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Dave Goldberg ([email protected]), Juerg Matter, Taro Takahashi and John Mutter Lamont-Doherty Earth Observatory of Columbia University, Palisades, New York Potential for Permanent CO 2 Sequestration in Sub-Bottom Oceanic Basalt Acid neutralization and cation release rates IODP drill site details and proposed CO 2 /tracer injection tests Juan de Fuca ridge flank: Drill site locations and basement topography CO 2 injection tests on land (Palisades diabase) See B33A-1010 for further detail on land injection tests Solute breakthrough curves Geochemical modeling 115 120 125 Calcium Magnesium -10.5 -10 -9.5 -9 -8.5 -8 -7.5 5.8 5.9 6 6.1 6.2 6.3 6.4 6.5 6.6 log(k) [mmol/cm 2 /s) pH -12 -11 -10 -9 -8 -7 -6 2 3 4 5 6 7 log(k) [mmol/cm 2 /s) pH Calcium Magnesium 2 3 4 5 6 7 0 0.4 0.8 1.2 1.6 2 2.4 2.8 3.2 pH calcium + magnesium added by dissolution (mol) CO 2 and subsequent mineral dissolu- tion reactions were modeled using PHREEQC. The initial fluid composition used in the model calculations is based on field measurements by Elderfield et al. (1999). The fluid was equilibrated with CO 2 (pCO 2 10 MPa, 60˚C), resulting in a pH of 3.09 and subsequently react- ing with Ca-Mg silicate minerals (diopside, forsterite in 2:1 molar ratio). The change in pH due to mineral disso- lution reveals that approximately 1.6 moles of Ca, Mg are required to neutral- ize injection conditions (pH 3 --> 6.7). Hydrothermal flow and fluid chemistry Abstract Ridge-flank basalt aquifers offer a unique scientific and technical opportunity for long-term sequestration of CO 2 . We investigate the potential for injection testing on the flank of the Juan de Fuca ridge, approximately 250 km west of Seattle. The ocean crust offers three explicit advantages over other potential sequestration targets: (1) it has a potential geological capacity large enough to accommodate a major portion of ~22 billion tons/yr of fossil fuel CO 2 (6 Gt-C/yr) which is produced globally; (2) the chemical reaction of CO 2 with basalt will produce (Ca,Mg,Fe) 2 CO 3 infilling minerals, permanently sequestering carbon in a chemically stable and non-toxic form; and (3) physical traps for potential CO 2 leakage below thick impermeable sediments and 2.5 km of cold ocean water. Based on laboratory and land-based field experiments, the rates of basalt dissolution and carbonate precipitation reactions are efficient. Recent studies from the Integrated Ocean Drilling Program suggest that deep basaltic aquifers on the eastern flank of the Juan de Fuca ridge offer large volumetric capacities, warm temperatures to facilitate CO 2 -basalt reactions, high permeability and sufficiently closed water-rock circulation pathways, long fluid retention times, and pre-existing technological options for the injection and subsequent monitoring of CO 2 . Field experiments are needed to monitor the fate of injected CO 2 -fluid tracers using sealed-in, semi-permanent instruments and samplers. Such experiments will establish the in situ rates of the basalt-brine-CO 2 reactions, the relationship of CO 2 injections to subsurface biologic activity, and the potential for immobilizing CO 2 as non-toxic and stable Ca-Mg carbonate minerals in oceanic basalt. Location maps of drill sites and nearby basement topography on the eastern flank of the Juan de Fuca ridge. The direction of fluid flow in the crust is inferred. Heat flow data indicate the drawdown of bottom water at Grizzly Bare, outflow at Baby Bare and a lack of thermal anomalies in between, suggesting that imper- meable sediments blanket the region near existing and proposed drill sites (from Fisher et al., 2003; Shipboard Scientific Party, 2004). Critical Questions: What is the potential capacity and retention time for CO 2 in the ocean crust? What is the rate of basalt-CO 2 neutralization and CaCO 3 pre- cipitation reactions in this environment? How does lateral permeability change after CO 2 injection and CaCO 3 precipitation? Where do CO 2 hydrates form? What is the response of subsurface microrganisms to stimu- lated biogeochemical processes after injection of CO 2 ? Which conservative tracers will be most effective (e.g. Xe, SF 6 , etc.) in this environment? Carbon dioxide injection test were conducted in a basalt forma- tion as single well push-pull tests. A CO 2 saturated fluid (pCO 2 ~20 atm, pH ~3.5) was injected into a hydraulically isolated zone, and pumped back after an incubation time of 1 to 3 weeks. Solute concentrations were measured in the extracted water samples and used to develop breakthrough curves. Break- through curves of conservative tracers (e.g. chloride, δ 2 H) were used to calculate recovery percentages for the injected solution and as a reference point that discounts for dilution through mixing. Breakthrough curves indicate chloride and major cation concentrations were reduced to back- ground levels <1000 minutes after pumping. Similar peak arrival times and shapes for these two curves suggest similar transport properties for chloride and calcium, although the mass of recovered calcium is larger than chloride (area under curves), indicating a significant contribu- tion of cations by rock dissolution. In situ rate constants for the bulk rock dissolution were computed using the mass transfer from the push-pull test, the residence time of the injected fluid in the injection interval, and the reactive surface area of the test interval. The ion release rates decrease with increasing pH, which is confirmed by laboratory experiments on crushed bulk rock samples. Based on the experimental results, and applying an average bulk rock dissolution rate of 0.138 mol/m 2 /hour, a 1000 m 3 volume of CO 2 saturated water at PCO 2 = 8 bar would be neutralized approximately 19 hours after injection. The release rates are anticipated to be even faster in oceanic basalt. Push-Pull Test Laboratory Test Tracer + CO 2 (liquid) Fluid Sampling Injection Phase Pumping Phase Illustration of completions in IODP Holes 1026B, U1302A, and U1301B (Shipboard Scientific Party, 2004). Instru- mented borehole packer systems will be used to monitor pressure, fluid conductivity, and sample fluids. Core samples from ODP Holes 1027C and 1026B, 624.4 and 268.6 meters below seafloor. Scales are given in centimeters. Conservative tracer injections are planned near these sites, and CO 2 injection tests are proposed 18-24 months later. Monitoring will occur at nearby (existing) holes offset by 200-2000m in orthogonal directions. Shipboard Scientific Party (2004), Juan de Fuca hydrogeology: The hydrogeologic architecture of basaltic oceanic crust: compartmentalization, anisotropy, microbiology, and crustal-scale properties on the eastern flank of Juan de Fuca Ridge, eastern Pacific Ocean. IODP Prel. Rept., 301. http:// iodp.tamu.edu/publications/PR/301PR/301PR.PDF. Fisher, A.T., E.E. Davis, M. Hutnak, V. Spiess, L. Zühlsdorff, A. Cherkaoui, L. Christiansen, K. M. Edwards, R. Macdonald, H. Villinger, M. J. Mottl, C. G. Wheat, and K. Becker (2003), Hydro- thermal recharge and discharge across 50 km guided by seamounts on a young ridge flank. Nature, 421:618–621. Spinelli, G.A., and Fisher, A.T. (2004), Hydrothermal circulation within topographically rough basaltic basement on the Juan de Fuca Ridge flank, Geochem., Geophys., Geosyst., doi 5:10.1029/2003GC000616. Elderfield, H., C.G. Wheat, M. J. Mottl, C. Monnin, and B. Spiro (1999), Fluid and geochemical transport through oceanic crust: a transect across the eastern flank of the Juan de Fuca Ridge,.Earth Planet. Sci. Lett., 172:151–165. (A) Spatial distribution and depths of existing drill sites at basement ridges and troughs. (B) Measured heat flow and basement tempera- tures. Near-constant 60˚C temperatures imply vigorous advection and homogenization of basement fluids. (C) C 14 age and Mg ++ concentrations in recov- ered basement fluids. Younger ages at Sites 1026/1027 relative to the ridge indicate that fluids must recharge elsewhere. C 14 age of base- ment fluids at Site 1026 is ~4300 yrs with respect to zero-age bottom water, a residence time suffi- cient for geochemical equilibration with altered basalt (from Elderfield et al., 1999; Shipboard Sci- entific Party, 2004). References cited Preferred flow model in basement near Site 1026 and 1027. Channelized fluid flow with k=10 -9 m 2 reproduces relative pressure observations at Site 1026 and 1027 (from Spinelli and Fisher, 2004). Experimental data indicate bulk k=10 -10 to 10 -13 m 2 , with significant uncertainty due to scale and an- isotropy effects (Shipboard Scientific Party, 2004). Natural Analog: Magnesite filled fractures in the Samail Ophiolite, Sultanate of Oman 0 1 2 3 4 5 6 7 8 0 500 1000 1500 2000 Ca (mmol/kg) time since injection stopped (min) 1.5 2 2.5 3 3.5 4 4.5 5 0 500 1000 1500 2000 Cl (mmol/L) time since injection stopped (min) Geochemical Sequestration Model (idealized reaction scheme) Process 1: CO 2 dissolution into formation fluid, carbonic acid formation,and deprotonation CO 2 (g) = CO 2 (aq) CO 2 (aq) + H 2 O = CO 3 2- + 2H + Process 2: Acid Neutralization Reaction with host rocks and CaCO 3 precipitation CaAl 2 Si 2 O 8 + 2H + + 2H 2 O = Ca 2+ Al 2 Si 2 O 5 (OH) 4 Ca 2+ + CO 3 2- = CaCO 3 (s) Net Mineral Trapping Reaction CaAl 2 Si 2 O 8 + CO 2 + 2H 2 O = CaCO 3 + Al 2 Si 2 O 5 (OH) 4 110 17.5 20 22.5 25 27.5 L A M O N T D O H E R T Y B O R E H O L E R E S E A R C H

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Dave Goldberg ([email protected]), Juerg Matter, Taro Takahashi and John MutterLamont-Doherty Earth Observatory of Columbia University, Palisades, New York

17.5

Potential for Permanent CO2 Sequestration in Sub-Bottom Oceanic Basalt

Acid neutralization and cation release rates

IODP drill site details and proposed CO2/tracer injection tests

Juan de Fuca ridge flank: Drill site locations and basement topography

CO2 injection tests on land (Palisades diabase)See B33A-1010 for further detail on land injection tests

Solute breakthrough curves Geochemical modeling

115

120

125

CalciumMagnesium

-10.5

-10

-9.5

-9

-8.5

-8

-7.5

5.8 5.9 6 6.1 6.2 6.3 6.4 6.5 6.6

log(

k) [m

mol

/cm

2 /s)

pH

-12

-11

-10

-9

-8

-7

-6

2 3 4 5 6 7

log(

k) [m

mol

/cm

2 /s)

pH

CalciumMagnesium

2

3

4

5

6

7

0 0.4 0.8 1.2 1.6 2 2.4 2.8 3.2

pH

calcium + magnesium added by dissolution (mol)

CO2 and subsequent mineral dissolu-tion reactions were modeled using PHREEQC. The initial fluid composition used in the model calculations is based on field measurements by Elderfield et al. (1999). The fluid was equilibrated with CO2 (pCO2 10 MPa, 60˚C), resulting in a pH of 3.09 and subsequently react-ing with Ca-Mg silicate minerals (diopside, forsterite in 2:1 molar ratio). The change in pH due to mineral disso-lution reveals that approximately 1.6 moles of Ca, Mg are required to neutral-ize injection conditions (pH 3 --> 6.7).

Hydrothermal flow and fluid chemistryAbstractRidge-flank basalt aquifers offer a unique scientific and technical opportunity for long-term sequestration of CO2. We investigate the potential for injection testing on the flank of the Juan de Fuca ridge, approximately 250 km west of Seattle. The ocean crust offers three explicit advantages over other potential sequestration targets: (1) it has a potential geological capacity large enough to accommodate a major portion of ~22 billion tons/yr of fossil fuel CO2 (6 Gt-C/yr) which is produced globally; (2) the chemical reaction of CO2 with basalt will produce (Ca,Mg,Fe)2 CO3 infilling minerals, permanently sequestering carbon in a chemically stable and non-toxic form; and (3) physical traps for potential CO2 leakage below thick impermeable sediments and 2.5 km of cold ocean water. Based on laboratory and land-based field experiments, the rates of basalt dissolution and carbonate precipitation reactions are efficient. Recent studies from the Integrated Ocean Drilling Program suggest that deep basaltic aquifers on the eastern flank of the Juan de Fuca ridge offer large volumetric capacities, warm temperatures to facilitate CO2-basalt reactions, high permeability and sufficiently closed water-rock circulation pathways, long fluid retention times, and pre-existing technological options for the injection and subsequent monitoring of CO2. Field experiments are needed to monitor the fate of injected CO2-fluid tracers using sealed-in, semi-permanent instruments and samplers. Such experiments will establish the in situ rates of the basalt-brine-CO2 reactions, the relationship of CO2 injections to subsurface biologic activity, and the potential for immobilizing CO2 as non-toxic and stable Ca-Mg carbonate minerals in oceanic basalt.

Location maps of drill sites and nearby basement topography on the eastern flank of the Juan de Fuca ridge. The direction of fluid flow in the crust is inferred. Heat flow data indicate the drawdown of bottom water at Grizzly Bare, outflow at Baby Bare and a lack of thermal anomalies in between, suggesting that imper-meable sediments blanket the region near existing and proposed drill sites (from Fisher et al., 2003; Shipboard Scientific Party, 2004).

Critical Questions:

• What is the potential capacity and retention time for CO2 in the ocean crust?

• What is the rate of basalt-CO2 neutralization and CaCO3 pre-cipitation reactions in this environment?

• How does lateral permeability change after CO2 injection and CaCO3 precipitation?

• Where do CO2 hydrates form?

• What is the response of subsurface microrganisms to stimu-lated biogeochemical processes after injection of CO2?

• Which conservative tracers will be most effective (e.g. Xe, SF6, etc.) in this environment?

Carbon dioxide injection test were conducted in a basalt forma-tion as single well push-pull tests. A CO2 saturated fluid (pCO2 ~20 atm, pH ~3.5) was injected into a hydraulically isolated zone, and pumped back after an incubation time of 1 to 3 weeks. Solute concentrations were measured in the extracted water samples and used to develop breakthrough curves. Break-through curves of conservative tracers (e.g. chloride, δ2H) were used to calculate recovery percentages for the injected solution and as a reference point that discounts for dilution through mixing.

Breakthrough curves indicate chloride and major cation concentrations were reduced to back-ground levels <1000 minutes after pumping. Similar peak arrival times and shapes for these two curves suggest similar transport properties for chloride and calcium, although the mass of recovered calcium is larger than chloride (area under curves), indicating a significant contribu-tion of cations by rock dissolution.

In situ rate constants for the bulk rock dissolution were computed using the mass transfer from the push-pull test, the residence time of the injected fluid in the injection interval, and the reactive surface area of the test interval. The ion release rates decrease with increasing pH, which is confirmed by laboratory experiments on crushed bulk rock samples. Based on the experimental results, and applying an average bulk rock dissolution rate of 0.138 mol/m2/hour, a 1000 m3 volume of CO2 saturated water at PCO2 = 8 bar would be neutralized approximately 19 hours after injection. The release rates are anticipated to be even faster in oceanic basalt.

Push-Pull Test Laboratory Test

Tracer + CO2 (liquid) Fluid Sampling

Injection Phase Pumping Phase

Illustration of completions in IODP Holes 1026B, U1302A, and U1301B (Shipboard Scientific Party, 2004). Instru-mented borehole packer systems will be used to monitor pressure, fluid conductivity, and sample fluids.

Core samples from ODP Holes 1027C and 1026B, 624.4 and 268.6 meters below seafloor. Scales are given in centimeters. Conservative tracer injections are planned near these sites, and CO2 injection tests are proposed 18-24 months later. Monitoring will occur at nearby (existing) holes offset by 200-2000m in orthogonal directions.

Shipboard Scientific Party (2004), Juan de Fuca hydrogeology: The hydrogeologic architecture of basaltic oceanic crust: compartmentalization, anisotropy, microbiology, and crustal-scale properties on the eastern flank of Juan de Fuca Ridge, eastern Pacific Ocean. IODP Prel. Rept., 301. http:// iodp.tamu.edu/publications/PR/301PR/301PR.PDF.

Fisher, A.T., E.E. Davis, M. Hutnak, V. Spiess, L. Zühlsdorff, A. Cherkaoui, L. Christiansen, K. M. Edwards, R. Macdonald, H. Villinger, M. J. Mottl, C. G. Wheat, and K. Becker (2003), Hydro-thermal recharge and discharge across 50 km guided by seamounts on a young ridge flank. Nature, 421:618–621.

Spinelli, G.A., and Fisher, A.T. (2004), Hydrothermal circulation within topographically rough basaltic basement on the Juan de Fuca Ridge flank, Geochem., Geophys., Geosyst., doi 5:10.1029/2003GC000616.

Elderfield, H., C.G. Wheat, M. J. Mottl, C. Monnin, and B. Spiro (1999), Fluid and geochemical transport through oceanic crust: a transect across the eastern flank of the Juan de Fuca Ridge,.Earth Planet. Sci. Lett., 172:151–165.

(A) Spatial distribution and depths of existing drill sites at basement ridges and troughs.

(B) Measured heat flow and basement tempera-tures. Near-constant 60˚C temperatures imply vigorous advection and homogenization of basement fluids.

(C) C14 age and Mg++ concentrations in recov-ered basement fluids. Younger ages at Sites 1026/1027 relative to the ridge indicate that fluids must recharge elsewhere. C14 age of base-ment fluids at Site 1026 is ~4300 yrs with respect to zero-age bottom water, a residence time suffi-cient for geochemical equilibration with altered basalt (from Elderfield et al., 1999; Shipboard Sci-entific Party, 2004).

References cited

Preferred flow model in basement near Site 1026 and 1027. Channelized fluid flow with k=10-9 m2 reproduces relative pressure observations at Site 1026 and 1027 (from Spinelli and Fisher, 2004). Experimental data indicate bulk k=10-10 to 10-13 m2, with significant uncertainty due to scale and an-isotropy effects (Shipboard Scientific Party, 2004).

Natural Analog: Magnesite filled fractures in the Samail Ophiolite, Sultanate of Oman

0

1

2

3

4

5

6

7

8

0 500 1000 1500 2000

Ca

(mm

ol/k

g)

time since injection stopped (min)

1.5

2

2.5

3

3.5

4

4.5

5

0 500 1000 1500 2000

Cl (

mm

ol/L

)

time since injection stopped (min)

Geochemical Sequestration Model (idealized reaction scheme)Process 1:CO2 dissolution into formation fluid, carbonic acid formation,and deprotonationCO2(g) = CO2(aq)

CO2(aq) + H2O = CO32- + 2H+

Process 2:Acid Neutralization Reaction with host rocks and CaCO3 precipitationCaAl2Si2O8 + 2H+ + 2H2O = Ca2+ Al2Si2O5(OH)4Ca2+ + CO3

2- = CaCO3(s)

Net Mineral Trapping ReactionCaAl2Si2O8 + CO2 + 2H2O = CaCO3 + Al2Si2O5(OH)4

110 17.5

20

22.5

25

27.5

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EHOLE RESEARCH