Density driven flow in porous media: How accurate are our models?
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Transcript of Density driven flow in porous media: How accurate are our models?
Density driven flow in porous media: How accurate are our models?
Wolfgang Kinzelbach
Institute for Hydromechanics and Water Resources Engineering
Swiss Federal Institute of Technology, Zurich, Switzerland
Contents
• Examples of density driven flow in aquifers• Equations
– Formulation– Special features of density driven flows
• Benchmarks– Analytical and exact solutions– Experimental benchmark: Grid convergence– Experimental benchmark: Fingering problem
• Upscaling issues• Conclusions
Density driven flows in groundwater resources management
• Sea water intrusion• Salt water upconing under freshwater lenses
(both on islands and inland)• Salt water fingering under playa lakes and saltpans• Flow around salt domes (nuclear waste repositories)• Brine injection• Leachate from waste deposits• Even the ordinary tracer experiment...
Schematic cross section of an island
Transpiration
Evaporation
Increasing salinity of GW
Trona saltcrust
Increasing salinity of GW
gravity vs. upward flow
Instability on the Islands
ET
f
u
k Number Wooding
Critical Wooding Number:TEM Evaluation
Island-TransectTDS center
(mg/l)TDS layer 2
(mg/l)norm. density
contrast (-)Wooding
No.(-)Thata-1 22425.00 1352.94 0.0147 14.74
Thata-3 9425.00 878.59 0.0060 5.98
Mosupatsela-1 8645.00 1495.31 0.0050 5.00
Mosupatsela-3 5200.00 1803.28 0.0024 2.37
Tshwene-1 19110.00 1135.50 0.0126 12.57
Tshwene-2 19110.00 1135.50 0.0126 12.57
Lebolobolo-1 13000.00 1014.03 0.0084 8.38
Lebolobolo-2 26000.00 1887.59 0.0169 16.86
Lebolobolo-3 7800.00 886.25 0.0048 4.84
Monyopi-1 2665.00 1118.03 0.0011 1.08
Monyopi-2 2665.00 747.22 0.0013 1.34
Atoll-3 15600.00 2172.15 0.0094 9.39
Kwena-1 9750.00 1480.68 0.0058 5.78
Montsana-1 1625.00 367.65 0.0009 0.88
kf= 10-5 m/s, uET=10-8 m/s
0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6 1.8 20
2
4
6
8
10
12
14
16
18
20
k in units of u/D m-1
Criti
cal W
oodi
ng N
umbe
r
instable
stable
Simulation of fingering
20 40 60 80 100
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t=900 d cmax=11 mg/l
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t=2900 d cmax=30 mg/l
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10020 40 60 80 100
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t=6000 d cmax=54 mg/l
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t=8500 d cmax=75 mg/l
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t=12400 d cmax=110 mg/l
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t=16800 d cmax=235 mg/l
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t=25000 d cmax=350 mg/l
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t=32500 d cmax=350 mg/l
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t=46500 d cmax=350 mg/l
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t=66000 d cmax=350 mg/l
Flow in the vicinity of a salt dome
Recharge Discharge
Top of salt dome
Salt water -fresh waterinterface
No density difference With density difference
• Mass balance total mass
• Mass balance salt
• Darcy law
• Dispersion tensor
• Constitutive relationships
• Boundary conditions (many combinations)
Basic Equationsexpressed in mass fraction c and pressure p
volq s)c()v(t
)n(
volqqm scccDDnvccn
)())((t
)(
)gp(K
v
lk
lkijklij vvav
D,
1
),(),( pcpc
sf c
c
c
c
11
11
maxmax
e.g.
Possible simplification: Boussinesq approximation
Features of density driven flow
-Non-linearity
-Consistency problem of boundary conditions
-Rotational flow with closed streamlines
-Plus all difficulties known from advective- dispersive transport
Flow in porous media and rotation
Darcy-flow in heterogeneous porous media is rotationalExample:
)gp(k
v
gk
gpk
v
)())()((
But we still have:
In density flow, rotation is non-trivial: closed streamlines
Rotational when not parallel to g
0)k/v( f
For constant k/
kfv hkv f
0 v
Numerical solution and testing of codes
• Analytical solutions• Exact solutions• Inter-code comparison• Experimental benchmarks• Grid convergence
All computations are made with d3f, a density flow model usingunstructured grids, finite volume discretization, multigrid solver, error estimator, automatic local refinement/coarsening, parallel computing
Idea of „exact“ solution(steady state)
Pressure equation
Salt mass fraction equation
0),(),,((1 zxczxpL
0)),(),,((2 zxpzxcL
Assume any differentiable functions p(x,z), c(x,z)Assume any domainAssign function values as first kind boundary conditionson boundary of that domain
Plug functions into flow equations
Pressure
Salt mass fraction
),()),(),,((1 zxfzxczxpL
),()),(),,((2 zxgzxpzxcL Right-hand sides are not zero: They are interpreted as source-sink termsSo analytical expressions are exact solution for problem with - these source-sink terms and - first kind boundary conditions with given function values
Only good if source-sink terms are small and do not dominate the problem
Analytical expressions for „exact“ solution(steady state)
Pressure
Salt mass fraction
)z)xx()x3(()zzg)(z1()z,x(p ssx0z0
1
222
2
x )zx()z3x(hz2
5.4e1)z,x(c
Values in example tuned to make sources/sinks small: =20, =12, h=.14, =1, 0=1, =1, x=0.1, z=0.02, xs=1, zs=-0.1In PDE: n=1, g=1, k=10, =1, Dm=1, /c=0.1, (c)=0+ /c c=1+0.1c
Analytical
Salt mass fraction
Pressure
Values between 0 and 1.13 p units
Values between 0 and 1 c units
Plugged into equations for c and p
Source-sink distributions
Total mass
Salt mass
Red: max. inputTurquoise: 0 input
Red: max. inputLight blue: 0 inputBlue: output
Computed (with 4 grid levels)
Salt mass fraction
Pressure
Values between 0 and 1.13 p units
Values between 0 and 1 c units
Error
Pressure
Salt mass fraction
Red : computed value too large by 0.004 % Blue: computed value too small by 0.005 %
Red : computed value too large by 0.007 %Blue: computed value too small by 0.006 %
Experimental benchmark
• 3D transient experiment in box with simple boundary and initial conditions
• Measurement of concentration distribution in 3D with Nuclear Magnetic Resonance Imaging
• Measurement of breakthrough curves
Drawback: Test of both model equations and mathematics
Way out: Construction of a grid convergent solution inspired by the physical experiments
Experimental setup
• Cube filled with glass beads of diameter 0.7 mm• Size of model 20*20*20 cm3
• Injection of dense fluid on bottom center hole• Application of base flow via top corner holes• In unstable case: Injection from below and rotation• All parameters measured except transverse dispersivity,
diffusion coefficient
NMR images of diagonal section: stable situation at low concentration contrast
Injection
EndFlushing
Equilibration
NMR images of diagonal section: stabel situation at high concentration contrast
Injection Equilibration
„Entraining“ End
Comparison of computed and measured breakthrough curves
Low contrast
High contrast
Choice of parameters within intervals given through measurements of those
Level # grid points 0 8 1 27 2 125 3 729 4 4,913 5 35,937 6 274,625 7 2,146,689
Grid convergence: Low contrast case
unit 10-2
2
,1
,11
2
,1
1,1 , jijijiji cccc
x at level 7: 1.56 mm
Level # grid points 0 8 1 27 2 125 3 729 4 4,913 5 35,937 6 274,625 7 2,146,689 8 16,974,593
Grid convergence: High contrast case
unit 10-2
jijijiji cccc ,2
,12
2
,2
1,2 ,
x at level 8: 0.78 mm
Causes for poor perfomance
• Numerical dispersion smoothes out fingers and eliminates driving force
• Initial perturbance not known well enough• Start of fingers on microlevel, not
represented by continuum equations
Influence of heterogeneity on density flow
• Homogeneous Henry problem
• Heterogeneous Henry problem
Definition of Henry problem: Homogeneous aquifer
Hydraulic conductivity 1E-2 m/s, effective diffusion coefficient 1.886E-05 m2/sBoundary conditions: Left fresh water flux given at 6.6E-05 m/s
Right hydrostatic salt water, salt mass fraction 0.0357 kg/kg
Solution of Henry problem: Homogeneous aquifer
Relative concentration contours between 0 (left) and 1 (right) in steps of 0.1
Heterogeneous Henry problem: Permeability distribution
Lognormal distribution, exponential autocorrelationArithmetic mean 1.68E-9 m2, Geometric mean 1.02E-9 m2 Variance of log(k) = 1Corr. lengths: horizontal 0.05 m, vertical 0.05 mRed: 3.5E-08 m2, Blue: 2.6E-11 m2
Heterogeneous Henry Problem:Concentration distribution
Relative concentration contours between 0 (left) and 1 (right) in steps of 0.1Eff. diffusion coefficient as in homogeneous case
Question: Are there equivalent effective parameters to mimickmain effect of heterogeneity in a homogeneous model?
Heterogeneous Henry ProblemComparison (zero local dispersion)
Heterogeneous caseOnly diffusion
Homogeneous case:Permeability equal arithmetic mean of heterogeneous caseOnly diffusion
Homogeneous case:Permeability equal geometric mean of heterogeneous caseOnly diffusion
Heterogeneous Henry ProblemComparison (zero local dispersion)
Heterogeneous caseonly diffusion
Homogeneous case:Permeability equal geometric mean of heterogeneous caseonly diffusion, zero dispersion
Homogeneous case:Permeability equal geometric mean of heterogeneous case, diffusion plus macrodispersion after Gelhar&Axness
Heterogeneous Henry ProblemComparison (with local dispersion)
Heterogeneous caseDiffusion + local dispersion
Homogeneous case:Permeability geometric mean Diffusion + local dispersion
Homogeneous case:Permeability geometric meanDiffusion + macrodispersion after Gelhar&Axness
Effective dispersion parameters- Stable situation with flow against direction of density gradient effective longitudinal dispersivity given by Gelhar & Welty, A11(with density gradient) < A11(without density gradient)
- Unstable situation with flow in direction of density gradient at sufficiently large Wooding/Raleigh number, dispersivities grow to infinity due to fingers forming
- Horizontal flow towards a fixed concentration leads to „boundary layer“. Dispersion at upper right boundary and at stagnation point is „upstream diffusion“: c/c0 = 1 – exp (-x/L)
Upstream diffusion
Conclusions
• Density flow of increasing importance in groundwater field
• Tests for reliability of codes are available• Density flow especially with high contrast
numerically demanding: Grid convergence may require millions of nodes
• Numerical simulation of fingering instabilities still inadequate
• Heterogeneities can be handled by effective media approach in situation without fingering
• New numerical methods are in the pipeline