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Development and Evaluation of Innovative Strategies for Mineral and Physical Trapping of CO2 in Geological Formations and of Long-Term Cap Rock Integrity*
By
R. Meyer1, R. Azzam2, M. Back3, A. Bielinski4, A. Busch5, H. Class4, C. Clauser1, O. Dogan4, T. Fernández-Steeger2, R. Helmig4, T. Kempka2, B. M. Krooss5, M. Kühn6, R. Littke5, S. Peiffer3, H. Stanjek7, and M. Waschbüsch2
Search and Discovery Article #80009 (2008)
Posted February 7, 2007
*Reprinted, with some modification in format, from AAPG European Region Newsletter, December 2007, v.2 (http://www.aapg.org/europe/newsletters/index.cfm), p. 4-5, with kind permission of the authors and AAPG European Region Newsletter, Hugo Matias, Editor ([email protected]).
1RWTH Aachen University, E.ON Energy Research Centre, Applied Geophysics and Geothermal Energy, Lochnerstrasse 4-20, D-52056 Aachen, Germany ([email protected])
2RWTH Aachen University, Engineering Geology and Hydrogeology, Germany
3University of Bayreuth, Hydrology, Bayreuth, Germany
4University of Stuttgart, Hydraulic Engineering, Stuttgart, Germany
5RWTH Aachen University, Geology and Geochemistry of Petroleum and Coal, Aachen, Germany
6GeoForschungsZentrum Potsdam GFZ, Potsdam, Germany
7RWTH Aachen University, Clay and Interface Mineralogy, Aachen, Germany
In order to retard further global warming, carbon capture and storage (CCS) is acknowledged as a technically and geoscientifically feasible option for reducing green house gas emissions into the atmosphere. Amongst several other R&D projects related to carbon dioxide storage in depleted hydrocarbon reservoirs, saline aquifers, or unminable coal seams, the R&D project CO2TRAP (http://www.co2trap.org) focuses on mineral and physical trapping of CO2 as a permanent and inherently safe storage option.
The CO2TRAP project is currently performed within the German R&D program “Geotechnologien, Investigation, Use and Protection of the Underground” (http://www.geotechnologien.de/index_en.html), which is funded by the Federal Ministry of Education and Research (BMBF) and the German Science Foundation (DFG). Besides from this, the project is supported by several industry partners, which are the power generating company RWE Power and the E&P company RWE Dea, Evonik New Energies GmbH as an electric power and heat provider, Deutsche Steinkohle AG DSK, involved in German hard coal mining, and, DMT, who offers, amongst others, services in mining, exploration, systems, and civil engineering.
In the scope of the CO2TRAP project, we study and evaluate two different trapping technologies, mineralogical and physical, applied to future potential candidate storage sites, geothermal reservoirs, and abandoned coal mines. The project also considers site specific geological and technical settings, as well as the availability of different reactive raw materials.
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Technology I – Mineral Trapping: Precipitation of Aqueous CO2 as Calcium Carbonate in Formations Containing Calcium Sulphates and Feldspars In order to transform aqueous CO2 into geochemically more stable calcite (CaCO3), one technology studies the potential of combining CO2 sequestration with the production of ecologically desirable geothermal heat or electric power. From the economical point of view, costs for sequestration in deep saline aquifers could be transformed into a benefit. The technical and scientific feasibility of mineral trapping is studied in a well balanced combination of laboratory experiments (including batch-, mixed flow rate- and core flooding experiments) and numerical modelling using the simulation codes SHEMAT (Clauser, 2003) and PHREEQC (Parkhurst and Appelo, 1999). The transformation of CO2 into calcite is governed by several site specific geological and operative parameters; e.g., the porosity, permeability, temperature, the salinity, alkalinity, availability of reactive components, as well as the pumping rate and associated flow velocities of the geothermal brine. Mass balance calculations are used to calculate the maximum storage potentials of potential geothermal reservoirs (Stralsund, North Germany) as well as to reveal the limiting operative and geological factors for this technology. With respect to the operative lifetime of a geothermal plant, limitations are given by the maximum amount of CO2 dissolved in the geothermal brine, followed by the solubility of anhydrite as a natural source for Ca2+ ions. As an alternative attractive technology for mineral trapping, the potential of CO2 trapping by reactions of flue gas with alkaline fly ashes (called ALCATRAP, ALkaline CArbon TRAPping) investigates the use of fly ashes, a by-product of coal combustion for power generation. Using an autoclave system, reaction kinetics between alkaline lignite fly ashes and aqueous CO2 are studied at various solid-liquid-ratios, partial pressures of CO2, stirring rates, and temperatures. As a result, the technically feasible and promising technology ALCATRAP has a predicted potential to neutralize about 2% of the annual CO2 emissions of a coal fired power plant. Therefore, it is planned to demonstrate the technology in an industrial-scale pilot plant in the next project phase. A consortium of academic, research, and industry partners plans to optimize the technology in terms of process parameters and available materials at a real waste or biomass incineration plant.
Besides mineral trapping of CO2 as discussed in Technology I, options for physical trapping of CO2 in coal mines are studied in two conceptual studies: The sorptive CO2 storage on (i) residual coal and bedrock and on (ii) mining waste. Due to the high physical sorption capacity of coal and dispersed organic matter, unminable coal seams may provide an opportunity for the long-term CO2 storage and enhanced abandoned mine methane production (CO2-EAMM). As coal mining in Germany and some other European countries is now declining and will eventually phase out in the next decades, one conceptual approach investigates the feasibility of sorptive CO2 storage on residual coal and organic matter in gob areas and formation damage zones of abandoned coal mines. The main experimental and technical challenge consists in integrating physicochemical data with engineering and mining information. Based on comprehensive experimental studies on foreign and German (Ruhr and Saar Coal Districts) coal samples, CO2 storage potentials of abandoned coal mines are predicted. Another approach considers underground CO2 storage on mining wastes. Proven storage techniques developed by German mining research were adapted for underground CO2 storage in gob areas created by longwall workings (Figure 1). Using drag pipes mounted at the roof support shields, the injection of CO2 adsorbed on mining wastes proceeds with the advancement of the longwall face. Here, security considerations as well as the potential of subsidence mitigation by hydraulic stowage using mining wastes are addressed. Potential risks of CO2 outgassing into the longwall face or adjacent workings are determined by means of numerical multi-phase and multi-component flow simulations. These allow the evaluation of CO2 storage efficiency and security as well as the development and verification of general CO2 injection and sealing strategies in geological formations. One case study was chosen to estimate CO2 storage potentials in abandoned coal mines in Germany: The coal mine “Westfalen” was flooded completely in 2007 and therefore reached hydrostatic pressure conditions of about 10 MPa (according to an average depth of the mine of 1000 m) and approximately 40°C - 45°C. The CO2 storage potential of the mine is calculated to amount up to 2.70 Mt CO2 at the assumed reservoir conditions, mainly absorbed on the residual coal but also dissolved in formation waters. The CO2 storage potential on mining wastes was estimated in a case study considering the utilization of the simultaneous CO2 and mining waste injection during longwall mining (Figure 2) in Germany for the year 2004. A total CO2 storage potential of at least 0.6 Mt/year is predicted for the operating German coal mines for this technology. The calculation is based on experimental data and mining specific information, obtained from German mining research institutions. This technology is applicable to other mining regions world-wide involving increased storage potentials resulting from differences in mining and coal processing techniques.
As a third overriding research topic, the sealing efficiency of several low permeability rocks (mainly shales) is studied in different laboratory experiments, comprising CO2 diffusion and CO2 sorption experiments. In a case study conducted on the Australian Muderong Shale, the sealing efficiency was determined. Results indicate a considerably high CO2 sorption and retention potential as well as a measurable alteration of clay minerals, predominantly micas. This study is, to our knowledge, the first comprehensive investigation of the CO2 sorption capacity of natural shales and individual clay minerals under conditions relevant for CO2 subsurface storage.
Busch, A., Kempka, T., Waschbüsch, M., Fernández-Steeger, T., Schlüter, R., and Krooss, B.M., 2007 (accepted), CO2 storage in abandoned coal mines, in Carbon Dioxide Sequestration in Geological Media - State of the Art: AAPG Special Publication (in preparation). Clauser, C., 2003, Numerical Simulation of Reactive Flow in hot Aquifers using SHEMAT/Processing Shemat: Springer Verlag, Heidelberg-Berlin. Kempka, T., Waschbüsch, M., Fernandez-Steeger, T.M., and Azzam, R., 2008 (submitted), Reducing ground subsidence involving geological CO2 storage during longwall mining operations: Quarterly Journal of Engineering Geology and Hydrogeology. Langosch, U., Huwe, H.W., te Kook, J., Polysos, N., Ruppel, U., Stadie, U., and Zischinsky, U., 2006, Gebirgs- und Streckenverformung, in Junker, M., et al., Gebirgsbeherrschung von Flözstrecken: Glückauf, Essen, Germany, 172 (in German). Parkhurst, D.L., and Appelo, C.A.J., 1999, User’s guide to PHREEQC (version 2) - A computer program for speciation, batch-reaction, one-dimensional transport, and inverse geochemical calculations: U.S. Geological Survey Water-Resources Investigations Report 99-4259, 312 p.
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