Abstract:The objective of this study was to determine the influence of the possible CO 2 geological storage in the Baltic Region on the composition and properties of host rocks to support more reliable petrophysical and geophysical models of CO 2 plume. The geochemical, mineralogical, and petrophysical evolution of reservoir sandstones of Cambrian Series 3 Deimena Formation and transitional clayey carbonate caprocks of Lower Ordovician Zebre Formation from two offshore structures in Latvia and Lithuania and two onshore… Show more
“…From a geochemical perspective, CO 2 and impurities can influence the storage system in basically three ways: formation of carbonic acid or bicarbonates by dissolution of CO 2 in formation water (Equations (9) and (10) ); production of weak or strong acids due to the effects of impurities; and dissolution and/or precipitation of calcite as cementing material [ 13 , 58 , 59 ]. CO 2 + H 2 O ↔ H 2 CO 3 CO 2 + H 2 O ↔ H + + HCO 3 - …”
Carbon capture and storage (CCS) is expected to play a key role in meeting greenhouse gas emissions reduction targets. In the UK Southern North Sea, the Bunter Sandstone formation (BSF) has been identified as a potential reservoir which can store very large amounts of CO
2
. The formation has fairly good porosity and permeability and is sealed with both effective caprock and base rock, making CO
2
storage feasible at industrial scale. However, when CO
2
is captured, it typically contains impurities, which may shift the boundaries of the CO
2
phase diagram, implying that higher costs will be needed for storage operations. In this study, we modelled the effect of CO
2
and impurities (NO
2
, SO
2
, H
2
S) on the reservoir performance of the BSF. The injection of CO
2
at constant rate and pressure using a single horizontal well injection strategy was simulated for up to 30 years, as well as an additional 30 years of monitoring. The results suggest that impurities in the CO
2
stream affect injectivity differently, but the effects are usually encountered during early stages of injection into the BSF and may not necessarily affect cumulative injection over an extended period. It was also found that porosity of the storage site is the most important factor controlling the limits on injection. The simulations also suggest that CO
2
remains secured within the reservoir for 30 years after injection is completed, indicating that no post-injection leakage is anticipated.
“…From a geochemical perspective, CO 2 and impurities can influence the storage system in basically three ways: formation of carbonic acid or bicarbonates by dissolution of CO 2 in formation water (Equations (9) and (10) ); production of weak or strong acids due to the effects of impurities; and dissolution and/or precipitation of calcite as cementing material [ 13 , 58 , 59 ]. CO 2 + H 2 O ↔ H 2 CO 3 CO 2 + H 2 O ↔ H + + HCO 3 - …”
Carbon capture and storage (CCS) is expected to play a key role in meeting greenhouse gas emissions reduction targets. In the UK Southern North Sea, the Bunter Sandstone formation (BSF) has been identified as a potential reservoir which can store very large amounts of CO
2
. The formation has fairly good porosity and permeability and is sealed with both effective caprock and base rock, making CO
2
storage feasible at industrial scale. However, when CO
2
is captured, it typically contains impurities, which may shift the boundaries of the CO
2
phase diagram, implying that higher costs will be needed for storage operations. In this study, we modelled the effect of CO
2
and impurities (NO
2
, SO
2
, H
2
S) on the reservoir performance of the BSF. The injection of CO
2
at constant rate and pressure using a single horizontal well injection strategy was simulated for up to 30 years, as well as an additional 30 years of monitoring. The results suggest that impurities in the CO
2
stream affect injectivity differently, but the effects are usually encountered during early stages of injection into the BSF and may not necessarily affect cumulative injection over an extended period. It was also found that porosity of the storage site is the most important factor controlling the limits on injection. The simulations also suggest that CO
2
remains secured within the reservoir for 30 years after injection is completed, indicating that no post-injection leakage is anticipated.
“…Previous studies (Aminu et al, 2017;Gilfillan et al, 2009;Liu et al, 2012Liu et al, , 2011Shogenov et al, 2015) report that the acidification of formation waters, due to the dissolution of CO2, leads to brine-rock interaction and triggers dissolution or precipitation of rock minerals and cementation of the rocks which hold the rock grains together. Consequently, it can alter the reservoir rock grain-size characteristics and result in changing the permeability.…”
Section: Resultsmentioning
confidence: 99%
“…Depending on the impurities and pH of the formation water, quartz can react with carbonic acid, hydrogen ion or bicarbonates, which had already formed from the dissolution of CO2 in water, Equation 4 to Equation 8 (Rathnaweera et al, 2016;Shogenov et al, 2015).…”
The Bunter Sandstone formation in the UK Southern North Sea has been identified as having the potential to store large volumes of CO2. Prior to injection, CO2 is captured with certain amounts of impurities, usually less than 5%vol. The dissolution of these impurities in formation water can cause chemical reactions between CO2, brine, and rock, which can affect the reservoir quality by altering properties such as permeability. In this study, we explored the effect of CO2 and impurities (NO2, SO2, H2S) on reservoir permeability by measuring changes in grain size distributions after a prolonged period of 9 months, simulating in situ experimental conditions. It was found that the effects of pure CO2 and CO2-H2S are relatively small, i.e., CO2 increased permeability by 5.5% and CO2-H2S decreased it by 5.5%. Also, CO2-SO2 slightly decreased permeability by 6.25%, while CO2-NO2 showed the most pronounced effect, reducing permeability by 41.6%. The decrease in permeability showed a correlation with decreasing pH of the formation water and this equally correlates with a decrease in geometric mean of the grain diameter. The findings from this study are aimed to be used in future modelling studies on reservoir performance during injection and storage, which also should account for the shifts in boundaries in the CO2 phase diagram, altering the reservoir properties and affecting the cost of storage.
“…The sandstone consists of approximately 82% quartz, about 9% feldspar, 6% mica, and 3% various heavy metals, such as zircon, tourmaline, and rutile [44]. The reaction of Ca-and Mg-bearing aluminosilicates in the composition of the sandstone with the injected CO 2 has a potential to form calcite, dolomite, and MgCO 3 [77,78]. However, the interaction among aluminosilicates, carbonic acid, and newly formed carbonate minerals can reduce the overall salinity of the water and thus increase CO 2 solubility [77,79].…”
Section: Geological Feasibility Of the Dobele Structure For Fossil Co 2 Geological Storagementioning
confidence: 99%
“…The reaction of Ca-and Mg-bearing aluminosilicates in the composition of the sandstone with the injected CO2 has a potential to form calcite, dolomite, and MgCO3 [77,78]. However, the interaction among aluminosilicates, carbonic acid, and newly formed carbonate minerals can reduce the overall salinity of the water and thus increase CO2 solubility [77,79]. Wet density of the sandstone within the Dobele structure increases with depth, the average being approximately 2300 kg/m 3 .…”
Section: Geological Feasibility Of the Dobele Structure For Fossil Co 2 Geological Storagementioning
The importance of CO2 removal from the atmosphere has long been an essential topic due to climate change. In this paper, the authors aim to demonstrate the suitability of the underground reservoirs for CO2 storage based on their geological characteristics. The research addressed the potential of geological formations for fossil CO2 storage in the Baltic States to support the goal of achieving carbon neutrality in the region. The geological, technical, and economic feasibility for CO2 storage has been assessed in terms of carbon sequestration in geological structures and the legal framework for safe geological storage of fossil CO2. Results indicate that prospective structural traps in the Baltic States, with reasonable capacity for CO2 storage, occur only in Southwestern Latvia (onshore) and in the Baltic Sea (offshore), whilst other regions in the Baltics either do not meet basic geological requirements, or have no economically feasible capacity for CO2 storage. Based on the examination of geological characteristics, the most fitting is the middle Cambrian reservoir in the Baltic sedimentary basin, and one of the most prospective structural traps is the geological structure of Dobele, with an estimated storage capacity of 150 Mt CO2. This study revealed that the storage capacity of the middle Cambrian reservoir (up to 1000 Mt CO2) within the borders of Southwestern Latvia is sufficient for carbon capture and safe storage for the whole Baltic region, and that geological structures in Latvia have the capacity to store all fossil CO2 emissions produced by stationary sources in the Baltic States for several decades.
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