bands for crop discrimination using hyperspectral data in VNIR
region are centred at 547, 675, 718 and 904 nm.
For studying the crop biophysical parameters and crop variability
five vegetation indices were generated using the hyperspectral data
with 15 nm width. Those are presented in table 2.
Table 2. Formulation for computation vegetation indices using
hyperspectral data ‘
Vegetation Index Formula
NDVI(552-687) (R552-R687)/(R552+R687)
NDVI(927-687) (R927-R687)/(R927+R687)
RVI(552-687) R552/R687
RVI(927-687) R927/R687
MSI R1662/R927
NDVI-Normalised Difference Vegetation Index, RVI- Ratio
Vegetation Index, MSI-Moisture Stress Index
For studying soil variability through spectral data various
radiometric indices related to soil colour were computed spectral
property. These indices, as described in Table3, were adopted
from Mathieu et al (1998). Since soil olour is influenced by the
presence of many soil constituents, such as iron oxides, limestone,
organic matter, and water content (Taylor, 1982), it was assumed
the colour related indices would properly highlight the soil
variability in spectral data. For computing colour related indices
the narrow band spectral values were averaged over the broadband
regions of blue, green and red, as defined in IRS LISS I sensors.
(Pandya et al, 2002).
Table 3. Radiometric indices calculated using hyperspectral data
for soil property study (adopted from Mathieu et al,
IAPRS & SIS, Vol.34. Part 7, “Resource and Environmental Monitoring”, Hyderabad, India,2002
1998) d
Index Formula Index Property
Brightness Index, BI | (R>+G*+B?)/3.0)*° | Average reflectance
magnitude
Saturation Index, SI (R-B)/(R+B) Spectra Slope
Hue Index, HI (2*R-G-B)/(G-B) Primary colours
Coloration Index, CI | (R-G)/(R+G) Soil Colour
Redness Index, RI R2/(B*G?) Hematite Content
3.4 Analysis of Satellite Data
IRS 1D LISS III (multi-spectral, 23-m resolution) and
Pan (panchromatic, 5.8-m resolution) data were acquired on
February 21, 2002. To get combination of high spectral resolution
of IRS LISS III and high spatial resolution of IRS Pan, both the
data were fused using the Brovey technique. Four indices were
computed for cropped field using LISS III data (table 4). For
studying the soil variability the Brightness index (BNI) is defined
by Leone et al. (1995). For this study the BNI was computed as
the sum of the DN values of all the three layers of merged data.
Table 4. Indices derived from IRS LISS III data.
Index Formula
NDVI -R +R
NDVI GR-R)/(GR+R
RVI
MSI
NIR, R, GR and MIR are DN values in Near Infrared, Red, Green
and Middle Infrared bands, respectively.
3.5 Statistical analysis and surface mapping
The statistical analysis of the measured parameters, both
conventional and spectral, were carried using standard Windows
based statistical software, such as SPSS for Windows, Releases
6.0. The statistical analysis included computation of standard
deviation and coefficient of variation of each parameter to know
the variability; correlation analysis of spectral and conventional
parameters; and empirical model fitting.
Surface maps were generated, for various parameters, using Surfer
V 7.0, the surface mapping system of Golden Software Inc. The
surface fitting was carried out using Krigging interpolation
technique.
4. RESULTS AND DISCUSSION
The spectroradiometer provided reflectance curves for 35
locations for the fallow plot and 30 locations for the wheat
cropped field. The average reflectance pattern of all these
locations, separately for soil and crop, are plotted in the figure 2.
0.60
——Crop — Soil
050 |
0.40
9
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=
3
oe 030
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9
~
020
0.10 +
0.00 T T T T T T T
300 500 700 900 1100 1300 1500 1700
Wavelength(nm)
Figure 2. Average spectral reflectance pattern of crop and soil
classes.
The reflectance curve showed the typical soil and crop spectra,
except some erroneous values between 1350-1390 nm due toe
error in detector response. The average crop spectra showed a
reflectance peak of 0.053 at 565 nm (green reflectance), dip of
0.021 at 675 nm (chlorophyll absorption), strong peak of 0.52 at
865 nm (leaf structure caused reflectance) and a dip of 0.052 at
1454 nm (water absorption). The soil reflectance consistently
increased from 0.078 at 355 nm to 0.40 at 1810 nm.
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