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Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Page 1: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

Bayesian and Geostatistical Approaches

to Inverse Problems

Peter K. KitanidisCivil and Environmental

EngineeringStanford University

Page 2: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

2

Outline:

• Important points• Current Work

Page 3: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Inverse Problem:

•Estimate functions from sparse and noisy observations;

•The unknowns are sensitive to data gaps or flaws (Problem is ill-posed in the sense of Hadamard);

•Data are insufficient to zero in on a unique solution;

•Usually, it is the small-scale variability that cannot be resolved.

Page 4: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Page 5: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Cheney, M. (1997), Inverse boundary-value problems, American Scientist, 85: 448-455.

Page 6: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Bayesian Inference Applied to Inverse Modeling

'''

'

p | pp

p | p d

y s ss

y s s s

Posterior distributionof unknown parameter

Prior distribution ofunknown parameter

Likelihood of unknownparameter given data

y : measurementss : “unknown”

Page 7: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

7

Bayesian Inference Applied to Inverse Modeling

'''

'

p | pp

p | p d

y s ss

y s s s

Combined information (data and structure)

Information about structure

Information from observations

y : measurementss : “unknown”

Page 8: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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How do you get the structure?

• We often use an “empirical Bayes” in which the structure pdf is parameterized and inferred from the data; the approach is rigorous and robust.– Alternative interpretation: We use cross-

validation.

• In specific applications, we may use “geological” or other information to describe structure.

Page 9: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Computational cost

• Reduce cost by dealing with special cases, or

• Bite the bullet and use computer intensive numerical methods (MCMC, etc.)

'''

'

p | pp

p | p d

y s ss

y s s s

Page 10: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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S t T 2

x12 2

x22 st x1 x2 #

A source identification A source identification problemproblemIdentify the pumping rate at an extraction Identify the pumping rate at an extraction

well from head observations, in a well from head observations, in a neighboring monitoring well: neighboring monitoring well:

2 21 2

0 0

1 1exp

4 4

t x xt s d

T t D t

The importance of The importance of properly weighing properly weighing

observationsobservations

Page 11: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

110 100 200 300 400 500 600 700 800 900 1000

-0.005

0

0.005

0.01

0.015

0.02

0.025

0.03

0.035

Time t [min]

Pum

ping

(ex

trac

tion)

rat

e q

[m3/m

in]

Best Estimate for Pumping Rate

EstimateActual

Over-weighting

Observations

Five slides from:

Kitanidis, P. K. (2007), On stochastic inverse modeling, in Subsurface Hydrology Data Integration for Properties and Processes edited by D. W. Hyndman, F. D. Day-Lewis and K. Singha, pp. 19-30, AGU, Washington, D. C.

Page 12: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

120 100 200 300 400 500 600 700 800 900 1000

-0.005

0

0.005

0.01

0.015

0.02

0.025

0.03

0.035

Time t [min]

Pum

ping

(ex

trac

tion)

rat

e q

[m3/m

in]

Best Estimate for Pumping Rate

EstimateActual

Under-weighting

Observations

Page 13: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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0 0.002 0.004 0.006 0.008 0.01 0.012 0.014 0.016 0.018 0.025

5.2

5.4

5.6

5.8

6

6.2x 10

-4

cR

0 0.002 0.004 0.006 0.008 0.01 0.012 0.014 0.016 0.018 0.026

7

8

9

10x 10

-7

Act

ual M

SE

theta ratio

2

1

ˆ1

ii

m

k

ssm

MSE

measure validationcrossa cR

Page 14: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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10-4

10-3

100

Q2

10-4

10-3

10-2

10-1

100

101

Act

ual M

SN

E

theta2

2

2

1

ˆ1

i

iim

k

ss

mNMSE

measure validationcrossa 2 Q

Page 15: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

0 100 200 300 400 500 600 700 800 900 1000-0.005

0

0.005

0.01

0.015

0.02

0.025

0.03

0.035Estim ateU pper C onf.Low er C onf.Actual

Tim e [m in]

Pu

mp

ing

Rat

e [

m/m

in]

3

“Optimal” Weighting

Page 16: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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The cost of computations…

• Moore’s law: Cost of computations is halved every 1.5 years. Thus, between 1975 and 2006: 2^(31/1.5)=1.7E6.

• $5,000 of computer usage for a project in 1975.

• 1975$5,000 -- adjust for inflation -> 2006$20,000.

• $20,000/1.7E6 corresponds to 1 cent worth of computational power in 2006.

Page 17: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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From the BOISE HYDROGEOPHYSICAL RESEARCH SITE (BHRS)

Page 18: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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• Based on Michalak and Kitanidis (2003 and 2004)

• Use EM method on marginal distributions to find optimal parameters for structure and epistemic error.

• Employ a Gibbs sampler to build a set of conditional realizations of posterior pdf. (A large enough set of conditional realizations has the same statistical properties as the actual posterior distribution.)

METHOD—Markov Chain Monte Carlo

Page 19: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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PCE data at location PPC13. Measurement data and fitted concentrations resulting from the estimated boundary conditions.Michalak, A.M., and P.K. Kitanidis (2003) “A Method for

Enforcing Parameter Nonnegativity in Bayesian Inverse Problems with an Application to Contaminant Source Identification,” Water Resources Research, 39(2), 1033, doi:10.1029/2002WR001480.

A problem of forensic environmental engineering

Page 20: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Location PPC13. Estimated time variation of boundary concentration at the interface between the aquifer and aquitard. The end time represents the sampling date (June 6, 1996).

Page 21: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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PCE data at location PPC13 with non-negativity constraint. Measurement data and fitted concentrations resulting from the estimated boundary conditions.

Page 22: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Location PPC13 with non-negativity constraint. Estimated time variation of boundary concentration at the interface between the aquifer and aquitard. The end time represents the sampling date (June 6, 1996).

Page 23: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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TRACER RESPONSE—Synthetic Case

Output

Without Error

With Error

Tracer Input

True Transfer Function

Fienen, M. N., J. Luo, and P. Kitanidis (2006), A Bayesian Geostatistical Transfer Function Approach to Tracer Test Analysis, Water Resour. Res., 42, W07426, 10.1029/2005WR004576.

Page 24: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Current Work

• Large variance and highly nonlinear problems (Convergence of Gauss-Newton, usefulness of Fisher matrix, etc.)

• Tomographic inverse problems (development of protocols, processing of large data sets.)

Page 25: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Current Work (cont.)

• Identification of zone boundaries.• Solution methods for very large

data sets.• Making tools available to users.

Page 26: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Identification of zone boundaries:

Example• Linear

tomography• Zones + small-

scale variability• measurement

error (2%)

Four slides from the work of Michael Cardiff

Page 27: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Example Problem Performance

Page 28: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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We are developing…

• Stochastic analysis of zone uncertainty

• Merging of structural (level set) and geostatistical inverse problem concepts

• Use of level sets for joint inversion

Page 29: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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Toolbox for

COMSOL Multiphysics is a commercial general purpose PDE solver.

We are adding inverse-model capabilities, including adjoint-state sensitivity analysis and stochastics.

See: Cardiff, M, and P. K. Kitanidis, “Efficient solution of nonlinear underdetermined inverse problems with a generalized PDE solver”, Computers and Geosciences, in review, 2007.

Page 30: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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•Stochastic: (aka probabilistic or statistical): We assign a probability to every possible solution.

Our approach is:

•Bayesian: Because the Bayesian approach provides a general framework.

•Practical: Our methods are evolving, with particular emphasis on practicality, robustness, and computational efficiency.

•Geostatistical: We have adopted the best ideas from the geostatistical school.

Page 31: Bayesian and Geostatistical Approaches to Inverse Problems Peter K. Kitanidis Civil and Environmental Engineering Stanford University

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For More Info

See publications on the WWW:http://

www.stanford.edu/group/peterk/publications.htm