prediction of contaminant plumes (shapes, spatial moments and macro-dispersion) in aquifers with...

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A.M.M. Elfeki Section Hydrology and Ecology, Dept. of Water Management, Environmental and Sanitary Engineering, TU Delft, P.O. Box 5048, 2600 GA Delft, The Netherlands. Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

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Page 1: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

A.M.M. Elfeki Section Hydrology and Ecology, Dept. of Water

Management, Environmental and Sanitary Engineering, TU Delft, P.O. Box 5048, 2600 GA Delft,

The Netherlands.

Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-

dispersion) in Aquifers with Insufficient Geological Information

Page 2: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Outline

• Markov Chain in One-dimension.• Markov Chain in Multi-dimension:

Coupled Markov Chain (CMC) Model. • Application of CMC to Characterize heterogeneity at

the MADE1 site:- Parameter Estimation.- Sensitivity Analysis.

• Hydrogeological conditions at MADE1.• Model Assumptions.• Simulation Results.• Conclusions.

Page 3: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

One-dimensional Markov Chain

w p kN

lkN

)(lim

,:)Pr()Pr(

p S Z | S ZS Z ,..., S Z ,S Z ,S Z | S Z

lkl1-iki

p0r3-in2-il1-iki

)(Pr 1 qNliki S Z ,S Z | S Z

)1(

)(

1 )(Pr

iNlq

lkiN

kqqNliki p

pp S Z ,S Z | S Z

S So d

Page 4: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Coupled Markov Chain “CMC” in 2D

Dark Grey (Boundary Cells)Light Grey (Previously Generated Cells)W hite (Unknown Cells)

i-1 ,j i,ji,j-1

1 ,1

N x ,N y

N x ,1

1 ,N y

N x ,j

nkp . p

p . p SZSZSZ p

f

vmf

hlf

vmk

hlk

mjiljikjiklm ,...1.),|Pr(: 1,,1,,

.,...1,

),,|Pr(:

)(

)(

,1,,1,,

nkp . p . p

p .p . p

SZSZSZSZp

f

vmf

iNhfq

hlf

vmk

iNhkq

hlk

qjNmjiljikjiqklm

x

x

x

Page 5: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Procedure for Extracting a Final Geological Image

 

.0

1)(

otherwise

SZifZI

kij

ijk

MC

R

Rk

kR

kij ji

ji ZIMCMC

SZ

1

)()(

,

, 1}{#

}...,,max{ 21 nijijij

lij

Let the realizations be numbered 1,…, MC, and let Zij (R) be the

lithology of cell (i,j) in the Rth realization. The empirical relative frequency of lithology Sk at cell (i,j) is:

In the final image Z* the lithology at cell (i, j) will be the lithology which occurs most frequently in the MC realizations. So, if Sl is such that

Zij*= Sl.

Page 6: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

MADE Site Data

0 50 100 150 200 250

-10

-5

0

0

1

2

3

4

5

Page 7: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Estimation of Vertical Transition Probability

0 50 100 150 200 250

-10

-5

0

0

1

2

3

4

5

S. 1 2 3 4 5 6 7

1 .879

.103

.009

.000

.009

.000

.000

2 .026

.911 .046

.009

.003

.000

.005

3 .003

.030

.897

.044

.010

.000

.016

4 .000

.006

.094

.869

.031

.000

.000

5 .000

.000

.003

.010

.961

.000

.026

6 .009

.014

.009

.005

.000

.963

.000

7 .000

.000

.000

.000

.000

.000

1.00

Vertical Sampling Interval=0.1 m

T

T = pvlq

n

q

vlkv

lk

1

Tlkv is the number of observed

transitions from Sl to Sk in the vertical direction.

Page 8: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Horizontal Transition Probability MatricesS. 1 2 3 4 5 6 7

1 .500

.100

.100

.100

.100

.100

.000

2 .100

.500

.100

.100

.100

.000

.100

3 .100

.100

.500

.100

.100

.000

.100

4 .100

.100

.100

.500

.100

.000

.100

5 .100

.100

.100

.100

.500

.100

.000

6 .001

.001

.001

.001

.001

.994

.001

7 .001

.001

.001

.001

.001

.001

.994

S. 1 2 3 4 5 6 7

1 .879 .103 .009 .000 .009 .000 .000

2 .026 .911 .046 .009 .003 .000 .005

3 .003 .030 .897 .044 .010 .000 .016

4 .000 .006 .094 .869 .031 .000 .000

5 .000 .000 .003 .010 .961 .000 .026

6 .009 .014 .009 .005 .000 .963 .000

7 .001 .001 .001 .001 .001 .001 .994

S. 1 2 3 4 5 6 7

1 .922

.015

.015

.015

.015

.015

.003

2 .015

.922

.015

.015

.015

.015

.003

3 .015

.015

.922

.015

.015

.015

.003

4 .015

.015

.015

.922

.015

.015

.003

5 .015

.015

.015

.015

.922

.015

.003

6 .015

.015

.015

.015

.015

.922

.003

7 .001

.001

.001

.001

.001

.001

.994

Page 9: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Probability Maps under Different Transition Probabilities

12345a

- 1 0

- 5

0

c- 1 0

- 5

0

d

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

b

- 1 0

- 5

0

e

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

- 1 0

- 5

0

0.000.250.500.751.00

LITH O LO G Y 1

LITH O LO G Y 2

LITH O LO G Y 3

LITH O LO G Y 4

LITH O LO G Y 5

LITH O LO G Y

Probability

Page 10: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison between Single Realizations and Final Images

0 50 100 150 200 250

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

0 50 100 150 200 250

-10

-5

0

0 50 100 150 200 250

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

1

2

3

4

5

Page 11: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Horizontal Transition Probability

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0 1

2

3

4

5

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

a

b

c

d

e

Page 12: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on Site Characterization

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

1

2

3

4

50 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

Page 13: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison of the Proportion of Each Lithology

Conditioned on Number of Boreholes Lithology 16 Boreholes 9 Boreholes 6 Boreholes

1 0.046 0.038 0.0122 0.258 0.207 0.205

3 0.327 0.380 0.479

4 0.097 0.109 0.141

5 0.273 0.267 0.163

Page 14: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Hydraulic Conductivity Assigned to Facies (Lithofacies Definitions from Rehfeldt, et al. 1992 and Lithofacies

Values from Adams and Gelhar, 1992).

Facies Measured Conductivity (m/day) lower limit upper limit mid range

1. Open work gravel 86.4 864. 475.2

2. Fine gravel 8.64 86.4 47.52

3. Sand 0.864 8.64 4.752

4. Sandy gravel 0.0864 0.864 0.4752

5. Sandy clayey gravel 0.00864 0.0864 0.04752

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

b

1

2

3

4

5

Page 15: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison of Statistics Computed from the Three Scenarios (with upper, lower and mid range

conductivities) and the values estimated from the MADE site (Rehfeldt et al., 1992)

ln( )K

Parameter

16 Boreholes 9 Boreholes 6 Boreholes MADE dataRehfeldt, et al., [1992].

-5.28 (Upper)-5.87 (Mid Range)-7.68 (Lower)

-5.44 (Upper)-6.03 (Mid Range) -7.43 (Lower)

-5.15 (Upper)-5.75 (Mid Range)-7.47 (Lower)

-5.2(-10.1 - 0.4)

8.19 (Upper)8.19 (Mid Range)7.31 (Lower)

7.43 (Upper)7.43 (Mid Range)7.43(Lower)

5.25 (Upper)5.25 (Mid Range)5.03 (Lower)

4.5(3.4 - 5.6)2

ln( )K

Page 16: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Variogram Analysis of Images

0 20 40 60 80Spatial Lag (m )

39.80

79.80

119.80

159.80

199.80

Vrai

ogra

m L

n(K)

in T

he V

ertic

al D

irect

ion

0 20 40 60 80Spatial Lag (m )

39.80

79.80

119.80

159.80

199.80

Vrai

ogra

m L

n(K)

in T

he H

oriz

onta

l Dire

ctio

n

16 boreholes (Table 4 and Table 1)9 boreholes (Table 4 and Table 1)6 boreholes (Table 4 and Table 1)16 boreholes (Table 3 and Table 1)9 boreholes (Table 3 and Table 1)6 boreholes (Table 3 and Table 1)16 boreholes (Table 2 and Table 1)9 boreholes (Table 2 and Table 1)6 boreholes (Table 2 and Table 1)

Page 17: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison of various Models with CMC

0 50 100 150 200 250

-10

-5

0

0

1

2

3

4

5

0 5 0 1 0 0 1 5 0 2 0 0 2 5 0

- 1 0

- 5

0

Page 18: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

MADE Site Data

0 50 100 150 200 250

-10

-5

0

0

1

2

3

4

5

Page 19: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Flow and Transport Models Assumptions

• 2D-Vertical Cross-Section.• Steady State Flow System:

(Seasonal Variability is Negligible).• Confined Aquifer Conditions.• Non-reactive Transport (Bromid Tracer).• Molecular Diffusion is Negligible.

Page 20: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Simulation Parameters

Parameter Numerical ValueTime step 0.5 [day]Longitudinal dispersivity 0.1 [m]Transverse dispersivity 0.01 [m]Effective porosity 0.35 [-]Injected tracer mass 2500 [grams]Head difference at the site 0.7 [m]Gradient 0.0025 [-] Number of particles 1000,000 [particles]K (Open work gravel ) 864. [m/day]K (Fine gravel) 86.4 [m/day]K (Sand) 8.64 [m/day]K(Sandy gravel ) 0.864 [m/day]K(Sandy clayey gravel ) 0.0864 [m/day]

Page 21: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Simulation of MADE1Experement under Different Values of Conductivities

0 0.1 1 10 100

-10

-5

0

1 2 3 4 5

-10

-5

0

-10

-5

0

49 days

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

-10

-5

0

-10

-5

0

49 days

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

-10

-5

0

-10

-5

0

49 days

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

Lithology Coding

Concentration Scale (m g/L)

Page 22: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on the Simulated Plume Upper conductivity

49 days

0 50 100 150 200 250

279 days

0 50 100 150 200 250594 days

0 50 100 150 200 250

49 days49 days

279 days279 days

594 days594 days

1 2

3

45

6

7 8 9 10

11

12

13

14

15

161

3

5 7 9

11 13 15

16161 5 7

11 13

-10

-5

0

-10

-5

0

0 0.1 1 10 100

-10

-5

0

-10

-5

0

49 days

0 50 100 150 200 250

-10

-5

0

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

-10

-5

0

-10

-5

0

-10

-5

0

0 50 100 150 200 250

-10

-5

0

-10

-5

0

49 days49 days

279 days279 days

594 days594 days

Page 23: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on the Simulated PlumeLower Conductivity

-10

-5

0

-10

-5

0

0

0.1

1

10

100

-10

-5

0

-10

-5

0

-10

-5

0

49 days

0 50 100 150 200 250

-10

-5

0

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

0 50 100 150 200 250

-10

-5

0

-10

-5

0

49 days49 days

279 days279 days

594 days594 days

Page 24: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on the Simulated Plume Mid Range Counductivity

-10

-5

0

-10

-5

0

0

0.1

1

10

100

-10

-5

0

-10

-5

0

-10

-5

0

49 days

0 50 100 150 200 250

-10

-5

0

-10

-5

0

279 days

0 50 100 150 200 250

-10

-5

0

594 days

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

-10

-5

0

0 50 100 150 200 250

-10

-5

0

-10

-5

0

49 days49 days

279 days279 days

594 days594 days

Page 25: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison between Measured and Simulated Mean Displacement

Page 26: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Comparison between Measured and Simulated Longitudinal Variance

Page 27: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on Lateral Variance

Page 28: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on The Angle of Rotation of The Plume

Page 29: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on Longitudinal Marco-Dispersion

Page 30: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on Lateral Marco-Dispersion

Page 31: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Effect of Number of Boreholes on The Breakthrough Curves

Page 32: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Observed, Predicted and Simulated Macro-dispersivities (with upper and mid range conductivities)

Dispersivity(m)

Observed Adams& Gelhars[1992]

This study(16 boreholes)

This study(9 boreholes)

This study(6 boreholes)

A11 5-10 1.48 -1.5 13.25 (Upper)4.3 (Mid Range)

8.75 (Upper)4.7 (Mid Range)

16.18 (Upper4.5 (Mid Range)

A33 not computed < 0.005 0.005 (Upper)~ 0 (Mid Range)

0.003 (Upper) ~ 0 (Mid Range)

0.0016 (Upper)0.0015 (Mid Range)

Page 33: Prediction of Contaminant Plumes (Shapes, Spatial Moments and Macro-dispersion) in Aquifers with Insufficient Geological Information

Conclusions

1. The CMC model has shown successful results in delineating the complex geological configuration of the aquifer at the MADE1 site.

2. Piih = 0.922 produces the main heterogeneous features in the

site when conditioned on 16 boreholes.

3. Flow and transport simulations capture the salient features of the flow field and the large scale plume behaviour at the site, although some assumptions are made.

4. Reducing the number of Conditioned boreholes from 16, 9 to 6 still shows reasonably the same plume behaviour in terms of average longitudinal and vertical extensions specially in the far-field. This gives more reliability on the use of CMC model for predicting plume configuration at field sites.