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26-02-2013
1
Hyperspectral Remote Sensing Applications for Vegetation
(with special emphasis on Agriculture)
Shibendu S. Ray
Mahalanobis National Crop Forecast Centre, DAC, New Delhi – 110 012
Space Applications Centre, ISRO, Ahmedabad – 380 015
Email: [email protected]
DST Sponsored Training Programme “Hyperspectral Remote Sensing for Agriculture”, February 18-27, 2013, IARI, New Delhi
Introduction
• Hyperspectral remote sensing deals with large number of
narrow spectral bands over a contiguous spectral range
• Because of its ability to detect narrow absorption features
hyperspectral data are related to specific vegetation
physico-chemical characteristics, ocean biological
constituents, soil physical and chemical properties, mineral
composition and snow characteristics
• Because of presence of large number of bands,
hyperspectral data needs different analysis approach
26-02-2013
2
Why Hyperspectral?
Absorption Spectra of Plant Pigments
Carotene Chlorophyll
Why Hyperspectral?
0.00
0.10
0.20
0.30
0.40
0.50
425 725 1025 1325 1625 1925 2225
Wavelength(nm)
Re
fle
cta
nc
e
Crops
Habitation
Plantation
Soil
Water
0
0.1
0.2
0.3
0.4
0.5
425 925 1425 1925
Crops
Habitation
Plantation
Soil
Water
(As per IRS Bands)
Hyperion Data for Different Landcovers
~10 nm bandwidth Modipuram (U. P.)
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3
Data Sources
Hyperion Field Spectroradiometer
HySi/IMS-1
CHRIS/PROBA
350-1075 (2500) nm range
Resol. 3nm (350-1000nm)
10 nm (100-2500 nm)
224 bands
400-2500 nm range
Spectral Resol. 10/11 nm
Spatial Resol. 30 m
Swath 7.5 km
64 bands
400-950 nm range
Spectral separation 8 nm
Spatial Resol. 505.6 m
Swath 129.5 km
Various data set:
Land set has
18 bands
438-1035 nm range
6-10 nm bandwidth
Spatial Resol. 17m
Swath 14 km
Multi-angular (5 angles)
AIMS
Average Altitude: 6.473 km
Spatial Resolution: 4.4 m
Swath : ~1.6 km
Spectral Range: 456-889 nm
Number of Bands: 143
Band Width: 3.3-4.1 nm
AHYSI (Airborne Hyperspectral Imager)
Spatial Resolution : 3.5 m
Spectral Range : 420-950 nm
Number of Bands: 512
Spectral sampling interval: 1.2 nm
Causes of leaf spectral characteristics
(from Jensen, 2000)
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4
Wavelength [nm] Cause of absorption Chemicals
430 Electron transition Chlorophyll a
460 Electron transition Chlorophyll b
640 Electron transition Chlorophyll b
660 Electron transition Chlorophyll a
910 C-H stretch, 3rd overtone Protein
1020 N-H stretch Protein
1510 N-H stretch, 1st overtone Protein, Nitrogen
1690 C-H stretch, 1st overtone Lignin, Starch, Protein, Nitrogen
1940 O-H stretch, O-H deformation Water, Lignin, Protein, Nitrogen,
Starch, Cellulose
1980 N-H asymmetry Protein
2060 N-H bend, 2nd overtone /
N-H bend / N-H stretch
Protein, Nitrogen
2130 N-H stretch Protein
2180 N-H bend, 2nd overtone /
C-H stretch / C-O stretch
C-O stretch / C-N stretch
Protein, Nitrogen
2240 C-H stretch Protein
2300 N-H stretch / C-H stretch /
C-H bend, 2nd overtone
Protein, Nitrogen
2350 CH2 bend, 2nd overtone /
C-H deformation, 2nd overtone
Cellulose, Protein, Nitrogen
Absorption features in vegetation reflectance spectra
(Adapted from Curran, 1989; Lucas & Curran, 1999)
Canopy Spectral Profile
Spectral Profile of Vraious Kharif Season Crops
0.000
0.100
0.200
0.300
0.400
0.500
0.600
0.700
300 600 900 1200 1500 1800 2100 2400
Wavelength (nm)
Refl
ec
tan
ce
Paddy
Sorghum
Maize
Finger millet
Cluster bean
Lady finger
Green gram
Horse gram
Cowpea
Dhaincha
Sugarcane
Cotton
Pigeon pea
Groundnut
Soybean
Sesamum
Sunflower
Castor
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Vegetation Indices
Vegetation Indices
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6
Red Edge
• The red edge position (REP), also known as the red edge inflection point (REIP), is defined as the wavelength around 720 nm at which the first derivative of the spectral reflectance curve reaches its maximum value.
• When a plant is healthy with high chlorophyll content and high leaf area index (LAI), the red edge position shifts towards longer wavelengths (red shifts) while the shift is towards shorter wavelengths (blue shift) when the plant suffers from disease or chlorosis and hence
low LAI.
show the spectral curves before and after this analysis is done using the software.
Figure 8.3 Spectral curve before and after continuum removal
Continuum Removal
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7
Hyperspectral Study of Pulse Crop
Spectral profiles of Rabi crops - Lalitpur, UP
0.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
325 375 425 475 525 575 625 675 725 775 825 875 925 975 1025 1075
Wavelength (nm)
Refl
ecta
nce (
%)
LENTIL PEA-FLOWERING PEA-FLOW/POD CHICKPEA-POD CHICKPEA-BRANCHING
Objective: discrimination of pulse crop using hyperspectral data
Area: Patha village, Mahrouni taluk, Lalitpur-Jhansi, UP (IFGRI)
Chickpea Branching
Chickpea Pod
Lentil
Pea Flowering Pea Pod Formation Step Wavelength Wilk’s F-Value
1 800 0.305 45.6
2 750,800 0.014 144.6
3 750,800,960 0.002 149.1
4 750,800,940,960 0.001 149.9
5 450,750,800,940,960 0.000 162.7
6 450,490,750,800,940,960 0.000 187.1
7 450,490,670,750,800,940,960 0.000 188.3
Discriminant Analysis
Crop Stage Discrimination
• Data: Airborne HySI
• Crop: Sorghum 3 Stages
• Location: Visalpur Village near Ahmedabad
FCC Classified Simulated LISS IV
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Crop Stress Detection (Nitrogen)
• 7 levels of nitrogen applied to potato crop
• Lower level of nitrogen had low NIR reflectance and high red reflectance
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
300 400 500 600 700 800 900 1000 1100
Wavelength (nm)
Re
fle
cta
nc
e
N0 N50 N100 N150 N200 N250 N300
Crop Stress Detection (Nitrogen)
• Best Bands were selected using Stepwise Discriminant Analysis, Principal
Component Analysis and Band-Band Correlation (560, 650, 730 and 760nm)
• Many Narrowband indices evaluated for discrimination
• Red edge ratio and SIPI((R800 - R445)/(R800 + R680)) best for discrimination
• Similar analysis for disease detection and water stress discrimination
1
1.1
1.2
1.3
1.4
1.5
1.6
0.65 0.7 0.75 0.8 0.85 0.9
SIPI
Re
d e
dg
e 7
40
/72
0
N0 N50 N100 N150 N200 N250 N300
1
1.1
1.2
1.3
1.4
1.5
1.6
0.65 0.7 0.75 0.8 0.85 0.9
SIPI
Re
d e
dg
e 7
40
/72
0
N0 N50 N100 N150 N200 N250 N300
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Crop Parameter Estimation (Development of Indices: Chlorophyll)
• Correlation curves generated for potato leaf chlorophyll with reflectance & derivatives
• Bands selected for ratio, using peaks and troughs of correlation curves
• Red-edge importance was shown in derivative based indices
-0.6
-0.5
-0.4
-0.3
-0.2
-0.1
0
0.1
0.2
300 500 700 900 1100
Wavelength (nm)
Co
rre
latio
n c
oe
ffic
ien
t
Chl a Chl b Total ChlorophyllIndices Chl a Chl b Total
Chl
Ratio based indices
R750/R700 0.63** 0.45* 0.53** R750/R610 0.51** 0.33 0.41* R750/R420 0.42* 0.25 0.33
First derivative based ratios
D740/D690 0.69** 0.50* 0.59**
Second derivative based ratios
Dd720/Dd680 0.63** 0.45* 0.53** Dd720/Dd750
-0.66**
-0.47*
-0.55**
400 500 600 700 800 900 1000
400
500
600
700
800
900
1000
-0.75
-0.7
-0.65
-0.6
0
0.6
0.65
0.7
0.75
Crop Parameter Estimation (Development of Indices)
• Correlation map of ratio based (all possible band combinations) indices with leaf nutrients
• Selection of ratios with high correlation
• Stepwise regression for best fit model (-0.373+2.634 r750/710; R2 = 0.551, F=31.9**)
Leaf Nitrogen
26-02-2013
10
LEAF
CHARACTERISTICS
N, Cab, Cw
PROSPECT
Leaf
Reflectance
Transmittance
SAIL
CANOPY
REFLECTANCE
Measurement
Characteristics
(View & Sun Angle)
Canopy
Structure
LAI, LAD
Soil
Reflectance
PROSPECT+SAIL
Canopy Reflectance Model
1. PROSPECT (leaf optical properties model) requires the leaf structure parameter N,
the chlorophyll a,b content Cab (g/cm2), the equivalent water thickness Cw (g/cm2),
and dry matter content (g/cm2) to simulate leaf reflectance and transmittance spectra
in the optical domain.
2. SAIL (Scattering by Arbitrary Inclined Leaves) is the canopy reflectance model, which
computes canopy reflectance coupled with PROSPECT and using leaf area index
(LAI) and leaf angle distribution (LAD), soil background reflectance.
PROSAIL Model Calibration & LAI Estimation
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11
PROSAIL Inversion Software (PRIS)
Hierarchical Calibration
Neural Network Training
Inversion using GA
Inversion using NN
HySi/IMS-1
64 bands; 400-950 nm range; Spectral separation 8 nm;
Spatial Resol. 505.6 m; Swath 129.5 km Specifications
Crop Classification using HySI Data
Soil Parameter RMSE R2 RPD
N 11.058 0.838 10.509
P 2.872 0.963 6.809
K 7.049 0.862 4.062
SOC 0.101 0.830 6.730
Sand 6.877 0.848 6.234
Silt 5.403 0.833 5.252
Clay 3.282 0.801 9.532
Soil Parameter Estimation using HySI Data, PLSR Model and Ground Observation
26-02-2013
12
Remote Sensing of Crop Residue
Soil
Residue
Straw
Matured Wheat
CAI
-2
-1
0
1
2
3
4
5
RESIDUE STRAW MATURED SOIL
LCA
0
1
2
3
4
5
6
7
RESIDUE STRAW MATURED SOIL
CAI: Cellulose Absorption Index
LCA =100[2*R2.2 − (R2.1 + R2.3)]
LCA: Lignin Cellulose Absorption Index
Forest Species Classification
Study Area: Shoolpaneswar Forest Data Used: Hyperion Data of October Approach: Band Selection using PLSR technique, Different Classifiers
26-02-2013
13
Discrimination of Different Forest Classes
Forest Research Institute (FRI)
Isodata: 6 classes FRI map SAM: 6 classes
Avicennia alba
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
flec
tan
ce
Adaxial surface Abaxial surface
420
1130
1150
Avicennia alba
L = 0.001
Sonneratia caseolaris
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wanelength (nm)
Re
fle
cta
nc
e
Adaxial surface Abaxial surface
2050 1440
470
440
Sonneratia caseolaris
L = 0.044
Rhizophora mucronata
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
1
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
flec
tan
ce
Adaxial surface Abaxial surface
400
920
1620
2070 2320
1640
Rhizophora mucronata
L = 0.000
Leaf reflectance spectra
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
fle
cta
nc
e
Aa random leaves
Rm random leaves
Sc random leaves
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.045
0.05
400 600 800 1000 1200 1400 1600 1800 2000 22000
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.045
0.05
400 600 800 1000 1200 1400 1600 1800 2000 2200
p-v
alu
e
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.045
0.05
400 600 800 1000 1200 1400 1600 1800 2000 2200
p-v
alu
e
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.045
0.05
400 600 800 1000 1200 1400 1600 1800 2000 2200
p-v
alu
e
99% confidence level
95% confidence level
0
0.005
0.01
0.015
0.02
0.025
0.03
0.035
0.04
0.045
0.05
400 600 800 1000 1200 1400 1600 1800 2000 2200
p-v
alu
e
0 0
Random leaves
550, 720, 1630, 1750 nm
L = 0.003
Mangrove Study
26-02-2013
14
Canopies of Nypa fruticans and Phoenix paludosa
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
fle
cta
nc
e
N. fruticans P. paludosa
Canopies of Sonneratia apetal vs Sonneratia caseolaris
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
fle
cta
nc
e
S. apetala S. caseolaris
Canopies of Xylocarpus mekongensis vs Xylocarpus
granatum
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
fle
cta
nc
e
X. mekongensis X. granatum
Canopies of Avicennia officinalis vs Avicennia alba
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
400 600 800 1000 1200 1400 1600 1800 2000 2200
Wavelength (nm)
Re
fle
cta
nc
e
A. officinalis A. alba
400 2310
L = 0.03
2080 580 1540
2150
550
400
430 690
960
1000
720
970
1000
L = 0.004
L = 0.011 L = 0.019
Avicennia officinalis vs. A. alba Sonneratia apetala vs. S. caseolaris
Nypa fruticans vs. Phoenix paludosa Xylocarpus mekingensis vs. X. granatum
Mangrove Study
a
b c
Class 1
Class 2
Class 3
Class 4
Class 5
Others
75.28%
К = 0.69 Overall Accuracy = 65.39%
Kappa Coefficient (К) = 0.59 97.97%
К = 0.97
FCC Minimum Distance Spectral Angle Mapper Support Vector Machine
Mangrove Classification: Bhitarkanika
Class 1 Pure/ dominant communities of
Heritiera fomes
Class 2 Mixed communities of H. fomes
(with Cynometra ramiflora,
Aegiceras corniculatum,
Rhizophora mucronata, etc.)
Class 3 Mixed communities of
Excoecaria agallocha (with
Avicennia sp.)
Class 4 Fringing stands of mixed
Sonneratia apetala (with other
landward species)
Class 5 Mixed communities of
mangrove associates & salt
tolerant grasses
0
10
20
30
40
50
60
70
80
90
100
196 148 98 96 88 79 63 56 39 23 8
Number of bands
Ov
era
ll a
cc
ura
cy
(%
)
0
5
10
15
20
25
30
De
cre
as
e in
ac
cu
rac
y (%
)
Overall accuracy (%) Decrease in accuracy (%)
26-02-2013
15
In situ spectra of various wetland plant species
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0.70
0.80
325 375 425 475 525 575 625 675 725 775 825 875 925 975 1025 1075
Wavelength (nm)
Re
fle
cta
nc
e
Phragmites Ipomoea Typha Cheda Nelumbo Nympheae Chara
A
E
B
F
C
G
D
A: Phragmites karka
B: Typha angustata
C: Cheda (local name)
D: Ipomoea aquatica
E: Nelumbo nucifera
F: Nympheae stellata
G: Chara sp.
Wetland Vegetation Discrimination & Water Quality
AVERAGE SPECTRA OF WATER, CHILIKA LAGOON
-0.10
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0.70
0.80
300 400 500 600 700 800 900 1000 1100
WAVELENGTH (nm)
RE
FL
EC
TA
NC
E
Site-1
Site-2
Site-3
Site-4
Site-5
Site-6
Site-7
Site-8
Site-9
Site-10
Site-11
Best Reflectance Ratio
for Chlorophyll
Estimation
R713/R680
Correlation coefficient
for Chlorophyll-a (0.659)
and
Chlorophyll-a+
Pheophytine (0.677)
Site-1 Site-8
Site-10 Site-6
CV Indices
0
5
10
15
20
25
30
35
40
1 2 3
Stages Of Wheat
Perc
en
tag
e
NDVI
SR
NDVI705
mSR705
mNDVI705
SAVI
MSAVI2
OSAVI
MCARI
TCARI
NPCI
MCARI2
RdEdg
ZTM
PRI
SIPI
ARVI
EVI
RGRI
Angular effects on Vegetation Indices
Least anisotropy- SIPI and RGRI – CV <5%. They are ratios of bands
with similar angular effects and hence tend to cancel out the common
effects.
Maximum anisotropy for Red Edge, ARVI, MSAVI, MCARI etc
Other indices showing less anisotropy- ZTM,NPCI and mSR705
CV of Indices
Analysis of CHRIS/PROBA Data
26-02-2013
16
(a ) Earhead~Grain Formation
-20
0
20
40
60
80
100
120
140
160
180
-55.37 -36.77 +32.64 +53.31
View angle (°)
% C
ha
ng
e i
n d
no
rm
442.2 490 529.8 551 569.6 630.9
660.6 674.1 696.9 705.9 712 741.1
751.3 780.2 871.4 894.6 909 1018
(b ) Earhead~Milking Stage
-5
0
5
10
15
20
25
30
35
40
-55.37 -36.77 +32.64 +53.31
View angle (°)
% C
ha
ng
e i
n d
no
rm
442.2 490 529.8 551 569.6 630.9
660.6 674.1 696.9 705.9 712 741.1
751.3 780.2 871.4 894.6 909 1018
(c ) Grain Formation~ Milking Stage
-10
0
10
20
30
40
50
60
-55.37 -36.77 +32.64 +53.31
View angle (°)
% C
ha
ng
e i
n d
no
rm
442.2 490 529.8 551 569.6 630.9
660.6 674.1 696.9 705.9 712 741.1
751.3 780.2 871.4 894.6 909 1018
The Percent change in normalized distance from nadir between the reflectance of wheat crop in
different stages, for non- nadir view angles
Analysis of CHRIS/PROBA Data
LAI Vs VI
-0.6
-0.4
-0.2
0
0.2
0.4
0.6
0.8
ND
VI
SR
ND
VI7
05
mS
R7
05
mN
DV
I70
5
SA
VI
MS
AV
I2
OS
AV
I
MC
AR
I
TC
AR
I
NP
CI
MC
AR
I2
Rd
Ed
g
ZT
M
PR
I
SIP
I
EV
I
AR
VI
RG
RI
Vegetation Indices
R2
-55
-36
0
55
Graph showing correlation of LAI and vegetation indices computed using CHRIS/PROBA data.
Spectral Analysis Software
Spectral
Analysis
Continuum
Removal
Red Edge
Analysis
Data
Smoothing
Averaging
Derivative
Spectra
Vegetation
Indices
View Chart
Simple
Averaging
Broadband
Conversion
Chart
Chart
Chart
Chart
Chart
Predefined
Indices
Index
Calculator
Chart
An In-house developed
software to analyze spectral
profiles derived from
spectroradiometer
26-02-2013
17
Fig. 4. Graphic User Interface (GUI) and query modules of spectral Library
Send req. for
Plant List of
Plantation
Send req. for
Plant List of
Crops
Send req. for
Plant List of
Ornamental
User
Vegetation
Spectral Library
GUI
Natural
Vegetation
Plantation
Ornamental
Plants
SAC.mdb
Spectral
View
General
Info
Vegetatio
n AnalysisPlant
photograph
Observation
Details
Spectral
Details
Send Request
Send Request
Plant Info displayed on GUI on the basis of User’s Request
Plant List
displayed
Send request for Plant
List of Natural Veg.
Select
Plant
name
1
2
3
4
5
6
7
Development of Spectral Library
Optimum Band Selection
• Large Dataset
• Stepwise discriminant analysis
SOURCE OF VARIATION
WAVELENGTHS SELECTED WILKS’ LAMBDA
F VALUE
Rabi Season Crops (4)
400,450, 480, 550, 660, 680 nm 0.000 85.5
Kharif Season Crops (5)
400, 420, 450, 500, 550, 590, 600, 610, 670, 660, 710, 730, 740, 760, 830, 940 nm
0.001 86.3
Wheat Varieties (15) 370, 940, 770, 750, 1030 nm 6.32E-05
Mustard Stages (2) 400, 430, 480, 610 nm 0.065 53.9
Cotton- Dates of Sowing (2)
560,700 nm 0.001 1568.2
Rice: Nitrogen Treatments (5)
400, 440, 570, 710, 740, 760, 770, 800, 930, 970 nm
0.001 22.5
Rice: Phosphorus Treatments (5)
640, 680 nm 0.701 3.4
Potato: Irrigation Treatments (3)
540, 610, 630, 700,1000 nm 0.172 8.16
Soil Types (4) 420, 720, 770, 790, 850 nm 0.000 319.6
26-02-2013
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Selected Narrowbands
• Integration of all outputs, Bands selected on the basis of frequency of occurrence
• 13 optimum bands in VNIR (400-1050 nm) region
• These included bands in violet (2), blue (2), green (1), red (3), red edge (2), NIR (2)
and moisture sensitive NIR (1) region.
Frequency of Bands
0
1
2
3
4
5
370
400
420
430
440
450
480
500
540
550
560
570
590
600
610
630
640
660
670
680
700
710
720
730
740
750
760
770
790
800
830
850
940
970
1000
1030
Wavelelength (nm)
Fre
qu
en
cy
First Derivative Spectra
-0.03
-0.02
-0.01
0
0.01
0.02
0.03
0.04
400 500 600 700 800 900 1000
Wavelength (nm)
Fir
st
deri
vati
ve (
off
set)
3-nm 5-nm
10nm 15nm
20nm 25nm
30nm
Optimum Bandwidth
1st Derivative of Reflectance at Different Bandwidth with offset
• Data from nitrogen treatment of rice crop
• Original spectral resolution 3 nm, resampled to 1 nm
• Comparison of reflectance and derivative
• Integrated to 3, 5, 10, 15, 20, 25, 30 nm
26-02-2013
19
Optimum Bandwidth
• Optimum bandwidth required differed for different wavelength regions
• 700-800 nm region: ~5 nm, 600-700 & 800-900 nm: upto 15 nm; 400-500nm and 900-
1000nm: upto 25
Reflectance
difference
at peaks
RMSE at
varying
Bandwidth
RMSE at varying Bandwidth
0
0.05
0.1
0.15
0.2
5 10 15 20 25 30
Bandwidth
RM
SE
(40
0-5
00
,70
0-8
00
,90
0-1
00
0)
0
0.01
0.02
0.03
0.04
0.05
0.06
RM
SE
(50
0-6
00
, 6
00-7
00
, 8
00-9
00
)
400-500 700-800 900-1000
500-600 600-700 800-900
Bandwidth (nm) Reflectance (%); Difference from 3 nm 3 5 10 15 20 25 30
Reflectance 13.0 13. 12.8 12.5 12 11.8 11.3 Green Maximum Difference -- 0 -0.2 -0.5 -1 -1.2 -1.7
Reflectance 2.5 2.5 2.6 2.7 2.5 2.75 2.9 Red Minimum Difference -- 0 0.1 0.2 0 0.25 0.4
Reflectance 58.0 57.0 56.0 55.0 52.0 52.0 53.0 NIR maximum Difference -- -1.0 -2.0 -3.0 -6.0 -6.0 -5.0
Conclusion
• All these studies have been carried out under ‘Hyperspectral Remote Sensing Applications’ project of Space Applications Centre, in collaboration with large number of organizations including IARI.
• Narrowband data have shown higher potential in assessing crop stresses, vegetation type discrimination, and so on.
• It was also found suitable for more accurate bio-chemical and bio-
physical parameter retrieval
• Various software and database have been developed for better interpretation of hyperspectral data.
• Methodologies have been developed for selection of optimum bands and bandwidth for vegetation studies.