Scale considerations Flashcards

1
Q

Definitions

A

Particular character of objects with respect to time or space (1D, 2D, 3D, etc.)

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2
Q

Objects with scale

A
  1. Processes
  2. Observations
  3. Models
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3
Q

Special definitions of scale

A

(1) Extent → Total dimension, total time period
(2) Support → discretisation, raster, time steps
(3) Coverage → Observed/ modelled/ considered part of elements from total number of elements

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4
Q

Model structure:

Why distributed modelling?

A

(1) Variability of input variables (e.g. precipitation)
(2) Variability of basin characteristics (e.g. land use, soils)
(3) Considering different model approaches (e.g. urban, rural)

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5
Q

Model structure:

Conditions for model structuring:

A

(1) Problem appropriate (goals: target gauge, long term trends)
(2) Information appropriate (depends on available input data)
(3) Adequate for processes (floods vs. water balance)

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6
Q

Model structure:

Two types for model structuring:

A
  1. Horizontal structuring (→ runoff concentration, flood routing)
  2. Vertical structuring (→ runoff generation)
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7
Q

Spatial model structure – horizontal

A

a) Subcatchments, river sections

c) Quadratic raster network:

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8
Q

a) Subcatchments, river sections

A

Advantage:

  • Natural flow direction
  • 1D simulation possible
  • Fast computing
  • Many models available
  • Further structuring into hydrotopes easy possible

Disadvantage:

  • Poor distribution in space
  • no fully specification of location possible
  • Input scaling required
  • Hydraulics only for river sections possible
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9
Q

c) Quadratic raster network:

A

Advantages:

  • Fully explicit specification of locations!
  • Data usually available as raster data (e.g. elevations, weather radar rainfall)
  • Simple geometry for hydraulic approaches available

Disadvantages:

  • Flow direction not well defined
  • Real processes might take place at not-rectangular land forms
  • Uniform resolution required
  • Parameter intensive approach
  • Computationally expensive
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10
Q

Implicit, location independent structuring:

Hydrotopes

A

 Homogeneous with respect to hydrological behaviour
 Building of hydrotopes by combination of catchment properties
 Hydrotopes are also called HRU „hydrological response unit“ or HSU „hydrological similar units“

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11
Q

Implicit, location independent structuring:
Typical catchment characteristics
used for hydrotope building:

A

 Topography (Elevation, slope, etc.)
 Land use / coverage, vegetation
 Soil properties and
 Hydrogeology

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12
Q

Spatial model structure – vertical

A

 Application for each hydrotope class or raster cell or subcatchment

 Horizonal variation in model structure possible

 Further distribution within one simulation unit by statistical distribution of parameters possible

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13
Q

Scaling

A

 In a narrower sense → change of support for variables or
parameters (change of temporal or spatial resolution)

 In a wider sense → spatial or temporal transfer of variables or
parameters between two different scales

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14
Q

Regionalisation

A

 transfer of variables or parameters from known to unknown

points in space or time

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15
Q

Parameter estimation:

Calibration

A
  • Manual or automatic estimation (optimisation) of some model parameters
  • Repeated simulation with modified parameters (e.g. rainfall → runoff )
  • Maximize simulation performance comparing observed and simulated target variable (e.g. discharge)
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16
Q

Parameter estimation:

Validation

A
  • Test of model performance using a different data set and keeping model parameters constant
  • Using split sampling (two parts sample) or cross validation (leaf one out method) for separation of the data sets in calibration and validation data set

Note: Most often used criterion for the assessment of hydrological model performance is comparison of observed and simulated discharge

17
Q

Basic considerations for calibration

A

 Use as small as possible number of parameters for calibration
 Use parameters which cannot be derived from basin properties
 Try to restrict parameters to physically feasible range
 Use parameters with high sensitivity

18
Q

Analysis of parameter sensitivity

A

 Estimation of the sensitivity of the hydrological model output depending on change in parameters
 Sensitivity is often assessed with regard to model performance
 Theoretically analysis of a n-dimensional response surface corresponding to an n-dimensional parameter space
 Practically often only 1D sequential analysis changing one parameter at a time is carried out

19
Q

Model performance:

General comments

A

 Performance criteria are used both for optimisation in the objective function and for validation of the model

 Using simultaneously several criteria in optimisation (multi criteria optimisation) allows more robust parameter estimation

 Using additional criteria for validation is good test

 Performance criteria are usually calculated for each time step and then averaged over the total period

20
Q

Typical performance measures

A

mean error or bias: =0

Absolute/relative standard error: min

Nash-Sutcliff-criterion: 1 (-indefinite < NS <= 1

21
Q

Optimisation:

Local optimisation

A

 Locates the nearest optimum relative to the starting point no matter if it’s a local or global optimum

 One Parameter: e.g. univariate gradient method

 Several pars: downhill simplex (Nelder & Mead, 1965, HECHMS);
Gauss-Marquardt-Levenberg (Doherty, 2004, PEST)

22
Q

Optimisation:

Global optimisation

A

 Finds global optimum; different types of optimisation: deterministic, probabilistic, combination methods

 Well known example for combination methods is „Shuffled complex evolution“ algorithm (SCE) (Duan et al., 1992)

23
Q

Model Uncertainty

A

 All models are uncertain!

 Uncertainty can result from

a) Uncertain knowledge about processes
b) Uncertain model parameters
c) Uncertain input variables
d) Uncertain target/ reference variable(s)

 In modelling the uncertainty should be quantified:

a) The simplest way is by discussing the performance measures
b) Better is to provide results with confidence bands (Baye’sche uncertainty estimation, GLUE, different Monte-Carlo experiments, …)

24
Q

General Likelihood Uncertainty Estimation (GLUE):

Basic idea

A

 Because of our inability to represent exactly in a model how nature works there is no one optimal parameter set or model.

 Instead it is assumed that there are many good (behavioural) parameter sets equally suitable for simulation (equifinality).

 The different parameter sets are supposed to represent the uncertainties a) and b) (see above)

25
Q

General Likelihood Uncertainty Estimation (GLUE):

Procedure

A

 Find a representative set of parameter vectors and use these to assess model uncertainty together with predictions

 Realized by ensemble simulation using behavioral parameter sets weighted acc. to its prediction performance likelihood