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Hydrologic Data Assimilation: Merging Measurements and Models

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Title: Hydrologic Data Assimilation: Merging Measurements and Models


1
Hydrologic Data Assimilation Merging
Measurements and Models Steve
Margulis Assistant Professor Dept. of Civil and
Environmental Engineering UCLA CENS Technical
Seminar Series April 29, 2005
2
Outline
  • Introduction and Motivation
  • Data Assimilation and the Ensemble Kalman
    Filter
  • Application Soil Moisture Estimation via
    Assimilation of Microwave Remote Sensing
    Observations into a Hydrologic Model
  • Application to embedded sensor networks (?)
    Palmdale Wastewater Irrigation Site (future
    collaboration with Tom Harmon)

3
Introduction
  • Hydrologic Observations
  • Benefits
  • Provide important diagnostic information about
    real conditions
  • Yield important validation and model forcing
    databases
  • Limitations
  • Measurements generally sparse in time and/or
    space
  • interpolation/extrapolation
  • downscaling/upscaling
  • Contain measurement error
  • Often measuring states not fluxes
  • Hydrologic Models
  • Benefits
  • Representation of our knowledge of physical
    processes (dynamics)
  • Physical relationships between observables and
    states/fluxes of interest
  • Numerical tool for prediction
  • Limitations
  • Simplified abstractions of reality
  • Subject to uncertainties in time-varying
    inputs/time-invariant parameters

How can we combine the benefits of both in an
optimal framework?
4
What is data assimilation?
  • Goal Data assimilation seeks to characterize
    the true state of an environmental system by
    combining information from measurements and
    models.
  • Typical measurements for hydrologic applications
  • Ground-based hydrologic and geological
    measurements (stream flow, soil moisture, soil
    properties, canopy properties, etc.)
  • Ground-based meteorological measurements
    (precipitation, air temperature, humidity, wind
    speed, etc.)
  • Remotely-sensed measurements which are sensitive
    to hydrologically relevant variables (e.g. water
    vapor, soil moisture, etc.)
  • Mathematical models used for data assimilation
  • Models of the physical system of interest
  • Models of the measurement process
  • Probabilistic descriptions of uncertain model
    inputs and measurement errors

A description based on combined information
should be better than one obtained from either
measurements or model alone.
5
Key Features of Environmental Data Assimilation
Problems
State estimation -- System is described in terms
of state variables (random vectors), which are
characterized from available information Multiple
data sources -- Estimates are often derived from
different types of measurements (ground-based,
remote sensing, etc.) measured over a range of
time and space scales Spatially distributed
dynamic systems -- Systems are often modeled with
partial differential equations, usually
nonlinear. Through discretization the resulting
number of degrees of freedom (unknowns) can be
very large. Uncertainty -- The models used in
data assimilation applications are inevitably
imperfect approximations to reality, model inputs
may be uncertain, and measurement errors may be
important. All of these sources of uncertainty
need to be considered systematically in the data
assimilation process.
6
State-space Framework for Data Assimilation
  • State-space concepts provide a convenient way to
    formulate data assimilation problems. Key idea
    is to describe system of interest in terms of
    following variables
  • Input variables -- variables which account for
    forcing from outside the system or system
    properties which do not depend on the system
    state.
  • State variables -- dependent variables of
    differential equations used to describe the
    physical system of interest, also called
    prognostic variables.
  • Measurements -- variables that are observed (with
    measurement error) and are either directly or
    indirectly related to states.
  • Output variables -- variables that depend on
    state and input variables, also called diagnostic
    variables.

7
Basic Probabilistic Concepts in Data Assimilation
  • Uncertain forcing (u) and parameter (a) inputs
  • Postulated unconditional PDFs
    fu ( u) and fa (a )
  • Uncertain States (y)
  • Derived (from state eq.) unconditional PDF
    fy ( y )
  • Uncertain measurements (z)
  • Measurement PDF (error structure)
    fz ( z )
  • Knowledge of state after measurements included
  • Characterized by conditional PDF fy z
    (y z)
  • (Bayes Theorem)

8
Components of a Typical Hydrologic Data
Assimilation Problem
State Eq
Measurement Eq
The data assimilation algorithm uses specified
information about input uncertainty and
measurement errors to combine model predictions
and measurements. Resulting estimates are
extensive in time and space and make best use of
available information.
9
Characterizing Uncertain Systems
What is a good characterization of the system
state y(t), given the vector Zi z1, ..., zi
of all measurements taken through ti? The
posterior probability density p(y Zi) is the
ideal estimate since it contains everything we
know about the state y given Zi and other model
inputs u and a .
In practice, we must settle for partial
information about this density
  • Variational DA Derive mode of py(t) Zi by
    solving batch least-squares problem
  • Sequential DA Derive recursive approximation of
    conditional mean (and covariance?) of py(t) Zi

10
Monte Carlo Approach Ensemble Filtering
Divide filtering problem into two steps
propagation and update. Characterize random
states with an ensemble (j 1, , J) of random
replicates
Evolution of posterior probability density
Evolution of random replicates in ensemble
It is not practical to construct and update
complete multivariate probability
density. Ensemble filtering propagates only
replicates (no statistics). But how should
update be performed?
11
The Ensemble Kalman Filter (EnKF)
Propagation step for each replicate (y j)
Update step for each replicate
meas. residual
K Kalman gain derived from propagated ensemble
sample covariance. KCyz CzzCn-1 After each
replicate is updated it is propagated to next
measurement time. No need to update covariance
(i.e. traditional Kalman filter)results in large
computational savings.
12
Application Microwave Measurement of Soil
Moisture
Land surface microwave emission (at L-band) is
sensitive to surface soil moisture ( 5 cm).
  • Measurement Limitations
  • indirect measurement of soil moisture
    inversion?
  • sparse in time ( 1 measurement per day)
    interpolation?
  • spatially coarse (10s of kilometers)
    downscaling?
  • contains information about surface moisture only
    (want rootzone soil moisture) extrapolation?

13
Test Case Application to SGP97 Experiment Site
  • Month-long experiment in central OK in summer
    1997 (10,000 km2 area)
  • Daily airborne L-band microwave observations (17
    out of 30 days) to test feasibility of soil
    moisture estimation from space
  • Ground-truth soil moisture sampling performed
    daily at validation sites

Can we use EnKF to map rootzone soil moisture
fields and associated surface fluxes from
microwave measurements?
Margulis et al., 2002 2005
14
Key Features of Problem
  • Off-the-shelf models
  • Hydrologic NOAH LSM
  • Radiative Transfer Jackson et al. (1999)
  • Spatially-distributed states and parameters
  • Dealing with model nonlinearities and input
    uncertainties
  • Real-time (sequential) estimation
  • Next generation satellite observations (L-band
    passive microwave)

15
Spatially variable model inputs
NOAH soil class
NOAH vegetation class
Meteor. Stations
RTM Inputs
Clay fraction
El Reno
0
2
4
6
8
0
2
4
6
8
10
12
NOAH Model Inputs
0
0.05
0.1
Estimation region 40 by 280 km (11 by 70
pixels--4 km resolution)
16
Illustrative Results Sequential Updating
  • Left columns show estimated soil moisture fields
    before and after assimilating Tb
  • Right columns show estimated error in soil
    moisture fields from ensemble
  • Information in observations used to not only
    update mean fields, but reduces uncertainty

17
Illustrative Results Downscaling
Observing System Simulation Experiments (OSSEs)
Used to Investigate Impact of Coarse Measurements
Microwave Observations (Tb in ºK)
4 km
12 km
40 km
True Vol. Soil Moisture Field Day 178
Generate obs. at different meas. resolutions
Estimated Vol. Soil Moisture Fields
Space-time averaged results
18
Illustrative Results Interpolation
Comparison of Estimates to Real Ground-truth Time
series
Microwave obs. times
19
Illustrative Results Extrapolation/Flux
Estimation
Surface evaporation flux (latent heat) is a
function of entire rootzone moisture, not just
surface. Is information in radiobrightness
propagating to sub surface?
Note spin-up effect of filter during first 10
days
Over time, information from Tb about surface
conditions propagates downward through rootzone
20
Summary of Results
  • Data assimilation (in this case using the EnKF)
    allows for merging of model and data. Key
    benefits of this framework
  • inversion of electromagnetic measurement into
    estimates of hydrologic states of interest (soil
    moisture)
  • downscaling of coarse microwave radiobrightness
    measurement resolution to estimation scale
    (similar potential for upscaling?)
  • value added data products which are essentially
    continuous in time/space (interpolation between
    sparse measurements)
  • extrapolation/propagation of information to
    unobserved portions of domain (subsurface states)
    via incorporation of model physics
  • estimates of additional outputs of interest
    (e.g. fluxes) which are difficult to measure
    directly
  • estimates of uncertainty about mean estimate
    (via error propagation through system)

21
CENS Example Wastewater Reuse in Mojave Desert
  • Where does the County Sanitation District (CSD)
    of Los Angeles put 4 million gallons per day of
    treated wastewater in a landlocked region?
  • Can we use embedded sensors to track infiltration
    plume, assess nitrate concentrations, apply
    feedback control?

Reclaimed wastewater irrigation pivot plots
Palmdale, CA wastewater treatment plant
(slide courtesy of Prof. Tom Harmon)
22
Distributed Monitoring and Adaptive Management
Approach
  • Monitoring network design
  • How many sensors can we get away with?
  • How do we optimally place them?
  • Interpolating between sensors/extrapolating to
    depth
  • Distributed parameter models
  • Stochastic approaches

image by Jason Fisher (Cal-CLEANER)
(slide courtesy of Prof. Tom Harmon)
23
Site characterization
  • At the field scale
  • rigorous characterization sampling being done
  • geostatistical parameterization techniques

indicator kriging (probability Ks
exceeds...)
ordinary kriging (Ks)
(slide courtesy of Prof. Tom Harmon)
24
Proposed Research/Experiments
Data Assimilation (specifically the EnKF)
proposed as a potential tool for investigating
these research and operational implementation
questions
  • Task 1 Model and EnKF Interface
    Design/Implementation
  • Implementation of stochastic version of
    hydrologic flow/transport model
  • Input error model analysis using site
    characterization studies
  • EnKF wrapper design
  • Task 2 Network Design with Observing System
    Simulation Experiments
  • Model used to generate different measurement
    scenarios
  • Evaluation of scenarios using OSSEs to determine
    optimal sensor locations, sensor numbers, etc.
    (via minimization of state estimation error)

25
Proposed Research/Experiments (cont.)
  • Task 3 Real-time State and Parameter Estimation
  • After network deployment, use as real-time state
    estimation tool
  • Take advantage of early-life of sensors
    (accurate/stable error structure) to calibrate
    model parameters
  • Use real-time state estimates for feedback
    control
  • Task 4 Real-time Network Monitoring and
    Maintenance
  • What about degradation of sensor network over
    time?
  • Once model parameters are estimated, can
    measurement error be parameterized to detect
    changes in measurement error structure?

26
Summary
  • Data assimilation provides a very general
    framework for merging measurements and models
  • inversion, interpolation/extrapolation,
    uncertainty propagation, etc.
  • In hydrology, these techniques have primarily
    been used in the context of remote sensing due to
    limited availability of in-situ measurements
  • Problems where embedded sensor networks can be
    deployed are ideal candidates for application of
    these techniques where the ultimate goal is to
    maximize extraction of information content from
    measurements.

27
Acknowledgments
  • Funding for Research
  • NSF Water Cycle Research Grant
  • Collaborators
  • Dara Entekhabi (MIT)
  • Dennis McLaughlin (MIT)

28
Some Helpful Data Assimilation References
  • McLaughlin, D., 1995 Recent developments in
    hydrologic data assimilation, U.S. Natl. Rep.
    Int. Union Geod. Geophys. 1991-1994, Reviews in
    Geophysics, 33, 977-984.
  • Margulis, S.A., D. McLaughlin, D. Entekhabi, and
    S. Dunne, 2002 Land data assimilation and soil
    moisture estimation using measurements from the
    Southern Great Plains 1997 field experiment,
    Water Resources Research, 38(12), 1299,
    doi10.1029/2001WR001114.
  • Evensen, G., 2003 The Ensemble Kalman Filter
    theoretical formulation and practical
    implementation, Ocean Dynamics, 53, 343-367.
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