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Premium member Presentation Transcript Geologic Storage of CO2: Geologic Storage of CO2 Next Generation Coal Howard Herzog MIT Laboratory for Energy and Environment October 6, 2005IPCC Special Report: IPCC Special Report Intergovernmental Panel on Climate Change (IPCC) Working Group III Special Report on Carbon Dioxide Capture and Storage Accepted September 26, 2005 Summary for Policymakers on-line at www.ipcc.chIPCC Special ReportOverview: IPCC Special Report Overview Storage of CO2 in deep, onshore or offshore, geological formations uses many of the same technologies that have been developed by the oil and gas industry and has been proven to be economically feasible under specific conditions for oil and gas fields and saline formations, but not yet for storage in unminable coal beds. Carbon dioxide can be stored in several geological targets, usually as a supercritical phase: Carbon dioxide can be stored in several geological targets, usually as a supercritical phase Experience and Evolution from Oil & Gas Operations: Experience and Evolution from Oil & Gas Operations Acid Gas Injection Enhanced Oil Recovery (EOR) Natural Gas Storage CO2 Transport Acid Gas Injection: Acid Gas Injection First began: Acheson Field, 1989 In 2001, nearly 6.5 Billion cubic feet (360,000 tonnes) of acid gas injected at > 30 locations. Between 50 thousand and 5 million scf per day. Compositions vary but many over 90% CO2. Largest: Westcoast Energy injects 28 million scf per day (Sleipner: 50 million scf of CO2 per day) Acid Gas Disposal sites in Alberta, Canada. Map provided by Nickle’s New Technology Magazine, September 13, 2002 Enhanced Oil Recovery: Enhanced Oil Recovery First began: Scurry County, Texas, 1972 In 2000, 84 commercial or research-level CO2-EOR projects operational worldwide (72 in US) Rangely Field (Colorado) Started CO2 injection in 1986 346 producers, 235 injectors Injection rate of about 150 million scf/day (8300 t/d) Estimated leak rate of <170 tons/yr out of 23 million tonnes purchased (<0.001%/yr) Source: Applied Geochemistry, vol. 18, pp.1825-1838 (2003). Natural Gas Storage: Natural Gas Storage First began: 1915 in a partially depleted gas field. Total storage 1955: 2.1 Tcf Total storage 1985: 8 Tcf Volume of 8 Tcf will store one year of all US power plant CO2 emissions Since 1980’s, storage capacity has stabilized at around 8 Tcf while capacity to deliver has increased Total US consumption 2000 > 22 Tcf Natural Gas Storage by Type available at http://www.fetc.doe.gov/scng/trans-dist/ngs/storage-ov.html CO2 Transport: CO2 Transport Extensive network of CO2 pipeline stretching nearly 2000 miles, mostly in the United States 49CFR195 addresses transport of hazardous liquids and CO2 CO2 pipelines classified as High Volatile Low Hazard and Low Risk. Canyon Reef Carriers (CRC) pipeline, 1972 Relatively few failures (with no injuries) Extends 140 miles from McCarney, Texas, to Kinder Morgan’s SACROC field Size: 16 inches in diameter with capacity to deliver up to 240 MMscf of CO2 per day IPCC Special ReportOverview: IPCC Special Report Overview Storage of CO2 in deep, onshore or offshore, geological formations uses many of the same technologies that have been developed by the oil and gas industry and has been proven to be economically feasible under specific conditions for oil and gas fields and saline formations, but not yet for storage in unminable coal beds. … Three industrial-scale storage projects are in operation: the Sleipner project in an offshore saline formation in Norway, the Weyburn EOR project in Canada, and the In Salah project in a gas field in Algeria. Others are planned. CO2 Injection ProjectsMillion Tonne per Year Scale: CO2 Injection Projects Million Tonne per Year ScaleIPCC Special ReportCapacity: IPCC Special Report Capacity Available evidence suggests that worldwide, it is likely that there is a technical potential of at least about 2,000 GtCO2 (545 GtC) of storage capacity in geological formations. There could be a much larger potential for geological storage in saline formations, but the upper limit estimates are uncertain due to lack of information and an agreed methodology. The capacity of oil and gas reservoirs is better known. Technical storage capacity in coal beds is much smaller and less well known. Site Selection: Site Selection Reservoir Characteristics Injectivity Accessible pore volume Containment Reachable from CO2 Source IPCC Special ReportRegulation: IPCC Special Report Regulation Some regulations for operations in the subsurface exist that may be relevant or in some cases directly applicable to geological storage, but few countries have specifically developed legal or regulatory frameworks for long-term CO2 storage. Existing laws and regulations regarding inter alia mining, oil and gas operations, pollution control, waste disposal, drinking water, treatment of high-pressure gases, and subsurface property rights may be relevant to geological CO2 storage. Long-term liability issues associated with the leakage of CO2 to the atmosphere and local environmental impacts are generally unresolved. Some States take on long-term responsibility in situations comparable to CO2 storage, such as underground mining operations. Permitting - Current: Permitting - Current EPA Underground Injection Control (UIC) Program Created under the Safe Drinking Water Act (1974) Almost all underground injections must be authorized by permit Exemption for natural gas storage States may receive primacy for permitting – some states currently do allow injection into deep saline aquifers Five classes of UIC injection wells Relaxed standards for injection wells related to enhanced oil recovery (CO2-EOR) No class specific to carbon sequestration Pilot projects have been permitted under the Class V experimental well categoryMeasurement, Monitoring, and Verification: Measurement, Monitoring, and Verification Role of MMV Understand key features, effects, & processes Injection management Delineate and identify leakage risk and leakage Provide early warnings of failure Verify storage for accounting and crediting Currently, there are abundant viable tools and methods, but MMV systems still need to be developedIPCC Special ReportLeakage: IPCC Special Report Leakage Observations from engineered and natural analogues as well as models suggest that the fraction retained in appropriately selected and managed geological reservoirs is very likely to exceed 99% over 100 years, and is likely to exceed 99% over 1,000 years. For well-selected, designed and managed geological storage sites, the vast majority of the CO2 will gradually be immobilized by various trapping mechanisms and, in that case, could be retained for up to millions of years. Because of these mechanisms, storage could become more secure over longer timeframes. Storage Mechanisms: Storage Mechanisms Physical trapping Impermeable cap rock Either geometric or hydrodynamic stability Residual phase trapping Capillary forces immobilized fluids Sensitive to pore geometry (<25% pore vol.) Solution/Mineral Trapping Slow kinetics High permanence Gas adsorption For organic minerals only (coals, oil shales) Leakage: Leakage Some leakage is inevitable – question is whether the leakage will have any impacts on HSE or climate (there is active debate on value of temporary storage) Pathways Well integrity (cement damage) Fracturing Faulting Permeation and Spillover Leakage rate not a simple logistic function (i.e., x% per year) IPCC Special ReportRisks: IPCC Special Report Risks With appropriate site selection informed by available subsurface information, a monitoring program to detect problems, a regulatory system, and the appropriate use of remediation methods to stop or control CO2 releases if they arise, the local health, safety and environment risks of geological storage would be comparable to risks of current activities such as natural gas storage, EOR, and deep underground disposal of acid gas. … Impacts of elevated CO2 concentrations in the shallow subsurface could include lethal effects on plants and subsoil animals, and contamination of groundwater. High fluxes in conjunction with stable atmospheric conditions could lead to local high CO2 concentrations in the air that could harm animals or people. Pressure build-up caused by CO2 injection could trigger small seismic events. Types of Risk: Types of Risk Operational Risks Managed today Climate Risks Liability that can be handled In Situ Risks Formation leaks to the surface Migration within formation Seismic eventsIPCC Special ReportAccounting: IPCC Special Report Accounting The current IPCC Guidelines do not include methods specific to estimating emissions associated with CCS. The general guidance provided by the IPCC can be applied to CCS. A few countries currently do so, in combination with their national methods for estimating emissions. The IPCC guidelines themselves do not yet provide specific methods for estimating emissions associated with CCS. These are expected to be provided in the 2006 IPCC Guidelines for National Greenhouse Gas Inventories…Geological StorageGeneral Conclusions: Geological Storage General Conclusions Practical issues CO2 transport, injection and storage has been occurring since the early 1970’s. Tens of millions of tons of CO2 are injected annually. Further scale up would be required to play significant role in US power sector CO2 abatement. All key technologies and practices are in current commercial operation. No “breakthrough” technological innovations appear necessary for this scale-up. Volume of the total annual US power sector CO2 emissions are in the same order of magnitude volume of other key US gas and fluids currently injected and stored underground (e.g., natural gas, wastewater in Florida, oilfield brines) Environmental issues Based on our study of analogues, short term (three-decade) and local environmental risks are well understood and can be managed by current industry best practices. Long term (beyond three decade) risks are by definition uncertain but no evidence to date suggests significant leakage. Best near term course of action is to conduct pilot projects to gather information that will allow us to address the issue of long term risks and uncertainties.Contact Information: Contact Information Howard Herzog MIT Laboratory for Energy and the Environment (LFEE) Room E40-447 Phone: 617-253-0688 E-mail: hjherzog@mit.edu Web Site: sequestration.mit.edu You do not have the permission to view this presentation. In order to view it, please contact the author of the presentation.
hh Fenwick Download Post to : URL : Related Presentations : Share Add to Flag Embed Email Send to Blogs and Networks Add to Channel Uploaded from authorPOINTLite Insert YouTube videos in PowerPont slides with aS Desktop Copy embed code: (To copy code, click on the text box) Embed: URL: Thumbnail: WordPress Embed Customize Embed The presentation is successfully added In Your Favorites. Views: 188 Category: Entertainment License: All Rights Reserved Like it (0) Dislike it (0) Added: December 17, 2007 This Presentation is Public Favorites: 0 Presentation Description No description available. Comments Posting comment... Premium member Presentation Transcript Geologic Storage of CO2: Geologic Storage of CO2 Next Generation Coal Howard Herzog MIT Laboratory for Energy and Environment October 6, 2005IPCC Special Report: IPCC Special Report Intergovernmental Panel on Climate Change (IPCC) Working Group III Special Report on Carbon Dioxide Capture and Storage Accepted September 26, 2005 Summary for Policymakers on-line at www.ipcc.chIPCC Special ReportOverview: IPCC Special Report Overview Storage of CO2 in deep, onshore or offshore, geological formations uses many of the same technologies that have been developed by the oil and gas industry and has been proven to be economically feasible under specific conditions for oil and gas fields and saline formations, but not yet for storage in unminable coal beds. Carbon dioxide can be stored in several geological targets, usually as a supercritical phase: Carbon dioxide can be stored in several geological targets, usually as a supercritical phase Experience and Evolution from Oil & Gas Operations: Experience and Evolution from Oil & Gas Operations Acid Gas Injection Enhanced Oil Recovery (EOR) Natural Gas Storage CO2 Transport Acid Gas Injection: Acid Gas Injection First began: Acheson Field, 1989 In 2001, nearly 6.5 Billion cubic feet (360,000 tonnes) of acid gas injected at > 30 locations. Between 50 thousand and 5 million scf per day. Compositions vary but many over 90% CO2. Largest: Westcoast Energy injects 28 million scf per day (Sleipner: 50 million scf of CO2 per day) Acid Gas Disposal sites in Alberta, Canada. Map provided by Nickle’s New Technology Magazine, September 13, 2002 Enhanced Oil Recovery: Enhanced Oil Recovery First began: Scurry County, Texas, 1972 In 2000, 84 commercial or research-level CO2-EOR projects operational worldwide (72 in US) Rangely Field (Colorado) Started CO2 injection in 1986 346 producers, 235 injectors Injection rate of about 150 million scf/day (8300 t/d) Estimated leak rate of <170 tons/yr out of 23 million tonnes purchased (<0.001%/yr) Source: Applied Geochemistry, vol. 18, pp.1825-1838 (2003). Natural Gas Storage: Natural Gas Storage First began: 1915 in a partially depleted gas field. Total storage 1955: 2.1 Tcf Total storage 1985: 8 Tcf Volume of 8 Tcf will store one year of all US power plant CO2 emissions Since 1980’s, storage capacity has stabilized at around 8 Tcf while capacity to deliver has increased Total US consumption 2000 > 22 Tcf Natural Gas Storage by Type available at http://www.fetc.doe.gov/scng/trans-dist/ngs/storage-ov.html CO2 Transport: CO2 Transport Extensive network of CO2 pipeline stretching nearly 2000 miles, mostly in the United States 49CFR195 addresses transport of hazardous liquids and CO2 CO2 pipelines classified as High Volatile Low Hazard and Low Risk. Canyon Reef Carriers (CRC) pipeline, 1972 Relatively few failures (with no injuries) Extends 140 miles from McCarney, Texas, to Kinder Morgan’s SACROC field Size: 16 inches in diameter with capacity to deliver up to 240 MMscf of CO2 per day IPCC Special ReportOverview: IPCC Special Report Overview Storage of CO2 in deep, onshore or offshore, geological formations uses many of the same technologies that have been developed by the oil and gas industry and has been proven to be economically feasible under specific conditions for oil and gas fields and saline formations, but not yet for storage in unminable coal beds. … Three industrial-scale storage projects are in operation: the Sleipner project in an offshore saline formation in Norway, the Weyburn EOR project in Canada, and the In Salah project in a gas field in Algeria. Others are planned. CO2 Injection ProjectsMillion Tonne per Year Scale: CO2 Injection Projects Million Tonne per Year ScaleIPCC Special ReportCapacity: IPCC Special Report Capacity Available evidence suggests that worldwide, it is likely that there is a technical potential of at least about 2,000 GtCO2 (545 GtC) of storage capacity in geological formations. There could be a much larger potential for geological storage in saline formations, but the upper limit estimates are uncertain due to lack of information and an agreed methodology. The capacity of oil and gas reservoirs is better known. Technical storage capacity in coal beds is much smaller and less well known. Site Selection: Site Selection Reservoir Characteristics Injectivity Accessible pore volume Containment Reachable from CO2 Source IPCC Special ReportRegulation: IPCC Special Report Regulation Some regulations for operations in the subsurface exist that may be relevant or in some cases directly applicable to geological storage, but few countries have specifically developed legal or regulatory frameworks for long-term CO2 storage. Existing laws and regulations regarding inter alia mining, oil and gas operations, pollution control, waste disposal, drinking water, treatment of high-pressure gases, and subsurface property rights may be relevant to geological CO2 storage. Long-term liability issues associated with the leakage of CO2 to the atmosphere and local environmental impacts are generally unresolved. Some States take on long-term responsibility in situations comparable to CO2 storage, such as underground mining operations. Permitting - Current: Permitting - Current EPA Underground Injection Control (UIC) Program Created under the Safe Drinking Water Act (1974) Almost all underground injections must be authorized by permit Exemption for natural gas storage States may receive primacy for permitting – some states currently do allow injection into deep saline aquifers Five classes of UIC injection wells Relaxed standards for injection wells related to enhanced oil recovery (CO2-EOR) No class specific to carbon sequestration Pilot projects have been permitted under the Class V experimental well categoryMeasurement, Monitoring, and Verification: Measurement, Monitoring, and Verification Role of MMV Understand key features, effects, & processes Injection management Delineate and identify leakage risk and leakage Provide early warnings of failure Verify storage for accounting and crediting Currently, there are abundant viable tools and methods, but MMV systems still need to be developedIPCC Special ReportLeakage: IPCC Special Report Leakage Observations from engineered and natural analogues as well as models suggest that the fraction retained in appropriately selected and managed geological reservoirs is very likely to exceed 99% over 100 years, and is likely to exceed 99% over 1,000 years. For well-selected, designed and managed geological storage sites, the vast majority of the CO2 will gradually be immobilized by various trapping mechanisms and, in that case, could be retained for up to millions of years. Because of these mechanisms, storage could become more secure over longer timeframes. Storage Mechanisms: Storage Mechanisms Physical trapping Impermeable cap rock Either geometric or hydrodynamic stability Residual phase trapping Capillary forces immobilized fluids Sensitive to pore geometry (<25% pore vol.) Solution/Mineral Trapping Slow kinetics High permanence Gas adsorption For organic minerals only (coals, oil shales) Leakage: Leakage Some leakage is inevitable – question is whether the leakage will have any impacts on HSE or climate (there is active debate on value of temporary storage) Pathways Well integrity (cement damage) Fracturing Faulting Permeation and Spillover Leakage rate not a simple logistic function (i.e., x% per year) IPCC Special ReportRisks: IPCC Special Report Risks With appropriate site selection informed by available subsurface information, a monitoring program to detect problems, a regulatory system, and the appropriate use of remediation methods to stop or control CO2 releases if they arise, the local health, safety and environment risks of geological storage would be comparable to risks of current activities such as natural gas storage, EOR, and deep underground disposal of acid gas. … Impacts of elevated CO2 concentrations in the shallow subsurface could include lethal effects on plants and subsoil animals, and contamination of groundwater. High fluxes in conjunction with stable atmospheric conditions could lead to local high CO2 concentrations in the air that could harm animals or people. Pressure build-up caused by CO2 injection could trigger small seismic events. Types of Risk: Types of Risk Operational Risks Managed today Climate Risks Liability that can be handled In Situ Risks Formation leaks to the surface Migration within formation Seismic eventsIPCC Special ReportAccounting: IPCC Special Report Accounting The current IPCC Guidelines do not include methods specific to estimating emissions associated with CCS. The general guidance provided by the IPCC can be applied to CCS. A few countries currently do so, in combination with their national methods for estimating emissions. The IPCC guidelines themselves do not yet provide specific methods for estimating emissions associated with CCS. These are expected to be provided in the 2006 IPCC Guidelines for National Greenhouse Gas Inventories…Geological StorageGeneral Conclusions: Geological Storage General Conclusions Practical issues CO2 transport, injection and storage has been occurring since the early 1970’s. Tens of millions of tons of CO2 are injected annually. Further scale up would be required to play significant role in US power sector CO2 abatement. All key technologies and practices are in current commercial operation. No “breakthrough” technological innovations appear necessary for this scale-up. Volume of the total annual US power sector CO2 emissions are in the same order of magnitude volume of other key US gas and fluids currently injected and stored underground (e.g., natural gas, wastewater in Florida, oilfield brines) Environmental issues Based on our study of analogues, short term (three-decade) and local environmental risks are well understood and can be managed by current industry best practices. Long term (beyond three decade) risks are by definition uncertain but no evidence to date suggests significant leakage. Best near term course of action is to conduct pilot projects to gather information that will allow us to address the issue of long term risks and uncertainties.Contact Information: Contact Information Howard Herzog MIT Laboratory for Energy and the Environment (LFEE) Room E40-447 Phone: 617-253-0688 E-mail: hjherzog@mit.edu Web Site: sequestration.mit.edu