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Pore-scale Simulation of Reactive Transport in Micro-CT Images João Paulo Pereira Nunes Supervisors: Martin J. Blunt Branko Bijeljic Pore-scale consortium.

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Presentation on theme: "Pore-scale Simulation of Reactive Transport in Micro-CT Images João Paulo Pereira Nunes Supervisors: Martin J. Blunt Branko Bijeljic Pore-scale consortium."— Presentation transcript:

1 Pore-scale Simulation of Reactive Transport in Micro-CT Images João Paulo Pereira Nunes Supervisors: Martin J. Blunt Branko Bijeljic Pore-scale consortium meeting, January 2015

2 Objective Develop a pore-scale particle tracking method capable of simulating rock-fluid reactions in carbonates – Predict how petrophysical properties evolve during reactive transport Applications - CO2 injection (EOR or sequestration) and diagenesis modeling

3 Introduction Already established that acidic fluids flowing through carbonates react with the rock matrix, changing petrophysical and elastic properties of the reservoir Pore-scale is the natural scale to study rock-fluid interactions (and then upscale) This work – Lagrangian approach based on a pore-scale streamline method to simulate evolution of petrophysical properties at in situ conditions Quantify the impact of flow heterogeneity on average reaction rates Validate the model using 3D dynamic imaging data from a real carbonate

4 Reactive transport in four steps 1.Particle Advection – Modified Pollock Algorithm 2.Diffusion – Random Walk 3.Reaction – Flux of particles through solid interface 4.Velocity Field update – Finite volume with OpenFoam All simulations directly on segmented micro-CT images

5 ∆X diff ∆X adv ∆X diff ∆X adv

6 Data input: Image loading & velocity Particle advection using streamlines Particle diffusion: random walk Velocity Field Update: OpenFoam Particle hit solid ? Then reaction. Flow weighted particle injection Particle loop Calculate statistics, reaction rate etc. Time loop > ε ? yes Update statistics Model setup no Algorithm

7 Pore-scale streamline tracing

8 We improve Pollock’s algorithm, to trace streamlines semi-analytically, respecting the no-slip boundary conditions at pore- solid walls No need to make the time-step small. More efficient than std. particle tracking methods. Very useful in high Pe flows. In a cubic lattice there are 64 possible types of pores: -1 – no solid boundaries -6 – one solid boundary -15 – two solids -20 – three solids -15 – four solids -6 – five solids -1 – six solids w1w1 u2u2 v2v2 y z x w2w2 A pore with two solid boundaries: Modified Pollock for Streamline tracing at the pore-scale

9 y z x w1w1 w2w2 u2u2 v1v1 v2v2 Example: Pore with one solid boundary Calculate exit times and minimize

10 Standard and modified Pollock have very different outcomes. The standard Pollock fails to capture the non-Fickian behavior expected in heterogeneous rocks. Voxel Time-of-flight distributionsBreakthrough New method captures the complexity of flow in heterogeneous rocks Late arrival

11 Streamlines in the Ketton carbonate FLOW 3.5mm

12 Carbonate dissolution

13 Calcite Dissolution Three reactions occurring in parallel at the grain surface: With intrinsic rate - k = mol*m -2 *s 10MPa & 50C (Peng et al., 2014)

14 Reaction rate in the particle approach k – intrinsic reaction rate  Taken from independent experiments Dm – diffusion coefficient ∆t – time step C(r) – particle concentration Nmol – moles of calcite in each solid voxel A solid voxel dissolves when the cumulative flux of particles is > N hits

15 Dynamic imaging experiment – Menke et al Ketton oolite core flooded with CO2-equilibrated 10MPa / 50C -Porosity and permeability increasing -Péclet ≈ 2300 Damköhler ≈ Transport controlled reaction – dissolution limited to regions of significant intake of solute t

16 Workflow

17 Slice-averaged porosity Flow t0 50min. Experimental x Simulation

18 Porosity and permeability after flow and reaction Very good agreement between simulation and experiment.

19 Time-lapse images- perpendicular to flow

20 Time-lapse images – parallel to flow

21 More dissolution in regions of higher flux Essentially no dissolution in stagnant regions Magnitude of the flow field perpendicular to flow direction Dissolution in black Stagnant regions in white (not shown)

22 Average dissolution rates Time (min.) ∆ϕ∆ϕ k eff [10 -4 mol.m -2.s -1 ] ∆ϕ∆ϕ k eff [10 -4 mol.m -2.s -1 ] Experimental Simulation Compare with the batch rate: k = mol.m -2.s -1 (Peng et al., 2014) Average rates 10 times smaller due to transport limitations – no chemical/surface heterogeneity in the model.

23 Conclusions We have presented a particle tracking method to simulate carbonate dissolution at the pore-scale The method was validated using dynamic image data – carbonate dissolution in CO2-rich brine - without any fitting parameters Based on a very efficient streamline tracing method – Modified Pollock algorithm We predict a decrease of one order of magnitude in the average dissolution rates due to transport limitations only Easily modifiable to incorporate deposition and different flow regimes

24 Next steps: Impact of the flow rate on the average reaction rates - How to define the average rates for face dissolution ? -Run simulations on more complex rocks -Does the transition from face to uniform dissolution depends on the degree of heterogeneity? -Study different reaction rates  PeDa changing

25 Flow rate vs. dissolution extension Pe 1000 Pe 100 Inlet Outlet Pe 10 Pe 1 PeDa = 10 -2

26 Particle trajectories in the pore space Particles travel longer distances when the Pe number is higher, thus moving the dissolution front away from the inlet face

27 Pe 1 Pe 100 Pe 1000 Pe 10 Inlet Outlet

28 Estaillades Slow flow  Péclet =1 1.3 mm 0.67 mm Small Pe regime only “face dissolution” - Whole grains are being dissolved No significant impact in permeability.

29 Estaillades Péclet = mm 0.67 mm

30 Estaillades High velocity flow (Péclet 280)  Uniform dissolution

31 Acknowledgments Hannah Menke for sharing her experimental results Ali Raeini for providing the flow solver Petrobras for sponsoring this project

32 END


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