canopy height model switzerland. covering the whole variety of switzerland (elevation, topography,...
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![Page 1: Canopy Height Model SWITZERLAND. Covering the whole variety of Switzerland (elevation, topography, species mixtures, open and close forest) Applying](https://reader036.vdocuments.site/reader036/viewer/2022070409/56649e955503460f94b99d73/html5/thumbnails/1.jpg)
Canopy Height Model SWITZERLAND
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Covering the whole variety of Switzerland (elevation, topography, species mixtures, open and close forest)
Applying models using CHM outside forest areas Large outliers in areas where matching was not
successful Time differences in comparison to reference data Temporal heterogeneity of the CHM Potential for change detection Leaf-off and leaf-on status
Challenges
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Canopy Height Model (CHM)- input image data- workflow
Accuracy assessment- reference data sets- accuracy measures
Forest application CHM- comparison tree heights NFI- habitat suitability modelling
Outline Work Christian & Martina
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ADS 80 aerial stereo-images- 0.25 and 0.5 m GSD- mosaic of year 2007-2012- leaf-on (May – September)- CIR Nadir/Backward 16bit (pushbroom)
Aerial image data
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Image matching in SocetSet- different strategies in NGATE- area- and feature-based methods- completeness of 0.95
170’000 blocks of 0.5 x 0.5 km- most nadir part of image
Reasonable calculation time - 16 min per block/strategy- 320 days (16 2-cores virtual PCs)- update ⅙ Switzerland in ~50 days
Image matching
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Topographic survey points N = 198- independent data set
Ground control points N = 2,483- used for image orientation
Stereo measurements N = 195,784- land cover types assigned- double measurements for accuracy estimation
Reference data sets – DSM accuracy
Restrictions: - matched points only - no water bodies- same image data- raster of 4 pixel for comparison
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Topographic survey points
DSM accuracies flat terrain
GSD [m] Sample Median [m] NMAD [m]0.25 164 0.07 0.290.50 34 -0.11 0.64
NMAD = Normalized Median Absolute Deviation
Terrestrial measurement of elevation [m a.s.l.]
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Topographic survey points
Ground control points
DSM accuracies flat terrain
Topographic survey pointsGround control points
GSD [m] Sample Median [m] NMAD [m]0.25 164 0.07 0.290.50 34 -0.11 0.64
GSD [m] Sample Median [m] NMAD [m]
0.25 2,033 -0.10 0.270.50 450 -0.18 0.50
NMAD = Normalized Median Absolute Deviation
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DSM accuracies land cover
Stereo measurementsdifferent land cover
Land cover class GSD [m] Sample size N Median [m] NMAD [m]
Coniferous forest 0.25 24,996 -0.08 1.760.50 7,594 -0.34 2.39
Deciduous forest0.25 13,211 0.16 2.950.50 11,076 -0.79 3.94
Herb and grass 0.25 55,689 -0.13 0.490.50 37,233 -0.25 0.95
Building 0.25 2,919 -0.12 0.830.50 359 -0.24 1.12
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DSM accuracies slope
Stereo measurementsdifferent slope categories
Slope [°] GSD [m] Sample size N Median [m] NMAD [m]
≤ 10 0.25 63,232 -0.16 0.670.50 7,944 -0.44 0.90
> 10 & ≤ 20 0.25 24,319 -0.17 1.300.50 17,337 -0.64 0.96
> 20 & ≤ 30 0.25 11,336 0.46 2.400.50 25,307 -0.86 1.29
> 30 & ≤ 40 0.25 4,999 1.17 3.260.50 24,098 -1.01 1.78
> 40 0.25 1,468 0.59 4.000.50 15,744 -1.36 2.52
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Calculated based on swissALTI3D- laser data, 0.5 points/m2
- settlements mask out with TLM- cut at 0 and 60 m
Canopy height model
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NFI 4 terrestrial tree heights N = 3,109- top canopy layer trees only- geolocated plots only- year image data < year field measurement
Buffer d=5 m around each tree- maximum value for comparison- only where > 15 points matched- not when maximum value equal zero
Double measurements NFI N = 441- estimation of measuring errors in the field
Comparison with tree heights NFI
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Correlation all trees
Tree height in canopy height model [m]
Tree
hei
ght N
FI [m
] r2 = 0.69, N= 3109
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Correlations tree type
Tree height in canopy height model [m]Tree height in canopy height model [m]
Tree
hei
ght N
FI [m
]
Tree
hei
ght N
FI [m
]
r2 = 0.7, N= 2137r2 = 0.7, N= 972
Deciduous trees Coniferous trees
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Correlations elevation
Tree height in canopy height model [m]Tree height in canopy height model [m]
Tree
hei
ght N
FI [m
]
Tree
hei
ght N
FI [m
]
r2 = 0.6, N= 1329r2 = 0.72, N= 1780
Lower elevations Higher elevations
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Comparison tree height NFI
Tree type GSD [m]
Sample size
Sample no out-lier
Median [m]
NMAD [m]
Quant 68% [m]
Quant 95% [m]
RMSE [m]
RMSE no out-lier [m]
Deciduous 0.25 872 865 -0.56 3.34 0.93 7.31 4.24 3.910.50 100 97 0.50 3.08 2.38 9.54 4.47 3.75
Coniferous 0.25 1562 1541 -1.86 2.65 -0.54 4.02 4.30 3.630.50 575 560 -2.54 3.72 -0.81 4.02 6.28 5.02
Median errors < 2.6 m NMAD < 3.8 m
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Median errors < 15 cm NMAD < 2m
Double measurements NFI
Tree type Sample size
Sample size no outliers
Median [m]
NMAD [m]
Quant 68% [m]
Quant 95% [m]
RMSE [m]
RMSE no outliers [m]
Deciduous 117 116 -0.10 1.93 0.72 3.28 2.42 2.28
Coniferous 324 320 -0.15 1.26 0.50 3.27 1.72 1.55
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Capercaillie (Tetrao urogallus)- umbrella species of conservation concern- structurally rich, semi-open forests
Paired presence/absence data
Habitat suitability modelling
Capercaillie
HabitatKurt Bollmann
Michael Lanz
n=104
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Explanatory variables Two models: (1) Aerial image CHM and (2) ALS CHM
*only for ALS model
Environment+ Climate+ Topography+ NDVI
StructureChm10avg Mean 10th percentile of CHM [m]Chm10sd SD 10th percentile of CHM [m]*Chm95avg Mean 95th percentile of CHM [m]Chm95sd SD 95th percentile of CHM [m]
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Aerial image data ALS dataAUC (SE) AUC (SE)
Structure 0.72 (0.04) 0.70 (0.05)
Habitat suitability model
Boosted regression trees 10-fold cross validation
Environment 0.89 (0.03) 0.88 (0.05)