has eo found its customers? global vegetation monitoring unit mapping of arid regions in n. africa,...
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Global Vegetation Monitoring Unit
Mapping of arid regions in N. Africa, middle East and Southeast Asia using VGT S10
Michael Cherlet
Has
EO
foun
d its
cus
tom
ers?
Global Vegetation Monitoring Unit
Mapping of arid regions in N. Africa, middle East and Southeast Asia using VGT S10
Has
EO
foun
d its
cus
tom
ers?
Global Vegetation Monitoring Unit
Mapping of arid regions in N. Africa, middle East and Southeast Asia using VGT S10
Photo from 300 m height
Has
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Global Vegetation Monitoring Unit
Specific Problematic for Mapping Land Cover in Arid Areas
Low cover vegetation >> 3% - 40% (LCCS: sparse to open)
mixed with background soil
S10 NDVI products >> high variability of NDVI
not explained only by vegetation
In-Salah Oasis
50
55
60
65
70
75
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36
Decade
ND
VI
Tademait Plateau (in Salah)
50
55
60
65
70
75
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36
Decades
ND
VI
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Global Vegetation Monitoring Unit
IGBP
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Global Vegetation Monitoring Unit
timing of seasonal variability related to vegetation is difficult to determine:
- erratic character of rainfall in space and time
- influence of two climatic zones
N > Mediterranean influence
S > ‘tropical’ ITCZ influence
not possible to ‘choose’ best period for vegetation development throughout year
>> difficult to use S1
Specific Problematic for Mapping Land Cover in Arid Areas
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Global Vegetation Monitoring Unit
Using SPOT VGT S10 or longer composites based on MVC:
atmospheric, aerosol or clouds contamination is limited in S10 over arid areas (no persistence)
BRDF effect which is probably ‘enhanced’ in relation to topography
Spectral behaviour related to lithology and geology (colour)
confusionconfusion between low cover vegetation and sandy soils/sand-stones between low cover vegetation and sandy soils/sand-stones
Specific Problematic for Mapping Land Cover in Arid Areas
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Global Vegetation Monitoring Unit
Oct dek 1:
Unsure: 0.505 % of imageCloud :0.059 % of image
Nov dek 1:
Unsure: 0.715 % of imageCloud :0.029 % of image
Nov dek 2:
Unsure: 0.915 % of imageCloud :0.009 % of image
0
1
2
3
4
5
6
7
8
cloud
less d
ense
dens
e haze
light
haz
e
v, lig
ht h
aze
light
soil
med
ium so
il
dark
soil/r
ocks
gree
n ar
ea (m
ali)
MIR
/BO
MIR/BO cloud/haze
MIR/BO soils
2.48 thres
Linear (2.48 thres)
Threshold on ratio MIR/BO improves classification of unsure class
Contamination on S10
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Global Vegetation Monitoring Unit
Using SPOT VGT S10 or longer composites based on MVC:
atmospheric, aerosol or clouds contamination is limited over arid areas (no persistence)
BRDF effect which is probably ‘enhanced’ in relation to topography
Spectral behaviour related to lithology and geology (colour)
confusionconfusion between low cover vegetation and sandy soils/sand-stones between low cover vegetation and sandy soils/sand-stones
Specific Problematic for Mapping Land Cover in Arid Areas
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Global Vegetation Monitoring Unit
BRDF - Zone 4
0
10
20
30
40
50
60
70
-60 -55 -50 -45 -40 -35 -30 -25 -20 -15 -10 -5 0 5 10 15 20 25 30 35 40 45 50 55 60
VZN
0,000
0,020
0,040
0,060
0,080
0,100
0,120
0,140
0,160
nir red NDVI Linéaire (NDVI) Linéaire (nir) Linéaire (red)
11
21
1626 31
5
10
15
20
25 30 4
9
14
2429 3
813
2327
12
Backward Foreward
NDVINDVI
In general, but locally of importance increases confusion of e.g. sandstone outcrops and vegetation
Has
EO
foun
d its
cus
tom
ers?
Global Vegetation Monitoring Unit
Using SPOT VGT S10 or longer composites based on MVC:
atmospheric, aerosol or clouds contamination is limited over arid areas (no persistence)
BRDF effect which is probably ‘enhanced’ in relation to topography
Spectral behaviour related to lithology and geology (colour)
confusionconfusion between low cover vegetation and sandy soils/sand-stones between low cover vegetation and sandy soils/sand-stones
Specific Problematic for Mapping Land Cover in Arid Areas
Has
EO
foun
d its
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Global Vegetation Monitoring Unit
1.producing yearly composites: - NDVI image Max, Min, amplitude + statistics (st. dev….)
(cloudmask) - NDWI image Max, Mean, Min, amplitude + statistics(#methods tested) - Minimum B0, B2, B3, Mir
differentiation of different zones/masks using Max NDVI thresholds (~ cover)
Final Approach still openThree methods tried: 1.
Statistics of y2K Max NDVI green areas
0.00
20.00
40.00
60.00
80.00
100.00
120.00
0.12
0.15
0.18 0.2
0.23
0.26
0.29
0.32
0.34
0.37 0.4
0.43
0.46
0.48
0.51
0.54
0.57 0.6
0.62
0.65
0.68
0.71
0.74
0.76
0.79
0.82
0.85
0.88 0.9
NDVI
% o
f o
ccu
ren
ce
0.78 - 0.792
NDVI 0.786 = 100%
NDVI vs Cover
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
0 20 40 60 80 100
% cover
ND
VI
0.36 =~ 40%
Sensor sensitivity: 0.01
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Global Vegetation Monitoring Unit
- non-supervised classification (isoclass) within masks using yearly derived products
- grouping of ‘non-vegetation’ vs ‘vegetation’ classes and re-iterate isoclass and regrouping (min 3)based on subjective interpretation of all available data and field knowledgesubjective interpretation of all available data and field knowledge
- final grouping of all ‘non-vegetation’ and ‘vegetation’ masks
- differentiation of a. physical features using isoclass on bands and regrouping within ‘non-vegetation’
b. different ‘life forms’ within ‘vegetation’ part using NDVI time series statistics and ancillary data
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Orange: 3 - 6 % cover (GP length?) > LCCS: sparse herbaceous
Aquam: 6 - 10 % cover (GP length?) > LCCS: herbaceous
green1: 10 - 20 % cover (GP length?) > LCCS:
green2: 20 - 40 % cover (GP length?) > LCCS:
IGBPIGBP
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2.
2. - producing yearly composites: - NDVI image Max, Min, amplitude + statistics (st.dev….)- NDWI image Max, Mean, Min, amplitude + statistics- Min B0, B2, B3, Mir
- stratification of land-units based on classification of bandsstratification of land-units based on classification of bands (isoclass and re-grouping)
- non-supervised classification (isoclass) within landunits using yearly derived products- grouping of ‘non-vegetation’ vs ‘vegetation’ classes and re-iterate isoclass and regrouping (min 3)
based on subjective interpretation of all available data and field knowledge
- final grouping of all ‘non-vegetation’ and ‘vegetation’ masks
- differentiation of a. physical features using isoclass on bands and regrouping within ‘non-vegetation’, = optimizing first stratification
b. different ‘life forms’ within ‘vegetation’ part using NDVI time series statistics and ancillary data
Used to attach further info to vegetation classes:
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3. Determination of ‘vegetation’ character of individual pixels based on detection of significant NDVI change during year 2000 by separation of ‘background noise’ from ‘signal’ using long termtime series to establish ‘noise’ level per pixel (*):
3.
0
0.05
0.1
0.15
0.2
0.25
1st average - weight=1
Difference lessthan1%
the process stops
Δ
Decreasing weight with increasing NDVI value above the mean
Same weight (1) for the NDVI values under the mean
(Using Gaussian densityprobability function)
2nd average - weight=GF
(*) in cooperation with Univ. UCL, Belgium
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Global Vegetation Monitoring Unit
Image of MEANof ‘dry’ season
Image of STANDARDDEVIATION
of dry season
Pixel FLAGGEDPixel FLAGGEDNDVI > Mean + nSTDNDVI > Mean + nSTD
Result of the iterative process
Reflects a status of CHANGE in‘probable’ vegetation cover related to its “dry season” status
(whatever that is .... Soil or vegetation....)
Site2-Point7-Méthod2
0 11 22 33 44 55 66 77 88
Décades
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
N
D
V
I
NDVI>=0,14 NDVI>=2*s NDVI>=2,5*s NDVI>=3*s NDVI
(*) in cooperation with Univ. UCL, Belgium
Site5-Point6-Méthod2
0 11 22 33 44 55 66 77 88
Décades
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
N
D
V
I
NDVI>=0,14 NDVI>=2*s NDVI>=2,5*s NDVI>=3*s NDVI
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Global Vegetation Monitoring Unit
GPDF Threshold (2*StDev) and Max VI
0.00%
0.50%
1.00%
1.50%
2.00%
2.50%
3.00%
3.50%
4.00%
4.50%
-0.15 -0.1 -0.05 0 0.05 0.1 0.15 0.2 0.25 0.3 0.35 0.4 0.45 0.5 0.55 0.6 0.65 0.7 0.75 0.8 0.85 0.9 0.95 1
Ndvi
% o
ccu
ren
ce
Threshold
Max VI
Avg + 2*STdev
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Needs refiningto be used as base “probable vegetation” - non vegetation
Temporal mask …… and spatial mask
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Global Vegetation Monitoring Unit
Conclusions:
methods 1 & 2 - straightforward techniques- need for ‘ground’ knowledge- subjective- not very repeatable
method 3 - still to be validated technique- fine tuning required- objective- repeatable- ‘ground’ knowledge only required in final stage