risk of scaling up the capture plants (Will the capture process work on large scale? More 
demonstration projects are needed to eliminate this risk). 
• The risk of fully CCS integrated system and influence on the power plants: 
o The power plant ability and flexibility to provide electricity without CO2 capture (capture no capture option) 
o The risk of shutting down the whole power plant if a problem occurred in the capture plant (This might occur if the 
power plant is fully integrated with the capture process (e.g. pre combustion) or because it could not cope with the 
regulation of low CO2 emissions anymore after the failure of the capture plant). 
• Specific technical risks per capture technology: 
o Post combustion capture: solvent degradation and equipment corrosion 
o Oxy-fuel combustion capture: boiler operation (burner design, flue gas recycle, temperature control and preventing air-in 
leakage) 
o Pre-combustion capture: hydrogen rich turbines operation and availability. 
• The risk of integrating the capture process to the power plant (e.g. steam extraction issues). 
• Environmental impact: chemical emissions to air, water and land, and overall life cycle of the facility 
(e.g. increase fuel consumption). 
SUPPORTED BY:
4. CO2 transport hazards 
• Low temperature releases 
• High pressures 
• Corrosion 
• High vapour density 
• Detection issues 
SUPPORTED BY:
SUPPORTED BY: 
15 January 2009 Vancouver-line rupture 
A running fracture – 
result of a test 
Fractured gasoline line – 
undetected damage 
Results of metal embrittlement
5. Geological storage risks 
• Predictive modelling of reservoir (‘performance 
assessment’), leakage scenarios and potential 
subsurface impacts 
• Experiments and natural analogues used to assess 
potential impacts of leakage scenarios 
• Both elements combine for a storage risk 
assessment 
SUPPORTED BY:
Predictive modelling 
• Can vary from simple analytical equations to 
complex numerical models. 
• Based on knowledge from oil and gas industry, 
hydrogeology, theory. 
• Knowledge gained from recent experimentation 
and early demonstration projects. 
• Required by regulators. 
SUPPORTED BY:
Modelling example 
Courtesy Permedia Research 
SUPPORTED BY:
Modelling challenges 
• Coupling of processes 
• Effects of other substances 
• Old/abandoned wells 
• Effects of pressurisation and fluid displacement 
• Calibration of models – need more real projects to 
provide monitoring data 
SUPPORTED BY:
Potential impacts 
• Good site selection means minimal probability of 
leakage 
• But need to know ‘what if ?’……… 
• Data from natural and industrial analogues 
• Laboratory experiments and models 
• Controlled field tests 
SUPPORTED BY:
Leakage scenarios 
SUPPORTED BY:
University of Nottingham 
SUPPORTED BY:
The Latera caldera 
• The Latera caldera is about 150 km NW of Rome 
• Gas seeps occur throughout the heavily cultivated valley 
SUPPORTED BY: 
Prof Lombardi. URS
Latera – leakage pathways 
0 100 200 300 400 500 600 700 
SUPPORTED BY: 
1500 
1000 
500 
0 
CO2 flux (g m-2 d-1)
U.R.S – Panera, Italy 
SUPPORTED BY:
U.R.S. 
The impact of the gas is limited. Schools of fish swim around the gas plume 
SUPPORTED BY:
Crystal Geyser, Utah, USA 
SUPPORTED BY:
Monitoring and mitigation 
• Monitoring techniques established and 
demonstrated 
• Monitoring provides stakeholder reassurance and 
regulatory compliance 
• Mitigation strategies will be site-specific 
• Experience from CO2-EOR industry 
SUPPORTED BY:
SUPPORTED BY:
Conclusions 
• Capture and transport risks can be managed with 
existing engineering knowledge 
• Geological storage risks are site-specific 
• Predictive models provide performance 
assessment 
• Monitoring provides model calibration 
• Analogues provide information on potential impacts 
SUPPORTED BY:
Location 
ALBERTA 
SUPPORTED BY: 
MANITOBA 
MONTANA 
WYOMING 
NORTH DAKOTA 
SOUTH DAKOTA 
EDMONTON 
SASKATOON 
WINNIPEG 
REGINA 
HELENA 
BISMARCK 
PIERRE 
CALGARY 
WILLISTON BASIN 
HUDSON 
BAY 
SASKATCHEW 
AN 
WEYBURN
Weyburn oilfield 
SUPPORTED BY:
RA and Geological Storage of CO2 
104% Increase 670% Increase 
And for just the final? year of each 
Phase: 2004 – 4 and 2011 – 57 
SUPPORTED BY: 
1,325% Increase
Geological integrity 
SUPPORTED BY: 
• Reservoir 
Characteristics 
• Regional 
Characterization 
• System Model 
• Natural Analog 
• Mississippian 
hydrogeology 
• Aquitard 
characteristics 
• Assessing 
movement between 
reservoir and 
biosphere
Containment vs biosphere rocks 
SUPPORTED BY:
Background – Geosphere 
Geosphere risk assessment focuses on the deep subsurface and 
aims to identify and assess: 
• Assess the risk of CO2 escaping from the primary containment 
structure and reaching the biosphere (containment risk). 
• Assess the effectiveness of the Project in storing the target 
volume of CO2 within the confines of the Weyburn unit 
(effectiveness risk). 
• Identify areas where further research is required to address 
areas of high uncertainty. 
• Identify actions required to reduce risk, and areas where 
further research to develop risk management actions, is 
required. 
SUPPORTED BY:
Background – biosphere 
Biosphere risk assessment focuses on surface and near 
surface processes and aims to assess: 
• Likely movement of CO2 within various components of 
the biosphere once it reaches the biosphere; and 
• Potential impacts on flora, fauna, people and property. 
SUPPORTED BY:
Containment risk targets 
The mass of CO2 retained after 1,000 years should be at least 99% of the 
total CO2 that will be present immediately after the period of injection. 
• Therefore, if the CO2 mass in place at the conclusion of EOR is 
approximately 30 million tonnes, the maximum acceptable mass of CO2 
lost from the system over the next 1,000 years is 300,000 tonnes (1% of 
30 million tonnes). The Project has defined non-containment as any 
mass of CO2 that has left the geosphere and entered the biosphere. 
The minimum level of confidence that the target volume of CO2will be 
retained was set at 80%. Therefore, the maximum chance of losing more 
than the target volume of CO2 over the project period is 20%. 
• The target risk quotient (likelihood x consequences), is therefore 60,000 
for the project (0.2 chance over 1,000 years x 300,000 tonnes). 
SUPPORTED BY:
Process: Geosphere and Biosphere risk 
Building Capacity 
SUPPORTED BY: 
36 
Geosphere Risk 
Assessment 
Technical Inputs 
• Wellbore integrity research 
• Characterisation of reservoir characteristics & transport of CO2 
• Seismicity of area 
• Characterisation of CO2 reactions in reservoir 
• Monitoring techniques & effectiveness 
Outputs 
• CO2 risk events (initiating event & pathway) & ranking 
• Mass of CO2 released if event occurs 
• Likelihood of each event occurring & releasing CO2 
Biosphere Risk Assessment 
Other Technical Inputs 
• Characterisation of aquifers 
• Characterisation of surface water 
• Characterisation of soils / sediments 
• Behaviour of CO2 in soils, sediments, groundwater, surface 
water 
• Receptors in environment 
• Toxicology (animal, plant, human) 
Outputs 
• Risks to biosphere assets (ranking & severity) 
Stakeholder 
Engagement 
Stakeholder Values 
to Engage 
Acceptability of 
Risks 
Mitigation Measures
Guide to assist in the quantification of likelihood 
SUPPORTED BY:
Containment risk profile 
SUPPORTED BY:
Identifying Biosphere assets most at risk from 
pathways 
1000 
100 
10 
1 
0.1 
0.01 
0.001 
0.0001 
SUPPORTED BY: 
Initiating Events - Risk to Assets 
0.00001 
EOR Minor faults 
EOR Through faults 
Nat Seismicity-fault 
reactivation 
Nat Seismicity-new 
fracs 
Nat Seismicity-wells 
EOR Induced chem-fracs 
EOR Induced P/T-fault 
reactivation 
EOR Induced P/T-new 
fracs 
Wells Micros fracs, 
annuli 
Wells Casing 
corrosion 
Wells cement 
Risk Level 
Illness, injury, fatality 
Tourism 
Oil and gas 
Agriculture 
First Nation heritage 
Heritage 
Amenity - sensory, perception 
Amenity - recreation 
Species 
Habitat, communities, 
assemblages 
Ecosystem function 
Property/infrastructure 
Target Risk Level
Update on RA methodologies 
• Recent project assessments, e.g. Shell Quest, 
Aquistore, Bell Creek 
• CSA Standard (joint US-Canada work) 
• US DOE & Weyburn Best Practice Manuals 
• EC Storage Directive Guidance 
• Many other R&D projects and programs… 
SUPPORTED BY:
End. 
Advanced Workshop for CO2 Storage 
August 26-17, 2014 
DF IPN ESIA Ticomán Auditorium 
SUPPORTED BY:

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CCS Risk analysis, Neil Wildgust, Global CCS Institute

  • 1. CCS Risk Analysis Neil Wildgust, Global CCS Institute Advanced Workshop for CO2 Storage August 26-17, 2014 DF IPN ESIA Ticomán Auditorium SUPPORTED BY:
  • 2. Structure of presentation 1. Introduction to risk assessment 2. Properties of CO2 3. Risks associated with CO2 capture 4. Risks associated with CO2 transport 5. CO2 geological storage risks o Performance assessment/predictive modeling o Potential impacts o Risk management (monitoring, mitigation) 6. Case Study SUPPORTED BY:
  • 3. 1. Risk assessment • Technical meaning of risk (probability, magnitude of impact) • Risk assessments provide a structured approach to project evaluation • Part of a wider risk management process • Widely applied to industrial projects, environmental assessments, etc SUPPORTED BY:
  • 4. Fundamental RA considerations • Context • Purpose • Scope and Objectives • Methodology SUPPORTED BY:
  • 5. Example: UK landfills SUPPORTED BY:
  • 6. UK landfill approach • Conceptual model • Screening assessment: Source-pathway-receptor analysis • Simple risk assessment • Complex risk assessment (probabilistic) SUPPORTED BY:
  • 8. 2. Properties of CO2 and associated substances SUPPORTED BY: CO2 H2S SO2
  • 9. Impairment • CO2 can be tolerated in quite high concentrations without permanent risk to health. • BUT if those exposed have key tasks to execute their response may be impaired. • THUS need to consider effects during emergency situations. Atmosphere in submarines is typically 4000ppm CO2!! Just below the TLV. Crews should not be impaired. However levels up to 10,000ppm are reported. SUPPORTED BY:
  • 10. 3. CO2 capture risks • The risk of scaling up the capture plants (Will the capture process work on large scale? More demonstration projects are needed to eliminate this risk). • The risk of fully CCS integrated system and influence on the power plants: o The power plant ability and flexibility to provide electricity without CO2 capture (capture no capture option) o The risk of shutting down the whole power plant if a problem occurred in the capture plant (This might occur if the power plant is fully integrated with the capture process (e.g. pre combustion) or because it could not cope with the regulation of low CO2 emissions anymore after the failure of the capture plant). • Specific technical risks per capture technology: o Post combustion capture: solvent degradation and equipment corrosion o Oxy-fuel combustion capture: boiler operation (burner design, flue gas recycle, temperature control and preventing air-in leakage) o Pre-combustion capture: hydrogen rich turbines operation and availability. • The risk of integrating the capture process to the power plant (e.g. steam extraction issues). • Environmental impact: chemical emissions to air, water and land, and overall life cycle of the facility (e.g. increase fuel consumption). SUPPORTED BY:
  • 11. 4. CO2 transport hazards • Low temperature releases • High pressures • Corrosion • High vapour density • Detection issues SUPPORTED BY:
  • 12. SUPPORTED BY: 15 January 2009 Vancouver-line rupture A running fracture – result of a test Fractured gasoline line – undetected damage Results of metal embrittlement
  • 13. 5. Geological storage risks • Predictive modelling of reservoir (‘performance assessment’), leakage scenarios and potential subsurface impacts • Experiments and natural analogues used to assess potential impacts of leakage scenarios • Both elements combine for a storage risk assessment SUPPORTED BY:
  • 14. Predictive modelling • Can vary from simple analytical equations to complex numerical models. • Based on knowledge from oil and gas industry, hydrogeology, theory. • Knowledge gained from recent experimentation and early demonstration projects. • Required by regulators. SUPPORTED BY:
  • 15. Modelling example Courtesy Permedia Research SUPPORTED BY:
  • 16. Modelling challenges • Coupling of processes • Effects of other substances • Old/abandoned wells • Effects of pressurisation and fluid displacement • Calibration of models – need more real projects to provide monitoring data SUPPORTED BY:
  • 17. Potential impacts • Good site selection means minimal probability of leakage • But need to know ‘what if ?’……… • Data from natural and industrial analogues • Laboratory experiments and models • Controlled field tests SUPPORTED BY:
  • 19. University of Nottingham SUPPORTED BY:
  • 20. The Latera caldera • The Latera caldera is about 150 km NW of Rome • Gas seeps occur throughout the heavily cultivated valley SUPPORTED BY: Prof Lombardi. URS
  • 21. Latera – leakage pathways 0 100 200 300 400 500 600 700 SUPPORTED BY: 1500 1000 500 0 CO2 flux (g m-2 d-1)
  • 22. U.R.S – Panera, Italy SUPPORTED BY:
  • 23. U.R.S. The impact of the gas is limited. Schools of fish swim around the gas plume SUPPORTED BY:
  • 24. Crystal Geyser, Utah, USA SUPPORTED BY:
  • 25. Monitoring and mitigation • Monitoring techniques established and demonstrated • Monitoring provides stakeholder reassurance and regulatory compliance • Mitigation strategies will be site-specific • Experience from CO2-EOR industry SUPPORTED BY:
  • 27. Conclusions • Capture and transport risks can be managed with existing engineering knowledge • Geological storage risks are site-specific • Predictive models provide performance assessment • Monitoring provides model calibration • Analogues provide information on potential impacts SUPPORTED BY:
  • 28. Location ALBERTA SUPPORTED BY: MANITOBA MONTANA WYOMING NORTH DAKOTA SOUTH DAKOTA EDMONTON SASKATOON WINNIPEG REGINA HELENA BISMARCK PIERRE CALGARY WILLISTON BASIN HUDSON BAY SASKATCHEW AN WEYBURN
  • 30. RA and Geological Storage of CO2 104% Increase 670% Increase And for just the final? year of each Phase: 2004 – 4 and 2011 – 57 SUPPORTED BY: 1,325% Increase
  • 31. Geological integrity SUPPORTED BY: • Reservoir Characteristics • Regional Characterization • System Model • Natural Analog • Mississippian hydrogeology • Aquitard characteristics • Assessing movement between reservoir and biosphere
  • 32. Containment vs biosphere rocks SUPPORTED BY:
  • 33. Background – Geosphere Geosphere risk assessment focuses on the deep subsurface and aims to identify and assess: • Assess the risk of CO2 escaping from the primary containment structure and reaching the biosphere (containment risk). • Assess the effectiveness of the Project in storing the target volume of CO2 within the confines of the Weyburn unit (effectiveness risk). • Identify areas where further research is required to address areas of high uncertainty. • Identify actions required to reduce risk, and areas where further research to develop risk management actions, is required. SUPPORTED BY:
  • 34. Background – biosphere Biosphere risk assessment focuses on surface and near surface processes and aims to assess: • Likely movement of CO2 within various components of the biosphere once it reaches the biosphere; and • Potential impacts on flora, fauna, people and property. SUPPORTED BY:
  • 35. Containment risk targets The mass of CO2 retained after 1,000 years should be at least 99% of the total CO2 that will be present immediately after the period of injection. • Therefore, if the CO2 mass in place at the conclusion of EOR is approximately 30 million tonnes, the maximum acceptable mass of CO2 lost from the system over the next 1,000 years is 300,000 tonnes (1% of 30 million tonnes). The Project has defined non-containment as any mass of CO2 that has left the geosphere and entered the biosphere. The minimum level of confidence that the target volume of CO2will be retained was set at 80%. Therefore, the maximum chance of losing more than the target volume of CO2 over the project period is 20%. • The target risk quotient (likelihood x consequences), is therefore 60,000 for the project (0.2 chance over 1,000 years x 300,000 tonnes). SUPPORTED BY:
  • 36. Process: Geosphere and Biosphere risk Building Capacity SUPPORTED BY: 36 Geosphere Risk Assessment Technical Inputs • Wellbore integrity research • Characterisation of reservoir characteristics & transport of CO2 • Seismicity of area • Characterisation of CO2 reactions in reservoir • Monitoring techniques & effectiveness Outputs • CO2 risk events (initiating event & pathway) & ranking • Mass of CO2 released if event occurs • Likelihood of each event occurring & releasing CO2 Biosphere Risk Assessment Other Technical Inputs • Characterisation of aquifers • Characterisation of surface water • Characterisation of soils / sediments • Behaviour of CO2 in soils, sediments, groundwater, surface water • Receptors in environment • Toxicology (animal, plant, human) Outputs • Risks to biosphere assets (ranking & severity) Stakeholder Engagement Stakeholder Values to Engage Acceptability of Risks Mitigation Measures
  • 37. Guide to assist in the quantification of likelihood SUPPORTED BY:
  • 38. Containment risk profile SUPPORTED BY:
  • 39. Identifying Biosphere assets most at risk from pathways 1000 100 10 1 0.1 0.01 0.001 0.0001 SUPPORTED BY: Initiating Events - Risk to Assets 0.00001 EOR Minor faults EOR Through faults Nat Seismicity-fault reactivation Nat Seismicity-new fracs Nat Seismicity-wells EOR Induced chem-fracs EOR Induced P/T-fault reactivation EOR Induced P/T-new fracs Wells Micros fracs, annuli Wells Casing corrosion Wells cement Risk Level Illness, injury, fatality Tourism Oil and gas Agriculture First Nation heritage Heritage Amenity - sensory, perception Amenity - recreation Species Habitat, communities, assemblages Ecosystem function Property/infrastructure Target Risk Level
  • 40. Update on RA methodologies • Recent project assessments, e.g. Shell Quest, Aquistore, Bell Creek • CSA Standard (joint US-Canada work) • US DOE & Weyburn Best Practice Manuals • EC Storage Directive Guidance • Many other R&D projects and programs… SUPPORTED BY:
  • 41. End. Advanced Workshop for CO2 Storage August 26-17, 2014 DF IPN ESIA Ticomán Auditorium SUPPORTED BY: