conclusion and summary of results introduction storage capacity

1
Conclusion and summary of results Introduction Site selection criteria Storage capacity estimation standards GeoCapacity recommendations The three-year EU-based GeoCapacity project was launched in January 2006 and is focussing on mapping large CO 2 point sources, infrastructure and potential for geological storage in European countries. GeoCapacity involves 25 European partners and 1 Chinese partner and the main objective of the project is to assess the European capacity for geological storage of CO 2 in deep saline aquifers, hydrocarbon and coal fields. Other key elements of the project is constructing a comprehensive GIS database of the results, further development of innovative and standardized methods for capacity assessment, economic modelling and site selection criteria and international cooperation, especially with China. The work includes full assessment and GIS mapping of countries which have not already been covered, and updates of previously covered territory. Figure 1 shows overview and status of the countries being covered and outlines the scope of work in bullet points. Thomas Vangkilde-Pedersen, Karen Lyng Anthonsen (Geological Survey of Denmark and Greenland, GEUS), Nikki Smith, Karen Kirk (British Geological Survey, BGS), Filip Neele, Bert van der Meer (TNO Built Environment and Geosciences), Yann Le Gallo, Dan Bossie-Codreanu, (Institut Francais du Pétrole, IFP), Adam Wojcicki (PBG Geophysical Exploration Company Limited), Yves-Michel Le Nindre (Bureau de Recherches Géologiques et Minières, BRGM), Chris Hendriks (Ecofys), Finn Dalhoff, Niels Peter Christensen (Vattenfall A/S, Generation Nordic – Thermal Power) Figure 1: Overview and status of countries covered in GeoCapacity and scope of work in bullet points. Identification of storage potential Storage capacity assessment begins with identifying sedimentary basins. The GeoCapacity project comprises most of the sedimentary basins suitable for geological storage of CO 2 located within the EU and the Central and Eastern European new member states and candidate countries. Figure 2 shows a European CO 2 storage prospectivity map with major CO 2 emission point sources. This is not a map of actual storage capacity, but a map of where to look for storage capacity. The understanding of the basic geological/technical site selection criteria is important. A basic set of criteria for selection of storage sites have been produced in GeoCapacity and described together with their related geological/physical parameters in a dedicated report. The basic site selection criteria is listed in bullet points in Figure 2. Figure 2: European CO 2 storage prospectivity map with major CO 2 emission point sources and basic site selection criteria listed in bullet points. GeoCapacity has adopted a simplified version of the storage potential pyramid suggested by the CSLF, see Figure 3. We have decided not to consider theoretical storage capacities and the estimates in the GIS database will be regional or trap specific effective storage capacities. We have developed capacity estimation standards based on the methodologies described by the CSLF or modifications hereof. Most important we suggest different approaches for the storage efficiency factor and the GeoCapacity recommendations specifically for deep saline aquifers are summarized below. The combined efforts of the many partners in GeoCapacity will result in a detailed and comprehensive GIS database containing updated data on CO 2 emissions, infrastructure such as pipelines, and the location of potential geological storage capacity in deep saline aquifers, hydrocarbon and coal fields. The emission data include technical information on the type of industry (power, cement, iron and steel, paper), fuel, technology, capacity, etc. The pipeline data include properties such as type (oil, gas, etc.), diameter and length. The storage data include geological information and physical properties of the reservoir and sealing formations, as well as estimates of the storage capacity of each of the identified potential storage possibilities. Figure 4 shows a preliminary summary of the results of GeoCapacity and an illustration of the content of the GIS database.The results will be summarized and published at the completion of the project, and the technical and geological results are intended to provide a solid foundation upon which the application of CCS in Europe can be judged and, hopefully, be declared sufficiently sound to warrant widespread application. Top: Practical capacity with economic and regulatory barriers applied to effective capacity and with matching of sources and sinks: Case studies Middle: Effective capacity with technical/geological cut-off limits applied to theoretical capacity: site specific/regional estimates in GIS Bottom: Theoretical capacity including large uneconomic/unrealistic volumes: regional estimates without storage efficiency. Not considered in GeoCapacity Figure 4: Illustration of the content of the GeoCapacity database and table with preliminary summary of GeoCapacity results. Figure 3: Simplified version of the storage potential pyramid suggested by CSLF. Note that the bottom part of the pyramid is left blank as we do not consider theoretical storage capacity. The success and results of GeoCapacity have been relying on the partners in the individual countries represented in the project and we would like to thank all of those individuals and institutions not represented in the list of authors of this paper for their work and efforts in the project. The consortium consists of Geological Survey of Denmark and Greenland; University of Sofia, Bulgaria; University of Zagreb, Croatia; Czech Geological Survey; Institute of Geology Tallinn University of Technology, Estonia; Bureau de Recherce de Geologie et Miniere, France; Institute Francais du Petrole; Bundesanstalt für Geologie und Rohstoffen, Germany; Institute for Geology and Mining Engineering, Greece; Eötvös Loránd Geophysical Institute of Hungary; Isituto Nazionale Oceanografiee Geofisica Sperimentale, Italy; Latvian Environment, Geology & Meteorology Agency; Institute of Geology and Geography, Lithuania; TNO Built Environment and Geosciences,The Netherlands; Ecofys,The Netherlands; Polish Academy of Science (MEERI); PBG Geophysical Exploration Company, Poland; GeoEcoMar, Romania; Dionyz Stur State Geological Institute, Slovakia; GEOINZENIRING, Slovenia; Instituto Geologico y Minerode Espana; British Geological Survey; EniTecnologie (Industry Partner), Italy; ENDESA Generacion (Industry Partner), Spain; Vattenfall Utveckling AB (Industry Partner), Sweden; Tsinghua University, China. GeoCapacity is co-funded by the EU 6th Framework Programme, contract no. 518318. Acknowledgements Assessing European capacity for geological storage of carbon dioxide – the EU GeoCapacity project Better Quality injektion site and source-sink match Increasing cost of storage Sufficient depth of reservoir for CO 2 to be in supercritical dense phase but not so deep that permeability and porosity is to low Sufficient integrity of seal to prevent CO 2 from migrating out of the storage site Sufficient CO 2 storage capacity to hold the required volumes of CO 2 from the sour- ce(s) e.g. lifetime of a power plant Effective petrophysical reservoir pro- perties (porosity and permeability) to ensure injectivity to be economically viable • Distinguish between estimates for bulk volume of regional aquifers and estimates for individual structural or strati- grafic traps • For estimates based on the bulk volume of regional aquifers we suggest a storage efficiency factor of 2 % based on work by US DOE • For trap estimates the choice of storage efficiency factor depends on whether the aquifer system is open, semi- closed or closed • For traps in open or semi-closed aquifer systems we suggest a rule-of-thumb approach with values for the storage efficiency factor in the range between 3% and 40 % for semi-closed low quality and open high quality reservoirs, respectively • For traps in closed aquifer systems we suggest an approach based on trap to aquifer volume ratio, rock and water compressibility and allowable average pressure increase with typical values for the storage efficiency factor in the range between 1 % and 20 % • Storage capacity estimates should always be accompanied with information on methodology, assumptions and approach for storage efficiency factor Slovakia 23 13708 134 Estonia 12 N/A N/A N/A Latvia 2 122 N/A N/A Lithuania 6 42 8 N/A Poland 188 3522 764 Czech Republic 78 2863 33 408 Hungary 23 2065 408 68 Romania 78 38 246 Bulgaria 52 4553 6 Albania 0 20 ? N/A FYROM 4 3881 N/A Croatia 5 4067 192 Spain 152 23363 N/A 196 Italy 212 4585 133 N/A Slovenia 7 153 6 N/A Bosnia-Herzegovina 9 296 N/A Germany 465 22747 2318 779 Luxemburg 2 N/A N/A N/A The Netherlands 92 438 3393 France 131 21555 81 Greece 69 2349 35 N/A United Kingdom 259 38721 9942 Denmark 28 16626 810 N/A Norway 28 182215 12630 N/A Belgium 58 1392 N/A Total 1984 349321 31138 1451 Country Annual CO 2 emissions from large point sources (Mt) CO 2 storage capacity in deep saline aquifers (Mt) CO 2 storage capacity in hydrocarbon fields (Mt) CO 2 storage capacity in coal fields (Mt) • Mapping of major CO 2 emission point sour- ces and infrastructure • Assessment and mapping of potential for geological storage of CO 2 • Guidelines for estimation of geological sto- rage capacity • Technical site selection criteria and ranking methodology • Development of GIS mapping and economic analysis methodologies • Analysis of source-transport-sink scenarios and economical evaluations • International collaborative activities with China and other CSLF countries Full country evaluation Neighbour country review Full country evaluation work initiated in CASTOR GESTCO country, updated GESTCO country, no update BaseMap Pipelines Large CO 2 point sources Aquifers Hydrocarbon fields Coal fields Large CO 2 point sources Sedimentary basins

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Page 1: Conclusion and summary of results Introduction Storage capacity

Conclusion and summary of results

Introduction

Site selection criteria

Storage capacity estimation standards

GeoCapacity recommendations

The three-year EU-based GeoCapacity project was launched in January 2006 and is focussing on mapping large CO2 point sources, infrastructure and potential for geological storage in European countries. GeoCapacity involves 25 European partners and 1 Chinese partner and the main objective of the project is to assess the European capacity for geological storage of CO2 in deep saline aquifers, hydrocarbon and coal fields. Other key elements of the project is constructing a comprehensive GIS database of the results, further development of innovative and standardized methods for capacity assessment, economic modelling and site selection criteria and international cooperation, especially with China. The work includes full assessment and GIS mapping of countries which have not already been covered, and updates of previously covered territory. Figure 1 shows overview and status of the countries being covered and outlines the scope of work in bullet points.

Thomas Vangkilde-Pedersen, Karen Lyng Anthonsen (Geological Survey of Denmark and Greenland, GEUS), Nikki Smith, Karen Kirk (British Geological Survey, BGS), Filip Neele, Bert van der Meer (TNO Built Environment and Geosciences), Yann Le Gallo, Dan Bossie-Codreanu, (Institut Francais du Pétrole, IFP), Adam Wojcicki (PBG Geophysical Exploration Company Limited), Yves-Michel Le Nindre (Bureau de Recherches Géologiques et Minières, BRGM), Chris Hendriks (Ecofys), Finn Dalhoff, Niels Peter Christensen (Vattenfall A/S, Generation Nordic – Thermal Power)

Figure 1: Overview and status of countries covered in GeoCapacity and scope of work in bullet points.

Identification of storage potential

Storage capacity assessment begins with identifying sedimentary basins. The GeoCapacity project comprises most of the sedimentary basins suitable for geological storage of CO2 located within the EU and the Central and Eastern European new member states and candidate countries. Figure 2 shows a European CO2 storage prospectivity map with major CO2 emission point sources. This is not a map of actual storage capacity, but a map of where to look for storage capacity.

The understanding of the basic geological/technical site selection criteria is important. A basic set of criteria for selection of storage sites have been produced in GeoCapacity and described together with their related geological/physical parameters in a dedicated report. The basic site selection criteria is listed in bullet points in Figure 2.

Figure 2: European CO2 storage prospectivity map with major CO2 emission point sources and basic site selection criteria listed in bullet points.

GeoCapacity has adopted a simplified version of the storage potential pyramid suggested by the CSLF, see Figure 3. We have decided not to consider theoretical storage capacities and the estimates in the GIS database will be regional or trap specific effective storage capacities. We have developed capacity estimation standards based on the methodologies described by the CSLF or modifications hereof. Most important we suggest different approaches for the storage efficiency factor and the GeoCapacity recommendations specifically for deep saline aquifers are summarized below.

The combined efforts of the many partners in GeoCapacity will result in a detailed and comprehensive GIS database containing updated data on CO2 emissions, infrastructure such as pipelines, and the location of potential geological storage capacity in deep saline aquifers, hydrocarbon and coal fields. The emission data include technical information on the type of industry (power, cement, iron and steel, paper), fuel, technology, capacity, etc. The pipeline data include properties such as type (oil, gas, etc.), diameter and length. The storage data include geological information and physical properties of the reservoir and sealing formations, as well as estimates of the storage capacity of each of the identified potential storage possibilities. Figure 4 shows a preliminary summary of the results of GeoCapacity and an illustration of the content of the GIS database.The results will be summarized and published at the completion of the project, and the technical and geological results are intended to provide a solid foundation upon which the application of CCS in Europe can be judged and, hopefully, be declared sufficiently sound to warrant widespread application.

Top: Practical capacity with economic and regulatory barriers applied to effective capacity and with matching of sources and sinks: Case studies

Middle: Effective capacity with technical/geological cut-off limits applied to theoretical capacity: site specific/regional estimates in GIS

Bottom: Theoretical capacity including large uneconomic/unrealistic volumes: regional estimates without storage efficiency. Not considered in GeoCapacity

Figure 4: Illustration of the content of the GeoCapacity database and table with preliminary summary of GeoCapacity results.

Figure 3: Simplified version of the storage potential pyramid suggested by CSLF. Note that the bottom part of the pyramid is left blank as we do not consider theoretical storage capacity.

The success and results of GeoCapacity have been relying on the partners in the individual countries represented in the project and we would like to thank all of those individuals and institutions not represented in the list of authors of this paper for their work and efforts in the project. The consortium consists of Geological Survey of Denmark and Greenland; University of Sofia, Bulgaria; University of Zagreb, Croatia; Czech Geological Survey; Institute of Geology Tallinn University of Technology, Estonia; Bureau de Recherce de Geologie et Miniere, France; Institute Francais du Petrole; Bundesanstalt für Geologie und Rohstoffen, Germany; Institute for Geology and Mining Engineering, Greece; Eötvös Loránd Geophysical Institute of Hungary; Isituto Nazionale Oceanografiee Geofisica Sperimentale, Italy; Latvian Environment, Geology & Meteorology Agency; Institute of Geology and Geography, Lithuania; TNO Built Environment and Geosciences,The Netherlands; Ecofys,The Netherlands; Polish Academy of Science (MEERI); PBG Geophysical Exploration Company, Poland; GeoEcoMar, Romania; Dionyz Stur State Geological Institute, Slovakia; GEOINZENIRING, Slovenia; Instituto Geologico y Minerode Espana; British Geological Survey; EniTecnologie (Industry Partner), Italy; ENDESA Generacion (Industry Partner), Spain; Vattenfall Utveckling AB (Industry Partner), Sweden; Tsinghua University, China. GeoCapacity is co-funded by the EU 6th Framework Programme, contract no. 518318.

Acknowledgements

Assessing European capacity for geological storage of carbon dioxide– the EU GeoCapacity project

Better Quality injektion

site and source-sink matchIncr

easin

g co

st o

f sto

rage

• Sufficient depth of reservoir for CO2 to be in supercritical dense phase but not so deep that permeability and porosity is to low

• Sufficient integrity of seal to prevent CO2 from migrating out of the storage site

• Sufficient CO2 storage capacity to hold the required volumes of CO2 from the sour- ce(s) e.g. lifetime of a power plant

• Effective petrophysical reservoir pro- perties (porosity and permeability) to ensure injectivity to be economically viable

• Distinguish between estimates for bulk volume of regional aquifers and estimates for individual structural or strati- grafic traps

• For estimates based on the bulk volume of regional aquifers we suggest a storage efficiency factor of 2 % based on work by US DOE

• For trap estimates the choice of storage efficiency factor depends on whether the aquifer system is open, semi- closed or closed

• For traps in open or semi-closed aquifer systems we suggest a rule-of-thumb approach with values for the storage efficiency factor in the range between 3% and 40 % for semi-closed low quality and open high quality reservoirs, respectively

• For traps in closed aquifer systems we suggest an approach based on trap to aquifer volume ratio, rock and water compressibility and allowable average pressure increase with typical values for the storage efficiency factor in the range between 1 % and 20 %

• Storage capacity estimates should always be accompanied with information on methodology, assumptions and approach for storage efficiency factor

Slovakia 23 13708 134

Estonia 12 N/A N/A N/A

Latvia 2 122 N/A N/A

Lithuania 6 42 8 N/A

Poland 188 3522 764

Czech Republic 78 2863 33 408

Hungary 23 2065 408 68

Romania 78 38 246

Bulgaria 52 4553 6

Albania 0 20 ? N/A

FYROM 4 3881 N/A

Croatia 5 4067 192

Spain 152 23363 N/A 196

Italy 212 4585 133 N/A

Slovenia 7 153 6 N/A

Bosnia-Herzegovina 9 296 N/A

Germany 465 22747 2318 779

Luxemburg 2 N/A N/A N/A

The Netherlands 92 438 3393

France 131 21555 81

Greece 69 2349 35 N/A

United Kingdom 259 38721 9942

Denmark 28 16626 810 N/A

Norway 28 182215 12630 N/A

Belgium 58 1392 N/A

Total 1984 349321 31138 1451

Country

Annual CO2emissions from

large point sources(Mt)

CO2 storagecapacity in deepsaline aquifers

(Mt)

CO2 storagecapacity in

hydrocarbon fields(Mt)

CO2 storagecapacity incoal fields

(Mt)

• Mapping of major CO2 emission point sour- ces and infrastructure

• Assessment and mapping of potential for geological storage of CO2

• Guidelines for estimation of geological sto- rage capacity

• Technical site selection criteria and ranking methodology

• Development of GIS mapping and economic analysis methodologies

• Analysis of source-transport-sink scenarios and economical evaluations

• International collaborative activities with China and other CSLF countries

Full country evaluationNeighbour country reviewFull country evaluation work initiated in CASTORGESTCO country, updatedGESTCO country, no updateBaseMap

PipelinesLarge CO2 point sourcesAquifersHydrocarbon fieldsCoal fields

Large CO2 point sourcesSedimentary basins