improving the calibration of the moland urban growth model with land-use information derived from a...
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Improving the calibration of the MOLAND urban growth model with land-use information derived from a time-series of medium resolution remote sensing data - Tim Van de Voorde, Johannes van der Kwast, Inge UljeeGuy Engelen, Frank CantersTRANSCRIPT
Measuring and modelling urban dynamics (MAMUD)
GEOG-AN-MOD 2010
Improving the calibration of the MOLAND urban growth model with land-use information derived from a time-series of medium resolution remote sensing data
Fukuoka, Japan, March 23, 2010
Tim Van de VoordeJohannes van der KwastInge UljeeGuy EngelenFrank Canters
Measuring and modelling urban dynamics (MAMUD)Page 2
Introduction
• MOLAND (http://moland.jrc.ec.europa.eu/): dynamic, constrained CA-based LU change model
• Land-use change models are becoming important instruments • for the assessment of policies aimed at
– improved spatial planning – sustainable urban development
• scenario analysis
• Need for robust and reliable tools
• Correct calibration and validation of land-use change models is of major importance
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Introduction
• Land-use change models are typically calibrated using a historic calibration
not Ok Ok
Actual map 2000
Hindcast Forecast
20001990 2030
Courtesy of EC JRCActual map 1990parameters
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Introduction
• Dynamic land use models require for their calibration time series of high quality and consistent land-use information
Medium resolution satellite images have been available since the 1970s (e.g. Landsat)
• How can remote sensing data be used to:
– correct inconsistencies in land-use maps available for calibration
– produce land-use information at more timesteps?
• How to use this additional land-use information for improving calibration of the EU MOLAND model ?
Measuring and modelling urban dynamics (MAMUD)Page 5
Land-use map Land-cover classificationRemote sensing image
≠
Physical StatisticalFunctional
Inferring Land-Use from RS?
Introduction
≠
Measuring calibration improvement?
• Precise location of land-use change cannot be predicted
• Similarity in spatial patterns is important
SPATIAL METRICS
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Spatial metrics:• Quantitative measures to describe structures and patterns in
the landscape • Calculated from remote sensing derived maps (thematic, continuous)• Quantify urban morphology and changes in morphology through time• Measures of composition and spatial arrangement
• Can be calculated at different levels of abstraction: class level, landscape level, moving window, regional, ...
• Examples of spatial metrics: class area, patch density, contagion fractal dimension, adjacency events, frequency distribution
• Link between form and function
Spatial metrics
Measuring and modelling urban dynamics (MAMUD)Page 7
Calibration framework
Compare using spatial metrics
Correct model parameters
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Overview
• Introduction• Inferring land use from RS data
• Updating existing LU maps• Creating new LU maps
• Calibration (preliminary)
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Inferring land use
1988 2001
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Inferring land use
• Urban blocks (5767)
• Blocks < 1ha topologically removed
• 1 block = 1 MOLAND LU type
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Inferring land use
Built-up density map:
• 4 classes of sealed surface cover:
• 0-10%
• 11-50%
• 51-80%
• > 80%
• Based on MOLAND legend
Urban gradient clearly present
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Inferring land use
16%56%Residential discontinuous (50%-80%)
16%82%Commercial areas
17%14%Sports and leisure facilities
STDEVAVG %
sealedMOLAND LAND USE
17%21%Green urban areas
17%49%Residential discontinuous sparse (10%-50%)
12%4%Arable land
54%
73%
81%
84%
21%Public and private services
18%Industrial areas
16%Residential continuous dense (>80%)
14%Residential continuous medium dense (>80%)
Histogram of %sealed within residential classes
0
100
200
300
400
500
600
700
0 10 20 30 40 50 60 70 80 90 100
% Sealed surface
Fre
qu
ency
CUF (>80%)
DUF (50%-80%)
DSUF (10%-50%)
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Inferring land use
Moland LU 2000
Updated
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Inferring land use
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Inferring land use
Low density residential
(59% sealed)
Industrial
(71% sealed)
α = 10.9829β = -6.5240γ =1.0155δ = 0.0004
α = 4.9783β = -10.2649γ =160.9718δ = 0.0798
Error of fit:sigmoid (red) = 0.03723
Error of fit:sigmoid (red) = 1.3819
δγ βα ++
= +− )(1
1)(
fi efP δγ βα +
+= +− )(1
1)(
fi efP
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Inferring land use
• 5 classes: residential, commercial, industrial, services, sports and green areas
employment / non-employment classes
• Only for blocks with 10-80% sealed surface cover
• Stratified random sample:
about 100 training/validation cases per class
• Used variables:
parameters of transformed logistic function
average proportion sealed surfaces
spatial variance for different lags
• Classifier: multi-layer perceptron
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Inferring land use
1988 2001
Measuring and modelling urban dynamics (MAMUD)Page 18
Overview
• Introduction• Inferring land use from RS data
• Updating existing LU maps• Creating new LU maps
• Calibration (preliminary)
Measuring and modelling urban dynamics (MAMUD)Page 19
Calibration
Reference LU map 2000 Model forecast 2000 (from 1990)
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Calibration
Contagion reference land-use 2000Landscape average = 52
Contagion hindcast 2000Landscape average = 48Fuzzy Kappa (0.87)
Contag Fuzzy K
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Calibration
MOLAND simulations (▲), remote sensing data (▼),land-use maps (О)
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