Greenhouse Gas Control Technologies 7

Greenhouse Gas Control Technologies 7

Proceedings of the 7th International Conference on Greenhouse Gas Control Technologies 5– September 2004, Vancouver, Canada
Volume I, 2005, Pages 479-487
Greenhouse Gas Control Technologies 7

- Evaluation of the spread of acid-gas plumes injected in deep saline aquifers in western Canada as an analogue for CO2 injection into continental sedimentary basins

https://doi.org/10.1016/B978-008044704-9/50049-5Get rights and content

Publisher Summary

Injection of CO2 into deep saline aquifers in sedimentary basins appears to be an important means for reducing anthropogenic emissions of CO2 into the atmosphere. In the design, approval and monitoring of such operations it is important to predict the evolution of the plume of injected CO2 and identify potential leakage pathways. In mature sedimentary basins such as those in North America that underwent intense exploration for and production of hydrocarbons, the number and density of wells is extremely high, and a plume of injected CO2 is likely to encounter many wells that have to be identified and monitored. Under these circumstances, running full-blown numerical models becomes impractical and resource intensive, and simpler and faster tools are needed. An analytical model has been developed that, under a set of simplifying assumptions, can provide a rapid estimate of the shape and extent of a plume of CO2 injected into an aquifer. The method assumes constant gas properties, which is a valid assumption for a wide range of conditions found in sedimentary basins, and homogeneous and uniform aquifer properties, which, depending on scale, can be assumed for many aquifers at least in a statistical sense. The aquifer is assumed to be horizontal, and there is no mixing, diffusion or dissolution between the injected gas and formation water.

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Cited by (46)

  • Effects of impurities H<inf>2</inf>S and N<inf>2</inf> on CO<inf>2</inf> migration and dissolution in sedimentary geothermal reservoirs

    2021, Journal of Hydrology
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    But to our best knowledge, there has no published study investigating the impurity effects on CO2 storage and utilization in CPG systems. Apart from some impurities, e.g., N2 and Ar, allowed for reducing the costs, some hazardous gases, like H2S and SO2, even have been co-injected with CO2 deliberately, because their emission into atmosphere would cause the formation of acid rain and damage to human health (Bachu and Gunter, 2005; Bachu et al., 2005). The light-impurity species, such as N2, by decreasing the density and viscosity of injected CO2 streams, would increase the buoyancy force of free-phase CO2 and accelerate its migration (Wang et al., 2011; IEAGHG, 2011; Yu et al., 2021).

  • Design-of-experiment-based proxy models for the estimation of the amount of dissolved CO<inf>2</inf> in brine: A tool for screening of candidate aquifers in geo-sequestration

    2017, International Journal of Greenhouse Gas Control
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    For example, Hassanzadeh et al. (2005, 2007) used this geometry with a square lengths of 5 m and 6 m respectively. After examining the proposed data by Bachu et al. (2005) regarding deep saline aquifers in Western Canada, we decided to use 10 m in this study, because it is the most frequent thickness of reservoir between these aquifers (7 of 24). One possible option for using these similar studies in the large scale application is consideration of a sink term in the proper location to account for the removal of CO2 due to dissolution (Green and Ennis-King, 2014; Pruess and Nordbotten, 2011).

  • Experimental study of density-driven convection effects on CO<inf>2</inf> dissolution rate in formation water for geological storage

    2014, Journal of Natural Gas Science and Engineering
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    If we have the physical parameters expressed in Eq. (12), we can find an estimation of the convective mass flux of CO2, dissolved in each sequestration site, which would be helpful in examining the strength of candidate aquifer for CO2 geological storage. For examining the applicability of the presented scaling relationship, sample calculations for site number 11 in Alberta basin aquifers (Hassanzadeh et al., 2007; Bachu et al., 2005; Bachu and Carroll, 2005) with porosity equal to 0.09, permeability of 137 mD (assume isotropic), H∼60 m, Δρ = 4.1 kg/m3, μ = 0.36 × 10−3 Pa s, D = 7.6 × 10−9 m2/s, and ΔC = 660 mol/m3 were performed. Therefore, the Rayleigh number is ∼1359.

  • Effect of exposure environment on the interactions between acid gas (H<inf>2</inf>S and CO<inf>2</inf>) and pozzolan-amended wellbore cement under acid gas co-sequestration conditions

    2014, International Journal of Greenhouse Gas Control
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    In addition to pure CO2 injection, acid-gas (a mixture of CO2 and H2S) injection is also on the rise (Bachu and Gunter, 2004; Machel, 2005), so as to reduce atmospheric emissions of toxic H2S and reduce the cost to conduct surface desulfurization (Bachu et al., 2003). Acid gas injection is mainly employed to store H2S and CO2 separated from sour natural gas (Bachu and Carroll, 2005; Bachu et al., 2005). It could also be used to sequester H2S and CO2 from pre-combustion capture of carbon from coal-fired power plants (Kutchko et al., 2011).

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