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The Calibration Process

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Calibration is accomplished by finding a set of parameters, boundary conditions, ... two ways of finding model parameters to achieve calibration ... – PowerPoint PPT presentation

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Title: The Calibration Process


1
The Calibration Process
  • Calibration of a flow model refers to a
    demonstration that the model is capable of
    producing field-measured heads and flows which
    are the calibration values.
  • Calibration is accomplished by finding a set of
    parameters, boundary conditions, and stresses
    that produce simulated heads and fluxes that
    match field-measured values within a
    pre-established range of error.

2
Targets in Model Calibration
  • Head measured in an observation well is known
    as a target. Baseflow measurements or other
    fluxes are also used as targets during
    calibration.
  • The simulated head at a node representing an
    observation well is compared with the measured
    head in the well. (Similarly for flux targets)
  • Residual error observed - simulated
  • During model calibration, parameter values
    (e.g., R and T) are adjusted until the simulated
    head matches the observed value within some
    acceptable range of error. Hence, model
    calibration solves the inverse problem.

3
Target Values
4
Inverse Problem
  • Objective is to determine values of the
    parameters and hydrologic stresses from
    information about heads, whereas in the forward
    problem system parameters such as hydraulic
    conductivity, specific storage, and hydrologic
    stresses such as recharge rate are specified and
    the model calculates heads.
  • The inverse problem is an estimation of boundary
    conditions, hydrologic stresses, and the spatial
    distribution of parameters by methods that do not
    involve consideration of heads.

5
  • Calibration can be performed
  • steady-state
  • Requires some flux input to the system
  • transient data sets.

6
Information needed for calibration
  • head values and fluxes or other calibration data
    (called sample information),
  • parameter estimates (called prior information)
    that will be used during the calibration process.

7
Sample Information
  • Heads
  • Sources of error
  • transient effects that are not represented in the
    model.
  • measurement error associated with the accuracy of
    the water level measuring device
  • Interpolation Error
  • Calibration values ideally should coincide with
    nodes, but in practice this will seldom be
    possible. This introduces interpolation errors
    caused by estimating nodal head values. This type
    of error may be 10 feet or more in regional
    models. The points for which calibration values
    are available should be shown on a map to
    illustrate the locations of the calibration
    points relative to the nodes. Ideally, heads and
    fluxes should be measured at a large number of
    locations, uniformly distributed over the modeled
    region.

8
Examples of Sources of Error
  • Surveying errors
  • Errors in measuring water levels
  • Interpolation error
  • Transient effects
  • Scaling effects
  • Unmodeled heterogeneities

9
Sample Information
  • Fluxes
  • Field-measured fluxes, such as baseflow,
    springflow, infiltration from a losing stream, or
    evapotranspiration from the water table may also
    be selected as calibration values.
  • associated errors for flux are usually larger
    than errors associated with head measurements.
  • Calibration to flows gives an independent check
    on hydraulic conductivity values.

10
Prior Information
  • Calibration is difficult because values for
    aquifer parameters and hydrologic stresses are
    typically known at only a few nodes and, even
    then, estimates are influenced by uncertainty.
  • Prior information on hydraulic conductivity
    and/or transmissivity and storage parameters is
    usually derived from aquifer tests.
  • Prior information on discharge from the aquifer
    may be available from field measurements of
    springflow or baseflow.
  • Direct field measurements of recharge are usually
    not available but it may be possible to identify
    a plausible range of values.
  • Uncertainty associated with estimates of aquifer
    parameters and boundary conditions must also be
    evaluated.

11
Calibration Techniques
  • two ways of finding model parameters to achieve
    calibration
  • (1) manual trial-and-error adjustment of
    parameters
  • (2) automated parameter estimation.
  • Manual trial-and-error calibration was the first
    technique to be used and is still the technique
    preferred by most practitioners.

12
Calibration parameters are parameters whose
values are uncertain. Values for these
parameters are adjusted during model calibration.
Typical calibration parameters include hydraulic
conductivity and recharge rate.
Parameter values can be adjusted manually by
trial and error. This requires the user to do
multiple runs of the model.
or parameter adjustment can be done with the
help of an inverse code.
13
Trial-and-Error Calibration
  • Parameter values assigned to each node or element
    in the grid.
  • The values are adjusted in sequential model runs
    to match simulated heads and flows to the
    calibration targets.
  • For each parameter an uncertainty value is
    quantified. Some parameters may be known with a
    high degree of certainty and therefore should be
    modified only slightly or not at all during
    calibration.
  • The results of each model execution are compared
    to the calibration targets adjustments are made
    to all or selected parameters and/or boundary
    conditions, and another trial calibration is
    initiated.
  • 10s to 100s of model runs may be needed to
    achieve calibration.
  • No information on the degree of uncertainty in
    the final parameter selection
  • Does not guarantee the statistically best
    solution, may produce nonunique solutions when
    different combinations of parameters yield
    essentially the same head distribution.

14
Trial and Error Process
15
Automated Calibration
  • Automated inverse modeling is performed using
    specially developed codes
  • Example PEST Parameter ESTimation,
  • Direct solution - unknown parameters are treated
    as dependent variables in the governing equation
    and heads are treated as independent variables.
  • The direct approach is similar to the
    trial-and-error calibration in that the forward
    problem is solved repeatedly. However, the code
    automatically checks and updates the parameters
    to obtain the best solution.
  • The inverse code will automatically find a set of
    parameters that matches the observed head values.
  • An automated statistically based solution
    quantifies the uncertainty in parameter estimates
    and gives the statistically most appropriate
    solution for the given input parameters provided
    it is based on an appropriate statistical model
    of errors.

16
Evaluating the Calibration
  • The results of the calibration should be
    evaluated both qualitatively and quantitatively.
    Even in a quantitative evaluation, however, the
    judgment of when the fit between model and
    reality is good enough is a subjective one.
  • There is no standard protocol for evaluating the
    calibration process.
  • Traditional measures of calibration
  • Comparison between contour maps of measured and
    simulated heads
  • A scatterplot of measured against simulated heads
    is another way of showing the calibrated fit.
    Deviation of points from the straight line should
    be randomly distributed.

17
Basecase simulation for the Final Project
18
Residual observed - simulated
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Tabular Data
22
Expressing differences between simulated and
measured heads
  • The mean error (ME) is the mean difference
    between measured heads (hm) and simulated heads
    (hs).
  • where n is the number of calibration values.
  • Simple to calculate
  • Both negative and positive differences are
    incorporated in the mean and may cancel out the
    error.
  • Hence, a small mean error may not indicate a good
    calibration.

23
Example of Mean Error
24
Tabular Data
25
Expressing differences between simulated and
measured heads
  • The mean absolute error (MAE) is the mean of the
    absolute value of the differences in measured and
    simulated heads.
  • All errors are positive.
  • Hence, a small mean error may would indicate a
    good calibration.

26
Expressing differences between simulated and
measured heads
  • The root mean squared (RMS) error or the standard
    deviation is the average of the squared
    differences in measured and simulated heads.
  • As with MAE, all errors are positive.
  • Hence, a small mean error may would indicate a
    good calibration.

27
Example of Root Mean Squared Error
28
  • The RMS is usually thought to be the best measure
    of error if errors are normally distributed.
    However, ME and MAE may provide better error
    measures (Figure 32).

29
Sensitivity Analysis
  • Purpose to quantify the uncertainty in the
    calibrated model caused by uncertainty in the
    estimates of aquifer parameters, stresses, and
    boundary conditions.
  • Process Calibrated values for hydraulic
    conductivity, storage parameters, recharge, and
    boundary conditions are systematically changed
    within the previously established plausible
    range. The magnitude of change in heads from the
    calibrated solution is a measure of the
    sensitivity of the solution to that particular
    parameter.
  • Sensitivity analysis is typically performed by
    changing one parameter value at a time.
  • A sensitivity analysis may also test the effect
    of changes in parameter values on something other
    than head, such as discharge or leakage

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