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,

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Transcript 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,

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...
Saltwater Intrusion
Fresh water
Salt water
Formation of toe
Fresh water
Salt water
Saltwater Upconing
Fresh water

1

 40
Salt water
Example: Salt Water Upconing on Wei Zhou Island
Thesis Li Guomin
Freshwater Lens
Upconing
Alternative Extraction Strategies
Salinity backflow from Chotts in Tunisia
Oasis
Salt fingers on islands in the Okavango Delta
200 km
Islands and salt crusts in Delta
Schematic cross section of an island
Transpiration
Trona saltcrust
Evaporation
gravity vs.
upward flow
Instability on the Islands
WoodingNumber 
k f 
uET 
kf= 10-5 m/s, uET=10-8 m/s
Critical Wooding Number:
TEM Evaluation
20
Island-Transect
18
Critical Wooding Number
16
instable
14
12
10
8
6
stable
4
2
0
0
0.2
0.4
0.6
0.8
1
1.2
k in units of u/D m
-1
1.4
1.6
1.8
2
TDS center
(mg/l)
TDS layer 2 norm. density Wooding
(mg/l)
contrast (-)
No.(-)
Thata-1
22425.00
1352.94
0.0147
14.74
Thata-3
Mosupatsela-1
9425.00
8645.00
878.59
1495.31
0.0060
0.0050
5.98
5.00
Mosupatsela-3
5200.00
1803.28
0.0024
2.37
Tshwene-1
Tshwene-2
19110.00
19110.00
1135.50
1135.50
0.0126
0.0126
12.57
12.57
Lebolobolo-1
Lebolobolo-2
13000.00
26000.00
1014.03
1887.59
0.0084
0.0169
8.38
16.86
Lebolobolo-3
Monyopi-1
7800.00
2665.00
886.25
1118.03
0.0048
0.0011
4.84
1.08
Monyopi-2
2665.00
747.22
0.0013
1.34
Atoll-3
Kwena-1
15600.00
9750.00
2172.15
1480.68
0.0094
0.0058
9.39
5.78
Montsana-1
1625.00
367.65
0.0009
0.88
Simulation of fingering
20
40
60
80
100
20
t=900
t=6000
t=8500
t=16800
t=32500
dddd
t=66000
t=46500
t=2900
t=12400
t=25000
40
60
80
100
100
cmax=350
=235
=11 mg/l
=54
=75
ccmax
=350
mg/l
=110
=30
max
Flow in the vicinity of a salt dome
Recharge
Discharge
Salt water fresh water
interface
Top of salt dome
No density difference
With density difference
Basic Equations
expressed in mass fraction c and pressure p
•
•
•
Darcy law
•
Dispersion tensor
•
•

 (n)
   (v)  (c q )s vol
t
Mass balance
total mass
Mass balance
salt

 (nc)
   ( cv  n( D  Dm )c)  cq  (cq ) svol
t


K
v   (p  g)

Dij 
Constitutive relationships
Boundary conditions
(many combinations)
1
v
a
vv
ijkl k l
k ,l
   (c, p)
   (c, p)
e.g.

c  1
c 1

 1 

  cmax   f cmax  s
1
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 advectivedispersive transport
Flow in porous media and rotation
Darcy-flow in heterogeneous porous media is rotational
Example:

v
kf
But we still have:

v  k f h

v  0

  (v / k f )  0
In density flow, rotation is non-trivial: closed streamlines


k
v   (p  g)

 k


k
For constant k/   v  (  (p)  ( )  g )   ( )  g


Rotational when  not parallel to g

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 using
unstructured grids, finite volume discretization, multigrid solver,
error estimator, automatic local refinement/coarsening, parallel
computing
Idea of „exact“ solution
(steady state)
Pressure equation
L1 ( p( x, z), c( x, z)  0
Salt mass fraction equation
L2 (c( x, z), p( x, z))  0
Assume any differentiable functions p(x,z), c(x,z)
Assume any domain
Assign function values as first kind boundary conditions
on boundary of that domain
Plug functions into flow equations
Pressure
L1 ( p( x, z), c( x, z))  f ( x, z)
Salt mass fraction
L2 (c( x, z), p( x, z))  g ( x, z)
Right-hand sides are not zero:
They are interpreted as source-sink terms
So 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
p(x, z)  (1  z)(g0   z z  z 0 )   x ((3  x s )  (x  x s )z)
Salt mass fraction

2z
2
2 

 4.5  2  ( x  3  z)  ( x  z) 
x

h

c( x , z )  1   e  







2
1
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=-0.1
In PDE: n=1, g=1, k=10, =1, Dm=1, /c=0.1, (c)=0+ /c c=1+0.1c
Analytical
Pressure
Salt mass fraction
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. input
Turquoise: 0 input
Red: max. input
Light blue: 0 input
Blue: output
Computed (with 4 grid levels)
Pressure
Salt mass fraction
Values between 0 and 1.13 p units
Values between 0 and 1 c units
Error
Pressure
Red : computed value too large by 0.004 %
Blue: computed value too small by 0.005 %
Salt mass fraction
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
Experimental setup continued
20 cm
20 cm
unstable situation
stable situation
Salt water
Stable situation: Low concentration contrast
NMR images of diagonal section: stable
situation at low concentration contrast
Injection
Flushing
Equilibration
End
NMR images of diagonal section: stabel
situation at high concentration contrast
Injection
Equilibration
„Entraining“
End
Two modes
No density contrast
Large density contrast
Experimental breakthrough curves
Low contrast
High contrast
Comparison of computed and measured
breakthrough curves
Low contrast
High contrast
Choice of parameters within intervals given through measurements of those
Comparison of concentrations along diagonal section
Low contrast case, end of experiment
Comparison of concentrations along diagonal section
High contrast case, end of experiment
Grid convergence: Low contrast case
c1i , j 1  c1i , j , c1i 1, j  c1i , j
2
2
unit 10-2
Level # grid points
0
8
1
27
2
125
3
729
4
4,913
5
35,937
6
274,625
7
2,146,689
x at level 7: 1.56 mm
Grid convergence: Low contrast case
Grid convergence: High contrast case
c2i , j 1  c2i , j , c2i 1, j  c2i , j
2
unit 10-2
Level
0
1
2
3
4
5
6
7
8
# grid points
8
27
125
729
4,913
35,937
274,625
2,146,689
16,974,593
x at level 8: 0.78 mm
Grid convergence: High contrast case
Error of grid-convergent solutions
Low contrast
High contrast
Unstable case: NMRI data
NMRI of vertical and horizontal section:
fingering experiment
Vertical section
Horizontal section
Fingering: Experiment vs. Computation
Finger velocity: comparison of experiment
and computation
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/s
Boundary 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 autocorrelation
Arithmetic mean 1.68E-9 m2, Geometric mean 1.02E-9 m2
Variance of log(k) = 1
Corr. lengths: horizontal 0.05 m, vertical 0.05 m
Red: 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 0.1
Eff. diffusion coefficient as in homogeneous case
Question: Are there equivalent effective parameters to mimick
main effect of heterogeneity in a homogeneous model?
Heterogeneous Henry Problem
Comparison (zero local dispersion)
Heterogeneous case
Only diffusion
Homogeneous case:
Permeability equal arithmetic
mean of heterogeneous case
Only diffusion
Homogeneous case:
Permeability equal geometric
mean of heterogeneous case
Only diffusion
Heterogeneous Henry Problem
Comparison (zero local dispersion)
Heterogeneous case
only diffusion
Homogeneous case:
Permeability equal geometric mean
of heterogeneous case
only diffusion, zero dispersion
Homogeneous case:
Permeability equal geometric mean of
heterogeneous case, diffusion plus
macrodispersion after Gelhar&Axness
Heterogeneous Henry Problem
Comparison (with local dispersion)
Heterogeneous case
Diffusion + local dispersion
Homogeneous case:
Permeability geometric mean
Diffusion + local dispersion
Homogeneous case:
Permeability geometric mean
Diffusion + 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/aL)
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