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Technology Collaboration Programme by IEA

Effects of Impurities on Geological Storage of CO₂

Jinsheng Wang, David Ryan , Edward J. Anthony, Andrew Wigston

Citation: IEAGHG, "Effects of Impurities on Geological Storage of CO₂", 2011-04, June 2011.

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Publication Overview

Study on evaluation of the effects of impurities on CO2 transport, injection and storage, sponsored by the International Energy Agency Greenhouse Gas R&D Programme (IEA GHG). The IEA GHG’s objectives of this study are:

  • To provide a review of existing information and published research on the potential impact of CO2 stream purity on storage reservoir and caprock performance and associated engineering costs;
  • To provide a high level overview of available knowledge. The focus is on storage of impure CO2 in deep saline formations, since this scenario has the largest theoretical storage capacity and the most significant potential for complex geochemical reactions, although depleted gas fields and CO2-EOR are also relevant.

Particular aspects to be considered include:

  • The potential effects of impurities on phase behaviour and storage capacity calculations;
  •  Effects on the rates of geochemical reactions with both formation and caprocks, and the impacts on injectivity, reservoir permeability and caprock integrity.
  •  Effects on buoyancy forces and trapping mechanisms;
  • Potential for corrosion of well components and estimated impact on system reliability if not mitigated.

Publication Summary

  1. The measure of storage capacity for impure CO2 and the impact of the impurities have been established. With a simple formula proposed in this work, normalized CO2 storage capacity can be calculated for any CO2 mixtures, and the impact of the impurities can be clearly seen.
  2. Non-condensable impurities which cannot be liquefied at ambient temperature, such as N2, O2 and Ar, result in significant decrease in CO2 storage capacity. The degree of decrease in the capacity is a function of pressure, temperature, and composition.
  3. For all mixtures of supercritical CO2 and non-condensable gases, there is a maximum decrease of the storage capacity at given temperature. This pressure corresponding to the maximum decrease changes with temperature.
  4. In contrast to non-condensable gases, impurities which are more easily condensable than CO2, such as SO2, could increase the storage capacity, and there is a maximum increase at a certain
  5. For a supercritical CO2 stream with high levels of N2, O2 and Ar, which are common impurities from oxyfuel combustion, the volume and density may be determined by the use of Ar to represent all impurities, computationally and/or experimentally.
  6. The change of density caused by non-condensable gas impurities results in lower injectivity of impure CO2 into geological formations. Above a threshold pressure range the injectivity could reach the level of pure CO2 due to lowered viscosity. However, more condensable impurities like SO2 may have an effect of increasing the injectivity, through increasing density of the CO2
  7. Non-condensable gas impurities increase the buoyancy of the CO2 This would decrease the sweep efficiency of injected CO2. As a result, the efficiency of solubility trapping and residual trapping of CO2 would decrease.
  8. A formula has been developed to enable quick determination of the effect of SOx on CO2 injectivity through precipitation of sulphates, which reduces rock porosity, an issue of substantial concern. With this formula, the degree of the porosity reduction could be directly predicted from the SOx content of the injected CO2.
  9. Among reactive impurity species, SOx, H2S and NOx would have the greatest chemical effects on the rocks. Based on our analysis, the effect of SOx on reduction of rock porosity and injectivity would be much smaller than commonly thought. However, if H2S and SOx are co-injected, such as in the case where CO2 streams from pre-combustion capture and oxyfuel combustion are merged, deposition of elemental sulphur in the pore space could be a concern for pore plugging and hence injectivity reduction.  
  10. The potential of corrosion of injection well materials has been assessed. The corrosion would be lower if the CO2 stream is dry, due to desiccation of the well zone during the injection period. However, after termination of injection the acidic impurities would promote the corrosion of cements in the presence of water. CO2 containing SOx, NOx and O2 impurities would be more corrosive to cements and steels than pure CO2 or CO2/H2S mixtures.

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