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Frontiers of Earth Science

ISSN 2095-0195

ISSN 2095-0209(Online)

CN 11-5982/P

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2018 Impact Factor: 1.205

Front. Earth Sci.    2022, Vol. 16 Issue (2) : 465-482    https://doi.org/10.1007/s11707-021-0901-1
RESEARCH ARTICLE
Study of corrosion mechanism of dawsonite led by CO2 partial pressure
Fulai LI1,2(), Hao DIAO1,2, Wenkuan MA1,2, Maozhen WANG3
1. Shandong Provincial Key Laboratory of Deep Oil and Gas, School of Geosciences, China University of Petroleum (East China), Qingdao 266580, China
2. Laboratory for Marine Mineral Resources, Qingdao National Laboratory for Marine Science and Technology, Qingdao 266071, China
3. Bohai Oilfield Research Institute, Tianjin Branch of CNOOC China Limited, Tianjin 300452, China
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Abstract

The stability of dawsonite is an important factor affecting the feasibility evaluation of CO2 geological storage. In this paper, a series of experiments on the interaction of CO2-water-dawsonite-bearing sandstone were carried out under different CO2 pressures. Considering the dissolution morphology and element composition of dawsonite after the experiment and the fluid evolution in equilibrium with dawsonite, the corrosion mechanism of dawsonite led by CO2 partial pressure was discussed. The CO2 fugacity of the vapor phase in the system was calculated using the Peng–Robinson equation of state combined with the van der Waals 1-fluid mixing rule. The experimental results indicated that the thermodynamic stability of dawsonite increased with the increase of CO2 partial pressure and decreased with the increase of temperature. The temperature at which dawsonite dissolution occurred was higher at higher fCO2. There were two different ways to reduce dawsonite’s stability: the transformation of constituent elements and crystal structure damage. Dawsonite undergoes component element transformation and crystal structure damage under different CO2 pressures with certain temperature limits. Based on the comparison of the corrosion temperature of dawsonite, three corrosion evolution models of dawsonite under low, medium, and high CO2 pressures were summarized. Under conditions of medium and low CO2 pressure, as the temperature continued to increase and exceeded its stability limit, the dawsonite crystal structure was corroded first. Then the constituent elements of dawsonite dissolved, and the transformation of dawsonite to gibbsite began. At high CO2 pressure, the constituent elements of dawsonite dissolved first with the increase of temperature, forming gibbsite, followed by the corrosion of crystalline structure.

Keywords dawsonite stability      CO2-water-rock interaction      corrosion mechanism      CO2 geological storage     
Corresponding Author(s): Fulai LI   
About author: Tongcan Cui and Yizhe Hou contributed equally to this work.
Online First Date: 19 October 2021    Issue Date: 26 August 2022
 Cite this article:   
Fulai LI,Hao DIAO,Wenkuan MA, et al. Study of corrosion mechanism of dawsonite led by CO2 partial pressure[J]. Front. Earth Sci., 2022, 16(2): 465-482.
 URL:  
https://academic.hep.com.cn/fesci/EN/10.1007/s11707-021-0901-1
https://academic.hep.com.cn/fesci/EN/Y2022/V16/I2/465
Fig.1  Laboratory apparatus used for water-rock-CO2 reactions.
Exp.# T/°C P/MPa Initial pH Time/h System Initial solution Mass before/g Mass after/g Mass loss Δm/g Mass loss rate Rm/%
1 80 0 7 72 Closed 350 mL pure water 1.49 1.47 0.02 1.34
2 100 0 7 72 Closed 350 mL pure water 1.43 1.39 0.04 2.8
3 80 4 7 72 Closed 350 mL pure water 0.62 0.566 0.054 8.71
4 100 4 7 72 Closed 350 mL pure water 0.701 0.622 0.079 11.27
5 120 4 7 72 Closed 350 mL pure water 0.814 0.727 0.087 10.69
6 120 7.3 7 72 Closed 350 mL pure water 0.735 0.675 0.06 8.16
7 140 7.3 7 72 Closed 350 mL pure water 0.902 0.816 0.086 9.53
8 160 7.3 7 72 Closed 350 mL pure water 0.772 0.677 0.095 12.31
Tab.1  Initial reaction conditions and weight loss of samples
Fig.2  Mass loss ratio of sandstone samples. (a) Mass loss ratio of sandstone samples at normal pressure; (b) mass loss ratio of sandstone samples at 4 MPa; (c) mass loss ratio of sandstone samples at 7.3 MPa.
Fig.3  Mineral composition of sandstone samples. (a) Mineral contents of the original sandstone sample; (b) the content of each mineral in the sandstone sample at normal pressure 80°C; (c) the content of each mineral in the sandstone sample at normal pressure 100°C; (d) the content of each mineral in the sandstone sample at 4 MPa 80°C; (e) the content of each mineral in the sandstone sample at 4 MPa 100°C; (f) the content of each mineral in the sandstone sample at 4 MPa 120°C; (g) the content of each mineral in the sandstone sample at 7.3 MPa 120°C; (h) the content of each mineral in the sandstone sample at 7.3 MPa 140°C; (i) the content of each mineral in the sandstone sample at 7.3 MPa 160°C.
Exp.# T/°C Initial pH P/MPa Concentration of soluble species/(mg·L–1)
F Cl N SO Na K Mg Ca H.C. Si Fe Al
1 80 7 0 0.08 1.79 0.345 1.42 24.8 0.441 0.608 1.75 73.6 0.175 0.002 0.1
2 100 7 0 0.02 444 0.319 1.02 16.6 0.653 0.662 260 26.5 0.099 0.313 0.018
3 80 7 4 0.12 1.58 1.773 2.07 14.6 0.695 17.4 50.9 263 2.07 0.112 0.02
4 100 7 4 0.08 1.72 0.675 2.14 60.7 1.1 12.4 40.1 328 1.42 0.102 0.017
5 120 7 4 0.08 1.46 0.688 2.61 102 2.64 9.76 47.4 447 5.55 0.112 0.019
6 120 7 7.3 0.462 1.08 0.135 21.8 80.8 1.02 7.76 46.6 351 1.68 0.002 0.006
7 140 7 7.3 0.078 1.99 0.204 20.2 101 2.7 10.9 51.9 443 5.52 0.002 0.018
8 160 7 7.3 0.02 0.706 0.097 20.3 117 3.94 7.59 49.8 465 11.8 0.002 0.029
Tab.2  Concentration of soluble species in solutions after reactions
Fig.4  Ion dissolution rate of each anion and cation in the solution after the reaction. (a) The change of anionic ion dissolution rate with temperature in the reaction solution at normal pressure; (b) the change of cationic ion dissolution rate with temperature in the reaction solution at normal pressure; (c) the change of anionic ion dissolution rate with temperature in the reaction solution at 4 MPa; (d) the change of cationic ion dissolution rate with temperature in the reaction solution at 4 MPa; (e) the change of anionic ion dissolution rate with temperature in the reaction solution at 7.3 MPa; (f) the change of cationic ion dissolution rate with temperature in the reaction solution at 7.3 MPa.
Fig.5  SEM photos of erosion and dissolution of major minerals in sandstone. (a) Calcite eroded along cleavages, and the surface was eroded to form a large number of pits and channels (normal pressure, T= 80°C); (b) kaolinite is vermiform and only slightly eroded (normal pressure, T= 80°C); (c) slight dissolution of potassium feldspar resulted in tiny pores on the mineral surface and tiny channels along cleavages (normal pressure, T = 100°C); (d) the further dissolution of potassium feldspar, corrosion pits increased, the hole deepened (P = 4 MPa, T= 80°C); (e) albite is obviously eroded, with wide and long channels and large holes on the surface (P = 4 MPa, T = 100°C); (f) the surface of quartz grains is smooth (P = 4 MPa, T = 120°C); (g) illite is reticular and slightly corroded (P = 7.3 MPa, T = 120°C); (h) albite is severely eroded, and the mineral has completely dissolved locally, leaving only some of the residue along the cleavage (P = 7.3 MPa, T= 140°C); (i) dissolution of potassium feldspar, the mineral surface was dissolved along the cleavages and formed a staggered channel (P = 7.3 MPa, T= 160°C). Cal-calcite, kln-kaolinite, kfs-potassium feldspar, Ab-albite, Qtz-quartz, Ill-illite.
Fig.6  SEM photos of dawsonite under different experimental conditions. (a) SEM photo of dawsonite in original sandstone; (b) dawsonite eroded significantly, and the surface of the columnar crystal became extremely rough, forming a large number of craters (normal pressure, T= 80°C); (c) dawsonite was further corroded into a thorn shape and the degree of dissolution of dawsonite aggregate was enhanced from the root to the outer edge (normal pressure, T= 100°C); (d) dawsonite preserved well and the mineral surface is relatively regular (P = 4 MPa, T = 80°C); (e) dawsonite with no obvious corrosion (P = 4 MPa, T= 100°C); (f) the surface of dawsonite was dissolved, the edges of the crystal were no longer clear, and the surface was covered by newly precipitated minerals (P = 4 MPa, T= 120°C); (g) the shape of dawsonite aggregate remained intact, but the crystal edges were no longer distinct and the surface was attached by fine new minerals (P = 7.3 MPa, T = 120°C); (h) radial dawsonite aggregate, the edges of individual crystals were more blurred, and the columnar shape was further lost (P = 7.3 MPa, T= 140°C); (i) dawsonite crystals were almost completely turned grayish white, and the aggregates dissolved from the outer edge of the columnar crystal to the root (P = 7.3 MPa, T = 160°C).
Fig.7  The composition and content evolution of dawsonite. (a) SEM photo of dawsonite in original sample, and the energy spectrum at the marked point; (b) SEM photo of dawsonite in sandstone at normal pressure 80°C, and the energy spectrum at the marked point; (c) SEM photo of dawsonite in sandstone at normal pressure 100°C, and the energy spectrum at the marked point; (d) the content of dawsonite under the experiment of normal pressure; (e) SEM photo of dawsonite in sandstone at 4 MPa 80°C, and the energy spectrum at the marked point; (f) SEM photo of dawsonite in sandstone at 4 MPa 100°C, and the energy spectrum at the marked point; (g) SEM photo of dawsonite in sandstone at 4 MPa 120°C, and the energy spectrum at the marked point; (h) the content of dawsonite under the experimental pressure of 4 MPa; (i) SEM photo of dawsonite in sandstone at 7.3 MPa 120°C, and the energy spectrum at the marked point; (j) SEM photo of dawsonite in sandstone at 7.3 MPa 140°C, and the energy spectrum at the marked point; (k) SEM photo of dawsonite in sandstone at 7.3 MPa 160°C, and the energy spectrum at the marked point; (h) the content of dawsonite under the experimental pressure of 7.3 MPa.
P/MPa T/K x Pc/MPa Tc/K ω k12 fCO2/MPa
CO2 H2O CO2 H2O CO2 H2O CO2 H2O
4 353.15 0.984 0.016 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 3.9
4 373.15 0.968 0.032 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 3.8
4 393.15 0.939 0.061 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 3.7
7.3 393.15 0.959 0.041 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 6.9
7.3 413.15 0.931 0.069 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 6.7
7.3 433.15 0.887 0.113 7.383 22.048 304.21 647.30 0.2236 0.3442 0.165 6.4
Tab.3  The parameters used for the calculation and the corrected CO2 fugacity values
Fig.8  Elemental composition evolution of dawsonite after the reaction.
Fig.9  Dissolution patterns of dawsonite under different CO2 partial pressures and temperature conditions.
1 T Ajayi, J S Gomes, A Bera (2019). A review of CO2 storage in geological formations emphasizing modeling, monitoring and capacity estimation approaches. Petrol Sci, 16(5): 1028–1063
https://doi.org/10.1007/s12182-019-0340-8
2 E Álvarez-Ayuso, H W Nugteren (2005). Synthesis of dawsonite: a method to treat the etching waste streams of the aluminium anodising industry. Water Res, 39(10): 2096–2104
https://doi.org/10.1016/j.watres.2005.03.017 pmid: 15922401
3 M D Aminu, S A Nabavi, C A Rochelle, V Manovic (2017). A review of developments in carbon dioxide storage. Appl Energy, 208: 1389–1419
4 R S Arvidson, I E Ertan, J E Amonette, A Luttge (2003). Variation in calcite dissolution rates: a fundamental problem? Geochim Cosmochim Acta, 67(9): 1623–1634
https://doi.org/10.1016/S0016-7037(02)01177-8
5 S Bachu (2002). Sequestration of CO2 in geological media in response to climate change: road map for site selection using the transform of the geological space into the CO2 phase space. Energy Convers Manage, 43(1): 87–102
https://doi.org/10.1016/S0196-8904(01)00009-7
6 P Bakhshi, R Kharrat, A Hashemi, M Zallaghi (2018). Experimental evaluation of carbonated waterflooding: a practical process for enhanced oil recovery and geological CO2 storage. Greenh Gases Sci Techn, 8(2): 238–256
https://doi.org/10.1002/ghg.1734
7 J C Baker, G P Bai, P J Hamilton, S D Golding, J B Keene (1995). Continental-scale magmatic carbon dioxide seepage recorded by dawsonite in the Bowen-Gunnedah-Sydney Basin system, eastern Australia. J Sediment Res, 65A: 522–530
https://doi.org/10.1306/D4268117-2B26-11D7-8648000102C1865D
8 S M Benson, D R Cole (2008). CO2 sequestration in deep sedimentary formations. Elements, 4(5): 325–331
https://doi.org/10.2113/gselements.4.5.325
9 A K Burnham, A Levchenko, M M Herron (2015). Analysis, occurrence, and reactions of dawsonite in AMSO well CH-1. Fuel, 144: 259–263
https://doi.org/10.1016/j.fuel.2014.12.018
10 W Chesworth (1971). Laboratory synthesis of dawsonite and its natural occurrences. Nat Phys Sci (Lond), 231(19): 40–41
https://doi.org/10.1038/physci231040a0
11 C Coquelet, A Chapoy, D Richon (2004). Development of a new alpha function for the Peng–Robinson Equation of state: comparative study of alpha function models for pure gases (natural gas components) and water-gas systems. Int J Thermophys, 25(1): 133–158
https://doi.org/10.1023/B:IJOT.0000022331.46865.2f
12 A Dejean, R Céréghino, J M Carpenter, B Corbara, B Hérault, V Rossi, M Leponce, J Orivel, D Bonal (2011). Climate change impact on neotropical social wasps. PLoS One, 6(11): e27004
https://doi.org/10.1371/journal.pone.0027004 pmid: 22073236
13 D J DePaolo, D R Cole (2013). Geochemistry of geologic carbon sequestration: an overview. Rev Mineral Geochem, 77(1): 1–14
https://doi.org/10.2138/rmg.2013.77.1
14 W R Dickinson (1970). Interpreting detrital modes of graywacke and arkose. J Sediment Res, 40: 695–707
https://doi.org/10.1306/74D72018-2B21-11D7-8648000102C1865D
15 L Dong, L Liu, X Qu, H Yang, F Li, N Liu, X Guo (2009). Crystal characteristics and genesis of dawsonite of the Qingshankou formation in the Honggang Oilfield in the Honggang Terrace of Songliao Basin. J Jilin U, 39: 1031–1104 (in Chinese)
https://doi.org/10.13278/j.cnki.jjuese.2009.06.018
16 S Elidemir, N Güleç (2018). Geochemical characterization of geothermal systems in western Anatolia (Turkey): implications for CO2 trapping mechanisms in prospective CO2-EGS sites. Greenh Gases Sci Techn, 8(1): 63–76
https://doi.org/10.1002/ghg.1747
17 L Fernández-Carrasco, F Puertas, M Blanco-Varela, T Vázquez, J Rius (2005). Synthesis and crystal structure solution of potassium dawsonite: an intermediate compound in the alkaline hydrolysis of calcium aluminate cements. Cement Concrete Res, 35(4): 641–646.
https://doi.org/10.1016/S0008-8846(04)00172-3
18 R L Frost, A López, R Scholz, N P Sampaio, F A de Oliveira (2015). SEM, EDS and vibrational spectroscopic study of dawsonite NaAl(CO3)(OH)2. Spectrochim Acta A Mol Biomol Spectrosc, 136(Pt B): 918–923
https://doi.org/10.1016/j.saa.2014.09.114 pmid: 25459617
19 Y, Gao L Liu (2006). Carbon-oxygen isotopic characteristics of authigenic dawsonite and its genetic significance. Geol J China U, 12(4): 522–529 (in Chinese)
20 Y Gao, L Liu, W Hu (2009). Petrology and isotopic geochemistry of dawsonite-bearing sandstones in Hailar Basin, Northeastern China. Appl Geochem, 24(9): 1724–1738
https://doi.org/10.1016/j.apgeochem.2009.05.002
21 Y Gao, L Liu, X Qu, N Liu (2008). Petrologic characteristics of dawsonite—bearing sandstones in Wuerxun Sag of Hailar Basin and Gudian CO2 gasfield in Songliao Basin. J Palaeogeograph, 10: 111–123 (in Chinese)
https://doi.org/10.7605/gdlxb.2008.02.001
22 I Gaus (2010). Role and impact of CO2–rock interactions during CO2 storage in sedimentary rocks. Int J Greenh Gas Control, 4(1): 73–89
https://doi.org/10.1016/j.ijggc.2009.09.015
23 I Gaus, P Audigane, L André, J Lions, N Jacquemet, P Durst, I Czernichowski-Lauriol, M Azaroual (2008). Geochemical and solute transport modelling for CO2 storage, what to expect from it? Int J Greenh Gas Control, 2(4): 605–625
https://doi.org/10.1016/j.ijggc.2008.02.011
24 M Gunnemyr (2019). Causing global warming. Ethical Theory Moral Pract, 22(2): 399–424
https://doi.org/10.1007/s10677-019-09990-w
25 A P Gysi, A Stefánsson (2008). Numerical modelling of CO2-water-basalt interaction. Mineral Mag, 72(1): 55–59
https://doi.org/10.1180/minmag.2008.072.1.55
26 H Hellevang, J Declercq, B Kvamme, P Aagaard (2010). The dissolution rates of dawsonite at pH 0.9 to 5 and temperatures of 22, 60 and 77 °C. Appl Geochem, 25(10): 1575–1586
https://doi.org/10.1016/j.apgeochem.2010.08.007
27 S Holloway (2005). Underground sequestration of carbon dioxide—a viable greenhouse gas mitigation option. Energy, 30(11–12): 2318–2333
https://doi.org/10.1016/j.energy.2003.10.023
28 S Holloway, D Savage (1993). The potential for aquifer disposal of carbon dioxide in the UK. Energy Convers Manage, 34(9–11): 925–932
https://doi.org/10.1016/0196-8904(93)90038-C
29 C W Huggins, T E Green (1973). Thermal decomposition of dawsonite. Am Mineral, 58: 548–550
30 IPCC (2014).Climate Change 2013—The Physical Science Basis: Working Group I Contribution to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge: Cambridge University Press
31 H Jiang, P Shen, X Li, W Huang, J Cai, B, Ju J Guo (2008). Study into technologies for estimating theoretical volume of CO2 stored underground worldwide. Sino-Global Energ, 13(2): 93–99 (in Chinese)
32 J W Johnson (2009). Integrated modeling, monitoring, and site characterization to assess the isolation performance of geologic CO2 storage: Requirements, challenges, and methodology. Energ Procedia, 1(1): 1855–1861
https://doi.org/10.1016/j.egypro.2009.01.242
33 J W Johnson, J J Nitao, K G Knauss (2004). Reactive transport modelling of CO2 storage in saline aquifers to elucidate fundamental processes, trapping mechanisms and sequestration partitioning. Geol Soc Lond Spec Publ, 233(1): 107–128
https://doi.org/10.1144/GSL.SP.2004.233.01.08
34 N Kampman, M Bickle, J Becker, N Assayag, H Chapman (2009). Feldspar dissolution kinetics and Gibbs free energy dependence in a CO2-enriched groundwater system, Green River, Utah. Earth Planet Sci Lett, 284(3-4): 473–488
https://doi.org/10.1016/j.epsl.2009.05.013
35 T R Karl, J M Melillo, T C Peterson, S J ( Hassol 2009). Global Climate Change Impacts in the United States. Cambridge: Cambridge University Press
36 T R Karl, K E Trenberth (2003). Modern global climate change. Science, 302(5651): 1719–1723
https://doi.org/10.1126/science.1090228 pmid: 14657489
37 Y K Kharaka, D R Cole, J J Thordsen, E Kakouros, H S Nance (2006). Gas–water–rock interactions in sedimentary basins: CO2 sequestration in the Frio Formation, Texas, USA. J Geochem Explor, 89(1–3): 183–186
https://doi.org/10.1016/j.gexplo.2005.11.077
38 R Korbøl, A Kaddour (1995). Sleipner vest CO2 disposal-injection of removed CO2 into the utsira formation. Energy Convers Manage, 36(6-9): 509–512
https://doi.org/10.1016/0196-8904(95)00055-I
39 K Lechat, J M Lemieux, J Molson, G Beaudoin, R Hébert (2016). Field evidence of CO2 sequestration by mineral carbonation in ultramafic milling wastes, Thetford Mines, Canada. Int J Greenh Gas Control, 47: 110–121
https://doi.org/10.1016/j.ijggc.2016.01.036
40 F Li, Y Cao, W Li, L Zhang (2018). CO2 mineral trapping: Hydrothermal experimental assessments on the thermodynamic stability of dawsonite at 4.3 MPa pCO2 and elevated temperatures. Greenh Gases Sci Techn, 8(1): 77–92
https://doi.org/10.1002/ghg.1699
41 F Li, W Li (2017). Petrological record of CO2 influx in the Dongying Sag, Bohai Bay Basin, NE China. Appl Geochem, 84: 373–386
https://doi.org/10.1016/j.apgeochem.2017.07.015
42 F Li, W Li, Z Yu, N Liu, H Yang, L Liu (2017). Dawsonite occurrences related to the age and origin of CO2 influx in sandstone reservoirs: a case study in the Songliao Basin, NE China. Geochem Geophys Geosyst, 18(1): 346–368
https://doi.org/10.1002/2016GC006555
43 L Liu, Y Hong, J E Hocker, M A Shafer, L M Carter, J J Gourley, C N Bednarczyk, B Yong, P Adhikari (2012). Analyzing projected changes and trends of temperature and precipitation in the southern USA from 16 downscaled global climate models. Theor Appl Climatol, 109(3–4): 345–360
https://doi.org/10.1007/s00704-011-0567-9
44 J M Melillo (2014).Climate change impacts in the United States, highlights: US national climate assessment. Washington D.C.: Government Printing Office
45 J Moore, M Adams, R Allis, S Lutz, S Rauzi (2005). Mineralogical and geochemical consequences of the long-term presence of CO2 in natural reservoirs: an example from the Springerville–St. Johns Field, Arizona, and New Mexico, U.S.A. Chem Geol, 217(3–4): 365–385
https://doi.org/10.1016/j.chemgeo.2004.12.019
46 E H Oelkers, D R Cole (2008). Carbon dioxide sequestration a solution to a global problem. Elements, 4(5): 305–310
https://doi.org/10.2113/gselements.4.5.305
47 Y Okuyama (2014). Dawsonite-bearing carbonate veins in the Cretaceous Izumi Group, SW Japan: a possible natural analogue of fracture formation and self-sealing in CO2 geological storage. Energ Procedia, 63: 5530–5537
https://doi.org/10.1016/j.egypro.2014.11.586
48 Y Okuyama, Y Nakashima, M Sasaki, A Ueda (2011). Do the sedimentary strata have power to neutralize leaking CO2? A natural analogue study on past CO2 invasion and carbonate precipitation in the Cretaceous Izumi Group, SW Japan. Energ Procedia, 4: 4953–4960
https://doi.org/10.1016/j.egypro.2011.02.465
49 D Y Peng, D B Robinson (1976). A new two-constant equation of state. Ind Eng Chem Fundam, 15(1): 59–64
https://doi.org/10.1021/i160057a011
50 A Raza, R Gholami, R Rezaee, V Rasouli, A A Bhatti, C H Bing (2018). Suitability of depleted gas reservoirs for geological CO2 storage: a simulation study. Greenh Gases Sci Techn, 8(5): 876–897
https://doi.org/10.1002/ghg.1802
51 P Raybaud, M Digne, R Iftimie, W Wellens, P Euzen, H Toulhoat (2001). Morphology and surface properties of boehmite (γ-AlOOH): a density functional theory study. J Catal, 201(2): 236–246
https://doi.org/10.1006/jcat.2001.3246
52 M Shevalier, M Nightingale, G Johnson, B Mayer, E Perkins, I Hutcheon (2009). Monitoring the reservoir geochemistry of the Pembina Cardium CO2 monitoring project, Drayton Valley, Alberta. Energ Procedia, 1(1): 2095–2102
https://doi.org/10.1016/j.egypro.2009.01.273
53 G Stoica, J Pérez-Ramírez (2010). Stability and inter-conversion of synthetic dawsonites in aqueous media. Geochim Cosmochim Acta, 74(24): 7048–7058
https://doi.org/10.1016/j.gca.2010.09.013
54 A Valtz, A Chapoy, C Coquelet, P Paricaud, D Richon (2004). Vapour–liquid equilibria in the carbon dioxide–water system, measurement and modelling from 278.2 to 318.2 K. Fluid Phase Equilib, 226: 333–344
https://doi.org/10.1016/j.fluid.2004.10.013
55 K Wang, T Xu, H Tian, F Wang (2016). Impacts of mineralogical compositions on different trapping mechanisms during long-term CO2 storage in deep saline aquifers. Acta Geotech, 11(5): 1167–1188
https://doi.org/10.1007/s11440-015-0427-3
56 R H Worden (2006). Dawsonite cement in the Triassic Lam Formation, Shabwa Basin, Yemen: a natural analogue for a potential mineral product of subsurface CO2 storage for greenhouse gas reduction. Mar Pet Geol, 23(1): 61–77
https://doi.org/10.1016/j.marpetgeo.2005.07.001
57 T Xu, J A, Apps K Pruess, (2003). Reactive geochemical transport simulation to study mineral trapping for CO2 disposal in deep arenaceous formations. J Geophys Res Sol Ea, 108
https://doi.org/10.1029/2002JB001979
58 T Xu, J A Apps, K Pruess (2004). Numerical simulation of CO2 disposal by mineral trapping in deep aquifers. Appl Geochem, 19(6): 917–936
https://doi.org/10.1016/j.apgeochem.2003.11.003
59 Z Yang, T Xu, F Wang, Y Yang, X Li, N Zhao (2018a). Impact of inner reservoir faults on migration and storage of injected CO2. Int J Greenh Gas Control, 72: 14–25
https://doi.org/10.1016/j.ijggc.2018.03.006
60 H Yang, F Liu, H Zhao, R Wu (2018b). Hydrothermal process of synthetic gibbsite and the characteristics of Na in gibbsite crystal. Chem Pap, 72(12): 3169–3178
https://doi.org/10.1007/s11696-018-0551-2
61 Z Yu, K Liu, L Liu, S Yang, Y Yang (2017). An experimental study of CO2‐oil‐brine‐rock interaction under in situ reservoir conditions. Geochem Geophys Geosyst, 18(7): 2526–2542
https://doi.org/10.1002/2017GC006858
62 Z Yu, S Yang, K Liu, Q Zhou, L Yang (2019). An experimental and numerical study of CO2–brine-synthetic sandstone interactions under high-pressure (P)–temperature (T) reservoir conditions. App Sci, 9: 3354
https://doi.org/10.3390/app9163354
63 G Yuan, Y Cao, N Zan, H M Schulz, J Gluyas, F Hao, Q Jin, K Liu, Y Wang, Z Chen, Z Jia (2019). Coupled mineral alteration and oil degradation in thermal oil-water-feldspar systems and implications for organic-inorganic interactions in hydrocarbon reservoirs. Geochim Cosmochim Acta, 248: 61–87
https://doi.org/10.1016/j.gca.2019.01.001
64 B Zerai, B Z Saylor, G Matisoff (2006). Computer simulation of CO2 trapped through mineral precipitation in the Rose Run Sandstone, Ohio. Appl Geochem, 21(2): 223–240
https://doi.org/10.1016/j.apgeochem.2005.11.002
65 X Zhang, Z Wen, Z Gu, X Xu, Z Lin (2004). Hydrothermal synthesis and thermodynamic analysis of dawsonite-type compounds. J Solid State Chem, 177(3): 849–855
https://doi.org/10.1016/j.jssc.2003.09.019
66 H Zhao, S N Lvov (2016). Phase behavior of the CO2–H2O system at temperatures of 273–623 K and pressures of 0.1–200 MPa using Peng-Robinson-Stryjek-Vera equation of state with a modified Wong-Sandler mixing rule: an extension to the CO2–CH4–H2O system. Fluid Phase Equilib, 417: 96–108
https://doi.org/10.1016/j.fluid.2016.02.027
67 B Zhou, L Liu, S Zhao, X Ming, E H Oelkers, Z Yu, D Zhu (2014). Dawsonite formation in the Beier Sag, Hailar Basin, NE China tuff: a natural analog for mineral carbon storage. Appl Geochem, 48: 155–167
https://doi.org/10.1016/j.apgeochem.2014.07.015
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