The Influence of Rock Mineralogy on Reactive Fracture Evolution in

92 engineering activities, including an evaporite limestone and a carbonate-rich shale. The fracture. 93. Page 5 of 28. ACS Paragon Plus Environment...
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The Influence of Rock Mineralogy on Reactive Fracture Evolution in Carbonate-rich Caprocks Kasparas Spokas, Catherine A. Peters, and Laura Pyrak-Nolte Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.8b01021 • Publication Date (Web): 09 Aug 2018 Downloaded from on August 10, 2018

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Environmental Science & Technology

The Influence of Rock Mineralogy on Reactive Fracture Evolution in Carbonate-rich Caprocks Kasparas Spokas1, Catherine A. Peters1*, Laura Pyrak-Nolte2,3,4 1

Department of Civil & Environmental Engineering, Princeton University, Princeton, New Jersey, 08544 2 Department of Physics and Astronomy, Purdue University, West Lafayette, Indiana, 47907 3 Lyle School of Civil Engineering, Purdue University, West Lafayette, Indiana, 47907 4 Department of Earth, Atmospheric and Planetary, Purdue University, West Lafayette, Indiana, 47907 *Corresponding author: Dr. Catherine A. Peters ([email protected]), E417A Engineering Quad, Department of Civil & Environmental Engineering, Princeton University, Princeton, New Jersey, 08544.

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1 2 3



storage of greenhouse gases, because of the possibility of unwanted upward fluid migration. The


risks of fluid leakage may be exacerbated if fractures are subjected to physical and chemical


perturbations that alter their geometry. This study investigated this by constructing a 2D fracture


model to numerically simulate fluid flow, acid-driven reactions, and mechanical deformation.


Three rock mineralogies were simulated: a limestone with 100% calcite, a limestone with 68%


calcite, and a banded shale with 34% calcite. One might expect transmissivity to increase fastest


for rocks with more calcite due to its high solubility and fast reaction rate. Yet, results show that


initially transmissivity increases fastest for rocks with less calcite because of their ability to


deliver unbuffered-acid downstream faster. Moreover, less reactive minerals become persistent


asperities that sustain mechanical support within the fracture. However, later in the simulations,


the spatial pattern of less reactive mineral, not abundance, controls transmissivity evolution.


Results show a banded mineral pattern creates persistent bottlenecks, prevents channelization,


and stabilizes transmissivity. For sites for geologic storage of CO2 that have carbonate caprocks,


banded mineral variation may limit reactive evolution of fracture transmissivity and increase


storage reliability.

Fractures present environmental risks for subsurface engineering activities, such as geologic

19 20 21

1. Introduction The leakage of fluids from engineered subsurface reservoirs poses environmental


pollution risk (1-2), jeopardizes security of greenhouse gas containment (3), and may


compromise regulatory compliance (4). In subsurface environments, fractures, faults and


abandoned or leaky wells can act as upward leakage pathways because of their high permeability

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relative to surrounding media (5-7). As a result, such leakage pathways present a large risk for


many subsurface engineering activities, such as geologic carbon storage, natural gas storage, oil


and gas extraction, enhanced-oil recovery, geothermal energy production, and deep-well


injection of hazardous wastes.

29 30

In the context of geologic carbon storage, the injection of supercritical CO2 creates


geochemical and geomechanical perturbations that could exacerbate the likelihood of vertical


leakage of CO2. Dissolution of CO2 into resident brine creates an acidified fluid that has


favorable conditions for dissolving carbonate minerals (8-11). The flow of acidic fluids through


fractures could result in mineral dissolution that enlarges the fracture aperture and its


permeability (12). Moreover, injection of fluids could change effective stresses on fractures (13),


which could alter geochemical-geomechanical coupled processes. To avert the risks associated


with unwanted fracture leakage, the factors that influence the geochemical and geomechanical


alteration of fractures must be better understood.

39 40

Reactive flow laboratory experiments and modeling studies have found that the fracture


surface dissolution pattern, i.e. the spatial distribution of apertures and how it evolves, is a very


important determinant of how the fluid flow increases. For example, channelization, which


results from a positive-feedback between the delivery of acid and aperture enlargement (14), can


lead to very fast increase in fluid flow. Other factors that have been identified include flow rate


(15-24), fracture length-scale (25), fluid reactivity (14, 25-29), aperture geometry (probabilistic


distribution and spatial correlation) (17, 24, 30-31) and particle decohesion and mineral


precipitation (33-34).

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The effect of mineral heterogeneity, which we define as the presence of more than one


mineral phase, is less understood (12, 33-34, 35, 38-42). Mineral heterogeneity can result in


barriers to flow and result in the dislocation of less reactive mineral grains that clog the fracture


opening (12, 33). Moreover, less reactive minerals in the rock matrix can lead to the formation of


reaction-induced porous layers (12, 36, 38) that have been shown to suppress reaction rates by


serving as a diffusion barrier for mass transfer (37). In contrast, Deng et al., (39) demonstrated


that mineral heterogeneity can enhance fracture channelization if the reactive mineral area is


contiguous in the direction of flow. Similar observations have been made for porous media about


the effects of variable porosity, mineral heterogeneity, and “worm-holing” (43-46).

57 58

It remains unclear how mineral heterogeneity will affect the coupling of geochemical and


geomechanical processes. For homogenous rocks, one hypothesis is that the dissolution of rock


material holding the fracture walls apart could lead to wall closure and a reduction of


permeability (16, 25, 47-53). Subsurface rocks, however, are often not mineralogically


homogenous. For heterogeneous rock mineralogies, a hypothesis is that less reactive rock


material remains stable, props the fracture open, and inhibits fracture closure and permeability


decrease. This would suggest less reactive minerals could prevent dissolution-induced fracture



66 67

The objective of this study was to investigate the effects of mineral heterogeneity on


geochemical-geomechanical coupling and overall fracture evolution. This study models reactive


transport through fractures in mineralogically heterogeneous carbonate rocks subject to


mechanical stress normal to the fracture plane. To evaluate this objective, we coupled a two-

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dimensional (2D) fracture reactive transport model (39) and a mechanical deformation model


(54-55) to simulate flow, reaction and deformation at multiple confining stresses. A 2D fracture


reactive transport model has the potential for over-prediction of reaction in a 2D framework due


to over-prediction of flow and concentration gradients that could limit reaction rates (20, 39).


Despite this, 2D reactive transport modeling is a valuable analytical tool that allows for


computationally practical simulation of fracture evolution (20, 23, 30, 39), enabling exploration


of a large parameter space and hypothetical scenarios that are beyond experimental feasibility.

78 79

The effect of pressure dissolution (56, 57), which is a form of plastic deformation, was


also investigated. However, the effects of pressure dissolution were found to be small at the


geologic carbon storage depth (1000 meters) and temperature (323 K) modeled in this study.


This is because the stress at the contacting asperities were either below or not much higher than


the critical stress (56). Therefore, we do not include pressure dissolution results in the body of


the article and include it in the Supporting Information.

85 86

Simulations were performed under different constant effective normal stresses of 10 and


50 MPa to represent a range of possible overburden, tectonic, and fluid forces present in geologic


carbon storage environments. This study utilized only a single flow regime, one that results in


channelization in a homogenous rock fracture. This decision was purposeful, to highlight the


capability of mineral heterogeneity to override flow rate effects to shape the evolution of fracture



92 93

The cases of mineral heterogeneity were based on rocks relevant in subsurface engineering activities, including an evaporite limestone and a carbonate-rich shale. The fracture

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was positioned to be orthogonal to the sedimentary bedding layers to represent vertical flow.


The model includes calcite as the only reactive mineral and separates heterogenous mineralogies


into binary mineral maps of calcite and effectively unreactive mineral. In many studies, the


dissolution of calcite is the primary driver of fracture enlargement and permeability increase (12,


14, 36-37, 39). In comparison to other minerals, calcite’s high solubility, fast dissolution kinetics,


and natural abundance makes calcite the mineral most likely to dissolve in quantities that cause


significant permeability increase (10). Other acid-sensitive minerals, such as dolomite, have


kinetic dissolution rate constants that are at least an order of magnitude lower than calcite (58),


and soluble silicates such as anorthite are rarely sufficiently abundant in sedimentary rock for


their dissolution to create large changes in void space. The importance of calcite is further


reinforced by experimental core flooding (45-46, 59) and field observation in limestone caves


(60). Minerals prone to oxidation reactions, such as pyrite, are also not considered because the


typical oxygen fugacity of deep saline formations is on the order of 10-63 bar (61), too low to


drive significant reaction.

108 109

2. Methods


2.1 System & Boundary Conditions


The simulated fracture geometry in this study derives from a previous experimental


fracture (14), which was generated in the laboratory by inducing a fracture in an Indiana


limestone rock core using the modified-Brazilian method. This experimental fracture geometry


was generated by imaging the fracture using 3D X-ray computed tomography (xCT) (62) (Figure


1a). To generate the 2D model of the fracture, the 3D geometry was projected onto a plane and a


digitized variable aperture map with a resolution of 30 µm was generated. Then, a new fracture

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geometry was generated in which apertures were randomly sampled from a statistically


representative log-normal distribution of the fracture apertures. It was assumed that there was no


spatial correlation length. The aperture map was then coarsened by spatial averaging to a

120 121

resolution of 560 µm (∆x and ∆y) to achieve computational efficiency. The resulting fracture size is 22.5 mm in width by 50 mm in the direction of flow (Figure 1b). The fracture plane is


discretized in the x and y dimensions and each grid cell has a unique aperture, b, i.e. the local


distance between the two fracture walls. The average aperture is 311 µm with a standard


deviation of 1.67 µm (Figure 1c). This is the initial fracture geometry for all the simulations. This


enables control of this condition in a way that cannot be controlled in experiments, where


separate fractures are subject to variations caused by the fracturing method.

127 128

The simulated reactive fluid was based on a 1 M NaCl brine equilibrated with CO2 at 7.7


MPa, resulting in a pH of 3.3 (14). Boundary conditions include no-flow boundaries along the


sides of the fracture and a constant pressure gradient of 6.6 Pa along the length of the fracture. A


constant pressure gradient was chosen to represent the conditions that may exist in the subsurface


for an upward fracture through a caprock that lies above a pressurized injection formation. It is


assumed that increasing flow through the fracture does not change large-scale formation fluid


pressures. Flow was simulated for ~72 hours, a timeframe that is regular for reactive flow


experiments at this scale, which allows for significant alteration of the fracture geometry, and is


not computationally cumbersome.


In the deformation model, the fracture is treated as two fracture walls that are held open


by elastic asperities. The asperities are represented as cylinders (Figure 1d) to allow for


analytical solutions to the elastic deformation equations. This is in contrast with the reactive

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transport model in which the asperities are modeled as rectangular prisms (Figure 1e). In the

deformation model, the diameter of the columns equals ∆x, the width of the cells in the reactive


transport model. Contact occurs when asperities span the distance between the two fracture walls


and provide mechanical support. Free-boundary conditions were assumed around the perimeter


of the sample. More resolved columns did not substantially change the mechanical equilibrium


of the fracture. While sensitivity of grid resolution was not tested for the coupled geochemical-


geomechanical model, previous reactive transport modeling studies have reported little to no


sensitivity (39, 63). a)

b) c)


y 50


Flo w

22.5 mm

22.5 mm


m m

σn e) i Surface A i-j

j ∆y ∆y


148 149 150 151 152 153 154

22.5 mm


Figure 1. a) Schematic of an xCT image of a fractured rock core (cropped to show detail), b) 2D representation of the discretized fracture in the reactive transport model with normal stress applied orthogonal to the fracture plane, c) initial aperture map, d) the cylindrical column representation in the deformation model, and e) reactive surface area for cell i is quantified by the sum of all exposed areas (red).

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2.2 Reactive Transport Model To simulate reactive transport, a modified version of the 2D, variable aperture, multispecies reactive transport model developed by Deng et al., (39) was used.

158 159 160 161

For species s, the governing equation in a discrete grid cell is   

= −∇ ∙   + ∇ ∙  ∙ ∇  + 


where b is aperture, Cs is the molar concentration of species s,  is the net volumetric flow rate,


Dm is the molecular diffusion coefficient, and R is the rate of reaction of species s due to calcite


reaction. Mechanical dispersion and tortuosity implicitly are not explicitly modeled as they arise


from in-plane velocity variations caused by directional aperture variation between discrete cells.


In addition, the model does not consider electrostatic effects and uses the same value for Dm for


all species, as in previous reactive transport modeling studies (38-39, 64).

167 168

To numerically solve eq 1, a five-point central difference approximation was used. The


procedure performs four sequential calculations during each time step: solute transport due to the


fluid pressure field, chemical equilibration with respect to instantaneous aqueous phase reactions,


kinetically-limited reaction of calcite based on local chemistry, and the final aqueous phase


equilibration after reaction. See Supporting Information for all modeling parameter values used.


The time step is determined such that the Courant number, a parameter used to ensure


convergence of finite difference approximations, is well-below unity. The flow field for the


entire 2D system is updated to reflect reaction-induced changes in fracture geometry. To


calculate the flow field, the 2D parallel-plate cubic law model is assumed to be valid locally


within each cell and a 2D steady-state mass balance is solved (65-66). Transmissivities at the cell

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boundaries are calculated using the harmonic mean of the cell’s and the adjacent cell’s


transmissivity, an update to the model of Deng et al., (39).

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180 181 182

Changes to fracture hydraulic properties are reported using transmissivity T measured along the entire length of the fracture using Darcy’s Law, =


QμL ∆



where Q is the volumetric flow rate through the fracture, µ is the viscosity of water, L is the


length of the fracture, and ∆P is the pressure difference along the fracture (66). The use of


transmissivity, rather than permeability, is purposeful as transmissivity is the parameter that


controls leakage in the subsurface. The importance of distinguishing the two quantities when


characterizing the evolution of fracture geometry both in simulation and experiments is provided


in the Supporting Information.

190 191

Chemical equilibrium of the aqueous phase is modeled by the carbonate system. The set


of primary components for which independent balance equations are written is Ca2+, CO32-, and


H+. Secondary aqueous species concentrations are calculated using mass action laws and a


charge balance equation.

195 196

The reaction rate is based on Transition State Theory, which accounts for the kinetic rate


and a thermodynamic driving force. The reaction rate requires the reactive surface area, and in


this application an important modification was made to allow for contacting asperities to dissolve.


In Deng et al., (39), the area modeled as exposed to reactive fluid in a cell is the planar area


2∆x∆y. In that model, contacting asperities cannot dissolve because they do not have an aperture

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(b=0), so there is no flow through the cell to dissolve the planar area rock surface. In this study,


the model considers the surface area exposed to flow to be both the surfaces parallel to and


perpendicular to flow (Figure 1e). This is represented by the eq 3 for reaction in cell i. Because


each perpendicular face is exposed to the solution chemistry of its adjacent cell, the calculation


of dissolution on each face in a cell is treated individually,


R =

2∆"∆# k%a'(), + , 1 −

>DE + ∑>DF ;A=> ∗ k%a'(),> + @ 1 − 

207 208 209 210

%./012 + 3. 


/415 1



%./012 + 3. A


/415 1





where Ksp is the calcite solubility product constant, j refers to an adjacent cell, GH=I refers to the surface of cell i facing cell j (Figure 1d) that is calculated by A=> = J

∆x %b> − b + if b> − b > 0 0 if I − H < 0


(∆x = ∆y. The volume of the fluid, S, and local aperture are used to convert the reaction rate


into units of moles per area per time. The sum of the dissolution to all five faces is converted to


an aperture change in cell i to avoid variably changing cell dimensions. This assumption does not


account for potential thinning of asperities that could be more susceptible to deformation or


effects of reaction on rock mechanical properties. In experiments, these processes could lead to


asperity fragments breaking off, leading to fracture closure or clogging from mobile rock


particles that become lodged in fracture bottlenecks.

217 218 219

The dissolution kinetics of calcite is modeled assuming three parallel reactions driven by H+(aq), H2CO3(aq) and H2O (l):

\Z Z = TUV  + WXY ⟷ TXY + WUV XY

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\Z = TUV  + W\ UVXY ⟷ TXY + 2WUVXY

\Z = = TUV  + W\ U] ⟷ TXY + WUV XY + UWXY


As such, the kinetic coefficient of calcite dissolution is the difference between the sum of the


forward rates of reaction and the backwards rate:

222 223 224

kT(  = kF a^Z  + k \ a^\_`V  + k V a^\`  − k  a_`15 a_.12  1


where k1, k2, k3, kb are rate coefficients determined for high carbonic acid conditions by Deng et al., (24),aS is the activity of the species denoted by subscript s and T( is the vector of species


activities used in the equation. In this work, activities were determined using activity coefficients


calculated using the Davies equation. Because the ionic strength is dominated by the invariant


species, sodium and chloride, the activity coefficients are largely invariant and are modeled as


constants throughout the simulations.

229 230

2.3 Elastic Deformation Model


This study utilizes the deformation model summarized in Pyrak-Nolte & Morris, (54) which


simulates elastic deformation of fracture surfaces and the asperities that provide regions of


contact between the two surfaces. To determine the solution for a specific normal stress on the


fracture, σn, the separation between the fracture walls, D, is incrementally reduced until the sum


of all the forces on all contacting asperities equals the force on the fracture surfaces:


∑ f = σb A



where fi is the force acting on the column in grid cell i, and A is the total area of the fracture


domain. For a contacting asperity in cell i, the elastic deformation is solved geometrically:



D + W = Le − ∆L

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where Wi is the deformation of the fracture wall, feH is the original height of the column, and ∆fH is defined as

∆L = f ∗






where E is the elastic modulus of the column and a is the radius of the column. For a specific D,


eq 7 is written for every contacting asperity and a set of linear equations is solved for all fi.

245 246 247

Because Wi and ∆fH depend on fi, this requires an iterative process to calculate the solution at

each cell to ensure elastic deformation kH does not result in a loss of contact between the two

fracture surfaces. This study does not model incremental adjustments of the orientation of the


fracture walls, as this is most relevant for uniform dissolution patterns in a homogenous reactive


rock (52), which are not considered in this study.


To couple the mechanical deformation model with the reactive transport model, a


numerical scheme was devised in which, at every time step, the calculation of fracture


geomechanical equilibrium precedes the calculation of the flow field. Therefore, the dissolution


of rock material, which shortens column heights, results in a new initial fracture geometry in the


mechanical deformation model and results in a new mechanical equilibrium that affects the flow


field. This numerical scheme is repeated until the end of the simulation.

256 257

2.4 Heterogenous Mineralogies


Two heterogeneous mineral patterns were analyzed in this study: the Amherstburg


limestone and the Eagle Ford shale. For comparison, an all-calcite case similar to Deng et al.


(14) and Deng et al. (39) was used to represent a granular homogeneous limestone made up


entirely of calcite, such as the Indiana limestone. The Amherstburg limestone is a dolomitic-


limestone evaporite, and it serves as the primary caprock for the U.S. Department of Energy pilot


CO2 injection project that was conducted in Ostego County, Michigan. The dominant minerals in

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the Amhestburg limestone are calcite, dolomite, quartz, fluorite and clay minerals (41). The


mineralogical makeup of the fracture shows nodular pattern of calcite and substantially slower


reacting dolomite (12, 33, 39). The Eagle Ford shale is an organic-rich laminated shale


containing 34% calcite from an oil-producing region in west Texas (67). The dominant minerals


in the Eagle Ford shale are calcite, quartz, and clay minerals (67). The distinguishing feature of


this rock mineralogy is the layered structure of the minerals, reflecting the bedding planes of the


sedimentary rock.


Binary mineral maps depicting calcite and effectively unreactive minerals were


constructed for the homogeneous and the two heterogeneous fractures with the same resolution


as the fracture aperture discretization (Figure 2). For the Amherstburg limestone, x-ray


attenuation contrast differences in xCT images presented in Ellis & Peters, (41) were used to


map the location of calcite. This study uses a coarsened version of mineral map “A” from Ellis &


Peters, (41) which was also used in Deng et al. (39). Results from this study are not a repetition


however, as we apply a new aperture geometry and simulate geochemical-geomechanical


coupling. For the Eagle Ford shale, the basis for the mineral map was a micro-XRF elemental


map of a rock fracture surface generated by Fitts et al., (68). To generate the binary mineral map,


the elemental map (shown in the Supporting Information) was segmented based on high calcium


content (and low iron content). The threshold for segmentation was chosen such that the final


fracture contains 34% calcite. It is acknowledged that the spatial dimensions of the XRF map is


on the mm-scale while the simulated fracture is on the cm-scale. Still, the XRF map provides a


useful mineral pattern that is indicative of many sedimentary rocks at multiple length scales.

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285 286 287 288

Figure 2. Binary fracture mineralogy maps of the a) all-calcite, b) Amherstburg limestone, and c) Eagle Ford shale with respect to calcite. White denotes calcite and black denotes other minerals.


In the reactive transport simulations, for cells labeled as not reactive, the R in eq 1 is


equal to zero. Thus, the only possibility for aperture change in unreactive areas is compression


due to geomechanical stress.

292 293

3. Results


3.1 Effect of Normal Stress


Simulations of reactive flow and elastic deformation with the three mineralogies for σn


values of 10 and 50 MPa are presented in this section. The results are presented as maps of


change in aperture, the difference in aperture between the current and initial state, ∆b, over time


(Figure 3). Alteration of fracture apertures reflects contributions from both reaction-driven


mineral dissolution and mechanical deformation.

300 301

For higher σn, the reaction front’s propagation along the flow direction is slower than at


lower stress (Figure 3). There are two explanations for this. First, the initial compression of the


fracture to 10 and 50 MPa results in initial fracture transmissivities of 5.6 x 10-12 and 3.1 x 10-12


m4, respectively. Low transmissivity results in the delivery of a smaller amount of reactive fluid

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and slower advancement of the reaction front than for higher values of transmissivity. Second,


dissolution of contacting asperities removes the support that holds the fracture surfaces apart.


Figure 4a presents a snapshot of contact asperities of the 50 MPa all-calcite simulation at 36


hours. During reactive flow, asperities are preferentially dissolved due to their large surfaces


perpendicular to flow. The removal of asperities loads remaining asperities with more


compression force that results in further elastic compression and a decrease in aperture. This


fracture closure creates new asperities that were initially too short prior to reactive flow. This


competition between asperity destruction and creation remains roughly in balance throughout the


simulations, and fracture contact area remains mostly constant (see Supporting Information). The


greater the normal stress on the fracture, the larger the forces that need to be redistributed and the


greater the column compression. High normal stress increases the load to be redistributed and


results in stronger geochemical-geomechanical coupling. Under 50 MPa, dissolution-induced


compression results in negative changes in aperture downstream, i.e. apertures become smaller


than the initial aperture prior to flow (Figure 4a). In comparison, the aperture change for the 10


MPa simulation shows no negative values because the fast reaction front increases apertures


downstream and the redistribution of the load onto the remaining asperities results in only a


small amount of additional compression.

322 323

Comparison between the 10 MPa and 50 MPa simulations of the Amherstburg limestone


and the Eagle Ford shale also shows a relative decrease in aperture (Figure 4b and 4c) and


transmissivity rise (Figure 3). However for heterogeneous fractures, nonreactive areas are not


chemically eroded (Figure 4c) and provide sustained mechanical support. This weakens the


geochemical-geomechanical coupling and inhibits fracture closure. As a result, the difference

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between the 10 and 50 MPa horizontally-averaged ∆b profiles is the smallest for the Eagle Ford Shale (Figure 4c).

330 331

3.2 Effect of Mineral Heterogeneity


Comparison of the three fracture evolutions showcases how mineral heterogeneity, and


specifically the spatial distribution of less reactive minerals, can result in an increase or decrease


in the rate of transmissivity increase compared to the all-calcite fracture. For the all-calcite


mineralogy (Figure 3a), high solution reactivity near the fracture inlet causes the greatest


increase in aperture, but the increase in alkalinity from mineral dissolution neutralizes the acid


and reduces the reactivity downstream and limits transmissivity increase due to unreacted


downstream apertures. However after 20-30 hours, once instabilities in the reaction front are


established, flow channels are established because of the positive feedback between enlarging


aperture and reactive flow delivery. Soon after the channel spans the length of the fracture,


transmissivity rapidly increases. This is confirmed when comparing snapshots of aperture change


maps with simulation time (Supporting Information).

343 344

For the Amherstburg limestone (Figure 3b), a channel develops on the left side, much


like for the all-calcite fracture, around the nodular areas of unreactive minerals. This channel


development arises from a connected path of reactive minerals in the direction of flow and the


same channelization process observed for the all-calcite fracture (Figure 3b). In comparison with


the all-calcite simulation, the transmissivity of the Amherstburg limestone rises faster due to


faster reaction-front propagation, as can be slightly seen in Figure 3b. At 52 hours for the 50


MPa simulations, the transmissivity of the all-calcite simulation has risen by a factor of 2.8. In

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contrast, the Amherstburg limestone simulation transmissivity has risen by a factor of 13.0. The


reaction-front propagates faster for the Amherstburg limestone because there is less calcite rock


material to dissolve and neutralize the reactive fluid, which allows flow to remain reactive and


dissolve rock material farther downstream.

355 a)


Transmissivit y Evolution

∆b [µm] 500+


100% Calcite




50 MPa

T/Torigina l

10 MPa

T/ Toriginal

10 10





Amherstburg Limestone


8 8

16 16

24 24

∆b [µm] 500+

32 32

Time [Hrs]

40 40

48 48

56 56

64 64

56 56

64 64

Time [Hrs] 15




50 MP a

10 MP a

T/To rigin al

T/ Toriginal

68% Calcite

10 10


55 100

0 0

Eagle Ford Shale



16 16

24 24

∆b [µm]

32 32

Time [Hrs]

40 40

48 48

Time [Hrs] 15




T/ Toriginal

34% Calcite



10 MPa



356 357 358 359 360 361 362 363

50 MPa





10 MPa



50 MPa






Time [Hrs]

Figure 3. Left: Aperture change maps (∆b) for reactive transport simulations after 36 hours with 10 MPa and 50 MPa stress: a) all-calcite, b) Amherstburg limestone and c) Eagle Ford shale. Right: Transmissivity evolution of the three mineralogies at 10 MPa and 50 MPa.

The dissolution patterns and transmissivity trajectories of the Eagle Ford shale simulations, however, are starkly different. For this rock, the reactive and nonreactive minerals

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are in a layered pattern corresponding to the sedimentary bedding layers of the shale. This


banded mineralogy is orthogonal to flow and inhibits channelization, which results in flow


“bottle-necks” along the layers of unreactive minerals (Figure 3c). Dissolution patterns of the


Eagle Ford shale simulations agree with images from previous reactive transport studies


examining layered rocks (12).

369 370

Comparing the transmissivity trajectories for the three mineralogies (Figure 3), the Eagle


Ford, which is the mineralogy with the least calcite content, has transmissivity trajectories that


are very different from the all-calcite and Amherstburg limestone simulations. Initially, the Eagle


Ford shale has the fastest transmissivity increase, reflecting the rapid front-propagation, due to


reduced acid neutralization, and sustained support caused by the large distributed amount of


unreactive area. This alone would suggest that transmissivity increase is inversely related to


reactive mineral content initially. Later in the simulations, however, the pattern of reactive


mineral controls the increase in transmissivity. The transmissivity of Eagle Ford stabilizes as the


unreactive layers remain and limit the transmissivity along the fracture plane.

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383 384 385 386 387 388

Figure 4. Left: Location of contact points for reactive transport under 50 MPa after 36 hrs. Right: Horizontally-averaged aperture change under 50 MPa (Red) and 10 MPa (Blue) of the a) allcalcite, b) Amherstburg Limestone, and c) Eagle Ford Shale. The initial asperity map at 50 MPa is provided in the Supporting Information.


4. Environmental Significance


This work is a novel contribution to subsurface engineering because it shows that certain


spatial patterns of less reactive minerals provide sustained flow bottlenecks and impede


channelization, even under flow regimes that promote channel formation in mineralogically


homogenous fractures. This study supports the idea that the spatial distribution of minerals, not

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just abundance, has a significant effect on the overall evolution of the fracture and its


transmissivity. The fastest transmissivity increase overall occurs in heterogeneous fractures that


have a contiguous pathway of reactive mineral in the direction of flow that allows for


channelization and reduced acid neutralization. This is consistent with findings by Deng et al.,


(39). Conversely, mineral heterogeneity can also result in barriers to transmissivity increase, as


was seen with bands of unreactive minerals perpendicular to flow, which act as sustained


bottlenecks to flow. This results in an entirely different transmissivity trajectory, one that


stabilizes rather than accelerating continuously.


This study also makes a significant contribution to understanding the interrelation


between mineral dissolution and geomechanical forces. Fracture transmissivity evolution in


homogeneous carbonate rocks is delayed by normal stress because when asperities dissolve,


fracture walls compress, and stress is redistributed to new contact points. For fractures in rocks


with heterogeneous mineralogy, fracture transmissivity is less affected by geomechanical forces


because the persistence of asperities composed of nonreactive minerals resists fracture


compression. An implication for future experimental and modeling studies is that ignoring


confining stress or artificially propping fractures open with epoxy would reduce or eliminate


geomechanical processes. Such conditions may lead to an overestimation of the enlargement in


aperture and transmissivity expected in subsurface fractures caused by the flow of reactive fluids.


Although not modeled in this study, another implication for future studies is that reaction-


induced decohesion of unreactive minerals (33) or fracture formation orthogonal to flow under


stress could further affect fracture closure and needs to be investigated in the context of coupled


geochemical-geomechanical processes.


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Beyond the laboratory scale, the retardation or acceleration of reactive fronts by


mineralogy or stress may have significant consequences for the timing of transmissivity increase


in larger scale fractures in subsurface engineered environments. As shown in the study,


channelization could lead to significant increases in transmissivity at short timescales. At the


field scale, the onset of transmissivity increase associated with the breakthrough of a channel


along the length of the fracture could take a long time. Furthermore, delay of channel


breakthrough caused by different normal stress conditions or rock compositions will be much


longer than the delays observed in this laboratory-scale study. Conversely, if injection of fluids


in the subsurface increases pore pressure and reduces the effective normal stress (13), this could


speed up channel breakthrough and result in earlier transmissivity increase. Questions remain as


to whether the nodular spatial pattern of unreactive minerals in the Amhersburg becomes


homogenously distributed at larger scales. As noted in Deng et al. (39), extending the lateral


width of the simulated fracture could result in the emergence of a continuous reactive mineral


pathway. However, upward fractures of larger length scales often penetrate multiple stratified


bands of lithologies, some of which may be relatively unreactive compared to carbonate-rich


layers (69). Identifying such bands of unreactive minerals and their lateral extent at specific sites


will be important to assess the risk of altering leakage pathways. This has significant


implications for the choice of caprock formations and should be included in carbon storage risk


assessments (70-71).

436 437

In summary, our work suggests that the spatial pattern of minerals is an equally important


evaluation criterion of caprock integrity in addition to the abundance of reactive minerals.


Although pure calcite limestone formations are assumed to be the most susceptible to

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transmissivity increase, our simulations show that mineralogically heterogeneous fractures with


contiguous calcite mineral pathways could result in faster transmissivity increases than for all-


calcite limestone fractures. Conversely, calcite-rich layered mineralogies with unreactive layers


act as flow barriers that stabilize transmissivity increase. Therefore, even calcite-rich caprocks


with bands of relatively less reactive minerals that are perpendicular to potential flow paths can


withstand chemical perturbations and may be reliable caprocks for geologic CO2 sequestration



447 448


449 450 451 452

Department of Energy under Grant DE-FE0023354 to Princeton University (via Penn State University). LJPN contributions were supported by the Center for Nanoscale Controls on Geologic CO₂ (NCGC), an Energy Frontier Research Center funded by the U.S. Department of Energy, Office of Science, Basic Energy Sciences under Award # DE-AC02-05CH1123.

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Supporting Information: X-ray fluorescence map of the Eagle Ford shale used for mineralogical map. Methodology and results of including pressure dissolution in model. Table of modeling parameters. Discussion of the importance of distinguishing permeability and transmissivity using results. Figure tracking the evolution of contact area for the all-calcite fracture simulation at the three normal stresses.

References: 1. Carroll, S.A., Keating, E., Mansoor, K., Dai, Z., Sun, Y., Trainor-Guitton, W., Brown, C., Bacon, D. Key factors for determining groundwater impacts due to leakage from geologic carbon sequestration reservoirs. Int. J. of Greenhouse Gas Control. 2014, 29, 153-168. 2. Clarens, A.F., Peters, C.A. Mitigating climate change at the carbon water nexus: A call to action for the environmental engineering community. Environ. Eng. Sci. 2012, 33(10), 719-724. 3. Deng, H., Bielicki, J.M., Oppenheimer, M., Fitts, J.P., Peters, C.A. Leakage risks of geologic CO2 storage and the impacts on the global energy system and climate change mitigation. Climatic Change. 2017, 144 (2), 151–163. 4. Bielicki, J.M., Peters, C.A., Fitts, J.P., Wilson, E.J. An Examination of Geologic Carbon Sequestration Policies in the Context of Leakage Potential. Int. J. of Greenhouse Gas Control. 2015, 37,61-75. 5. Nogues, J.P., Court, B., Dobossy, M., Nordbotten, J.M., Celia, M.A. Methodology to estimate maximum probable leakage along old wells in a geological sequestration operation. Int. J. of Greenhouse Gas Control. 2012, 7, pp. 39-47.

ACS Paragon Plus Environment


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Page 24 of 28

477 478 479 480 481 482 483 484 485 486 487 488 489 490 491 492 493 494 495 496 497 498 499 500 501 502 503 504 505 506

6. Shukla, R., Ranjith, P., Haque, A., Choi, X. A review of studies on CO2 sequestration and caprock integrity. Fuel. 2010, 89 (10), 2651-2664. 7. Benson, S.M., Cole, D.R. CO2 sequestration in deep sedimentary formations. Elements. 2008, 4 (5), 325-331. 8. Hawkes, C.D., Mclellan, P.J., Bachu, S. Geomechanical Factors Affecting Geological Storage of CO2 in Depleted Oil and Gas Reservoirs. J. Can. Petrol. Technol. 2005, 44 (10), 52-61. 9. Gaus, I. Role and impact of CO2-rock interactions during CO2 storage in sedimentary rocks. Int. J. Greenhouse Gas Control. 2010, 4 (1), 73-89. 10. Fitts, J.P., Peters, C.A. Caprock fracture dissolution and CO2 leakage. Rev. Mineralogy and Geochemistry. 2013, 77 (1), 459-479. 11. Soong Y., Crandall, D., Howard, B.H., Haljasmaa, I., Dalton, L.E., Zhang, L., Lin, R, Dilmore, R.M., Zhang, W., Shi, F., Mclendon, T.R. Permeability and Mineral Composition Evolution of Primary Seal and Reservoir Rocks in Geologic Carbon Storage Conditions. Envron. Eng. Sci. 2017, 35(5), 391-400. 12. Ellis, B., Peters, C., Fitts, J., Bromhal, G., McIntyre, D., Warzinski, R., Rosenbaum, E. Deterioration of a fractured carbonate caprock exposed to CO2-acidified brine flow. Greenhouse Gases: Sci. Tech. 2011, 1 (3), 248-260. 13. Rutqvist, J., Tsang, C.-F. A study of caprock hydromechanical changes associated with CO2 injection into a brine formation. Environ. Geol. 2002, 42 (2-3), 296-305. 14. Deng, H., Fitts, J.P., Crandall, D., McIntyre, D., Peters, C.A. Alterations of Fractures in Carbonate Rocks by CO2-Acidified Brines. Environ. Sci. and Technol. 2015, 49 (16), 10226-10234. 15. Detwiler, R.L., Rajaram, H. Predicting dissolution patterns in variable aperture fractures: Evaluation of an enhanced depth-averaged computational model. Water Resour. Res. 2007, 43 (4), W04403, 1-14. 16. Detwiler, R.L. Experimental observations of deformation caused by mineral dissolution in variable-aperture fractures. J. Geophys. Res: Solid Earth. 2008, 113 (8), 1-12. 17. Szymczak, P., Ladd, A.J.C. Wormhole formation in dissolving fractures. J. Geophys. Res: Solid Earth, 2009, 114 (6).

507 508 509 510 511 512 513 514 515 516 517 518 519 520 521 522

18. Garcia-Rios, M., Luquot, L., Soler, J.M., Cama, J. Influence of the flow rate on dissolution and precipitation features during percolation of CO2-rich sulfate solutions through fractured limestone samples. Chem. Geol. 2015, 414, 95-108. 19. Dávila, G., Luquot, L., Soler, J.M., Cama, J. Interaction between a fractured marl caprock and CO2-rich sulfate solution under supercritical CO2 conditions. Int. J. Greenhouse Gas Control. 2016, 48, 105-119. 20. Starchenko, V., Marra, C.J., Ladd, A.J.C. Three-dimensional simulations of fracture dissolution. J. Geophys. Res: Solid Earth. 2016, 121 (9), 6421-6444. 21. Elkhoury, J.E., Detwiler, R.L., Ameli, P. Can a fractured caprock self-heal? Earth Planet. Sci. Lett. 2015, 417, 99-106. 22. Menke, H. P., B. Bijeljic, and M. J. Blunt. Dynamic reservoir-condition microtomography of reactive transport in complex carbonates: Effect of initial pore structure and initial brine pH. Geochim. Cosmochim. Acta. 2017, 204, 267-285. 23. Upadhyay, V.K., Szymczak, P., Ladd, A.J.C. Initial conditions or emergence: What determines dissolution patterns in rough fractures? J. Geophys. Res: Solid Earth. 2015, 120 (9), 6102-6121.

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523 524 525 526 527 528 529 530 531 532 533 534 535 536 537 538 539 540 541 542 543 544 545 546 547 548 549 550 551 552 553 554 555 556 557 558 559 560 561 562 563 564 565 566

Environmental Science & Technology

24. Durham, W.B., Bourcier, W.L., Burton, E.A. Direct observation of reactive flow in a single fracture. Water Resour. Res. 2001, 37 (1), 1-12. 25. Polak, A., Elsworth, D., Liu, J., Grader, A.S. Spontaneous switching of permeability changes in a limestone fracture with net dissolution. Water Resour. Res. 2004, 40 (3), 110. 26. Luquot, L., Rodriguez, O., Gouze, P.Experimental Characterization of Porosity Structure and Transport Property Changes in Limestone Undergoing Different Dissolution Regimes. Trans. Porous Media. 2014, 101 (3), 507-532. 27. Menke, H. P., M. G. Andrew, M. J. Blunt, and B. Bijeljic. Reservoir condition imaging of reactive transport in heterogeneous carbonates using fast synchrotron tomography — Effect of initial pore structure and flow conditions. Chem. Geol. 2016, 428, 15-26. 28. O'Brien, G.S., Bean, C.J., McDermott, F. Numerical investigations of passive and reactive flow through generic single fractures with heterogeneous permeability. Earth Planet. Sci. Lett. 2003, 213 (3-4), 271-284. 29. Rajaram, H., Cheung, W., Chaudhuri, A. Natural Analogs for improved understanding of coupled processes in engineered earth systems: examples from karst system evolution. Curr. Sci. 2009, 97, 1162-1176. 30. Chaudhuri, A., Rajaram, H., Viswanathan, H. Alteration of fractures by precipitation and dissolution in gradient reaction environments: Computational results and stochastic analysis. Water Resour. Res. 2008, 44 (10), art. no. W10410, 1-19. 31. Noiriel, C., Madé, B., Gouze, P. Impact of coating development on the hydraulic and transport properties in argillaceous limestone fracture. Water Resour. Res. 2007, 43 (9). 32. Andreani, M., Gouze, P., Luquot, L., Jouanna, P. Changes in seal capacity of fractured claystone caprocks induced by dissolved and gaseous CO2 seepage. Geophys. Res. Lett. 2008, 35 (14). 33. Ellis, B.R., Fitts, J.P., Bromhal, G.S., McIntyre, D.L., Tappero, R., Peters, C.A. Dissolution-driven permeability reduction of a fractured carbonate caprock. Environ. Eng. Sci. 2013, 30 (4), 187-193. 34. Xu, Z., Li, Q., Sheets, J., Kneafsey, T.J., Cole, D., Jun, Y.-S., Pyrak-Nolte, L.J. Modification of fracture geometry by calcite precipitation. 50th US Rock Mech. Geomech. Symp. 2016, 3, 2477-2482. 35. Noiriel, C., Gouze, P., Madé, B. 3D analysis of geometry and flow changes in a limestone fracture during dissolution. J. Hydrol. 2013, 486, 211-223. 36. Deng, H., Ellis, B.R., Peters, C.A., Fitts, J.P., Crandall, D., Bromhal, G.S. Modifications of carbonate fracture hydrodynamic properties by CO2-acidified brine flow. Energy Fuels. 2013, 27 (8), 4221-4231. 37. Deng, H., Molins, S., Steefel, C., DePaolo, D., Voltolini, M., Yang, L., Ajo Franklin, J. A 2.5D Reactive Transport Model for Fracture Alteration Simulation. Env. Sci. Technol. 2016, 50 (14), 7564-7571. 38. Deng, H., Voltolini, M., Molins, S., Steefel, C., DePaolo, D., Ajo-Franklin, J., Yang, L. Alteration and Erosion of Rock Matrix Bordering a Carbonate-Rich Shale Fracture. Environ. Sci. and Technol. 2017, 51 (15), 8861-8868. 39. Deng, H., Peters, C.A. Reactive Transport Simulation of Fracture Channelization and Transmissivity Evolution. Env. Eng. Sci. 2018, 36(1), DOI:10.1089/ees.2018.0244.

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567 568 569 570 571 572 573 574 575 576 577 578 579 580 581 582 583 584 585 586 587 588 589 590 591 592 593 594 595 596 597 598 599 600 601 602 603 604 605 606

40. Hao, Y., M. Smith, Y. Sholokhova, and S. Carroll. CO2-induced dissolution of low permeability carbonates. Part II: Numerical modeling of experiments. Adv. Water Resour. 2013, 62, 388-408. 41. Ellis, B.R., Peters, C.A. 3D Mapping of calcite and a demonstration of its relevance to permeability evolution in reactive fractures. Adv. Water Resour. 2016, 95, 246-253. 42. Wen, H., Li, L., Crandall, D., Hakala, A. Where Lower Calcite Abundance Creates More Alteration: Enhanced Rock Matrix Diffusivity Induced by Preferential Dissolution. Ene. Fuels. 2016, 30 (5), 4197-4208. 43. Nogues, J.P., Fitts, J.P., Celia, M.A., Peters, C.A. Permeability evolution due to dissolution and precipitation of carbonates using reactive transport modeling in pore networks., Water Resour. Res. 2013, 49(6): 6006-6021. 44. Chen, L., Kang, Q., Viswanathan, H. S., Tao, W. Pore-scale study of dissolution-induced changes in hydrologic properties of rocks with binary minerals. Water Resour. Res. 2014, 50, 9343-9365. 45. Smith, M.M., Hao, Y., Carroll, S.A. Development and calibration of a reactive transport model for carbonate reservoir porosity and permeability changes based on CO2 coreflood experiments. Int. J. Greenhouse Gas Control. 2017, 57, 73-88. 46. Smith, M.M., Sholokhova, Y., Hao, Y., Carroll, S.A. Evaporite caprock integrity: An experimental study of reactive mineralogy and pore-scale heterogeneity during brine-CO2 exposure. Environ. Sci. and Technol. 2013, 47 (1), 262-268. 47. Polak, A., Elsworth, D., Yasuhara, H., Grader, A.S., Halleck, P.M. Permeability reduction of a natural fracture under net dissolution by hydrothermal fluids. Geophys. Res. Lett. 2003, 30 (20), 1-4. 48. Yasuhara, H., Elsworth, D., Polak, A. A mechanistic model for compaction of granular aggregates moderated by pressure solution. J. Geophys. Res: Solid Earth. 2003, 108 (11), ECV 1-1 - ECV 1-13. 49. Yasuhara, H., Elsworth, D. Compaction of a rock fracture moderated by competing roles of stress corrosion and pressure solution. Pure Appl. Geophys. 2008, 165 (7), 1289-1306. 50. Taron, J., Elsworth, D. Thermal-hydrologic-mechanical-chemical processes in the evolution of engineered geothermal reservoirs. Int. J. Rock Mech. and Min. Sci. 2009, 46 (5), 855-864. 51. Ishibashi, T., McGuire, T.P., Watanabe, N., Tsuchiya, N., Elsworth, D. Permeability evolution in carbonate fractures: Competing roles of confining stress and fluid pH. Water Resour. Res. 2013, 49 (5), 2828-2842. 52. Ameli, P., Elkhoury, J.E., Morris, J.P., Detwiler, R.L. Fracture permeability alteration due to chemical and mechanical processes: A coupled high-resolution model. Rock Mech. Rock Eng. 2014, 47 (5), 1563-1573. 53. Elkhoury, J.E., Ameli, P., Detwiler, R.L. Dissolution and deformation in fractured carbonates caused by flow of CO2-rich brine under reservoir conditions. Int. J. Greenhouse Gas Control, 2013, 16, S203-S215.

607 608 609 610 611

54. Pyrak-Nolte, L.J., Morris, J.P. Single fractures under normal stress: The relation between fracture specific stiffness and fluid flow. Int. J. Rock Mech. and Min. Sci. 2000, 37 (1-2), 245-262. 55. Petrovitch, C. L., Pyrak-Nolte, L. J., and D. D. Nolte, Combined Scaling of Fluid Flow and Seismic Stiffness in Single Fractures (2014) Rock Mechanics and Rock Engineering.

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612 613 614 615 616 617 618 619 620 621 622 623 624 625 626 627 628 629 630 631 632 633 634 635 636 637 638 639 640 641 642 643 644 645 646 647 648 649 650 651 652 653 654 655 656 657

Environmental Science & Technology

56. Yasuhara, H., Elsworth, D. Compaction of a rock fracture moderated by competing roles of stress corrosion and pressure solution. Pure Appl. Geophys. 2008, 165 (7), 1289-1306. 57. Taron, J., Elsworth, D.Constraints on compaction rate and equilibrium in the pressure solution creep of quartz aggregates and fractures: Controls of aqueous concentration. J. Geophys. Res: Solid Earth. 2010, 115 (7), 1-17. 58. Palandri, J.L., Kharaka, Y.K. A Compilation of Rate Parameters of Water-Mineral Interaction Kinetics for Application to Geochemical Modeling. U.S. Geological Survey Open File Report (OF 2004-1068). 2004, U.S. Geological Survey, Menlo Park, CA 59. Wang, H., Bernabé, Y., Mok, U., Evans, B. Localized reactive flow in carbonate rocks: Core-flood experiments and network simulations. J. Geophys. Res: Solid Earth. 2016, 121 (11), 7965-7983. 60. Dahan, O., Nativ, R., Adar., E., Berkowitz, B., Ronen, Z. Field observations of flow in a fracture intersecting unsaturated chalk. Water Resour. Res. 1999, 35, 3315-3326. 61. Helgeson, H.C., Knox, A.M., Owens, C.E., Shock, E.L. Petroleum, oil field waters, and authigenic mineral assemblages: are they in metastable equilibrium in hydrocarbon reservoirs? Geochim. Cosmochim. Ac. 1993, 57, 3295–3339. 62. Deng, H.; Fitts, J.P.; Peters, C.A. Quantifying Fracture Geometry with X-ray Tomography: Technique of Iterative Local Thresholding (TILT) for 3D Image Segmentation. Comp. Geosci. 2016, 20, 231–244. 63. Szymczak, P., Ladd, A.J.C. The Initial Stages of Cave Formation: Beyong the onedimensional paradigm. Earth Planet. Sci. Lett., 2011, 301. 424-432. 64. Li, L., Peters, C.A., Celia, M.A. Upscaling geochemical reaction rates using pore-scale network modeling. Adv. Water Res., 2006, 29 (9), 1351-1370. 65. James, S.C., Chrysikopuulos, C.V. Transport of polydisperse colloids in a saturated fracture with spatially variable aperture. Water Resour. Res. 2000, 36 (6), 1457-1465. 66. Zimmerman, R.W., Bodvarsson, G.S. Hydraulic conductivity of rock fractures. Trans. Porous Media. 1996, 23 (1), 1-30. 67. Elston, H.W. Mineralogical and Geochemical Assessment of the Eagle Ford Shale. Senior Thesis, 2014, Ohio State University. 68. Fitts, J.P., Ellis, B.R., Deng, H., Peters, C.A. Geochemical controls on fracture evolution in carbon sequestration. 46th US Rock Mech. Geomech. Symp. 2012, 3, 2243-2248. 69. USGS. National Assessment of Geologic Carbon Dioxide Storage Resources—Data. 2013, United States Geological Survey. 70. Pawar, R.J., Bromhal, G.S., Carey, J.W., Foxall, W., Korre, A., Ringrose, P.S., Tucker, O., Watson, M.N., White, J.A. Recent advances in risk assessment and risk management of geologic CO2 storage. Int. J. Greenhouse Gas Control, 2015, 40, 292-311. 71. Pawar, R.J., Bromhal, G.S., Chu, S., Dilmore, R.M., Oldenburg, C.M., Stauffer, P.H., Zhang, Y., Guthrie, G.D. The National Risk Assessment Partnership's integrated assessment model for carbon storage: A tool to support decision making amidst uncertainty. Int. J. of Greenhouse Gas Control. 2016, 52, 175-189.

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For Table of Contents only: Fracture Aperture Evolution

Transmissivit y Evolution

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