Full text: Proceedings, XXth congress (Part 7)

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International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B7. Istanbul 2004 
  
and (iii) to validate the indices’ prediction capability using 
CASI (Compact Airborne Spectrographic Imager) hyperspectral 
images and LAI measurements collected over fields different 
from those used to collect ground spectra. 
2. MATERIAL AND METHODS 
2.1 Ground Spectra and Corresponding LAI Values for 
Prediction Equations 
The study area is located near Montreal, at the Horticultural 
Research and Development Centre of Agriculture and Agri- 
Food Canada, St-Jean-sur-Richelieu, Quebec, Canada. It is 
known as the L’Acadie Experimental Research Sub-station 
where various crops are grown on different experimental fields. 
Intensive field campaigns (IFCs) were organized during the 
growing seasons of 2000, 2001, 2002, and 2003 in order to 
collect ground spectra and corresponding LAI values as well as 
crop growth measures. Over these four years, different crops 
(corn, beans, and peas) were monitored on experimental and 
commercial fields. Acquisition dates were planned to coincide 
with different phenological development stages, aiming to 
monitor temporal changes in crop biophysical variables such as 
LAI, ground cover, and other growth measures. A particular 
emphasis was placed on acquiring ground data covering the 
earliest, middle and latest periods of the growth season. 
Spectral reflectance data over the region 0.4 — 1.1 mm 
wavelength region were acquired with the ASD 
spectroradiometer (Analytical Spectral Device, Boulder, CO). 
A white Spectralon reference panel (Labsphere, North Sutton, 
NH) was used to calibrate the spectroradiometer spectral 
radiance measurements to reflectance, by measurements of the 
reference panel under the same illumination conditions as the 
ground targets. Reflectances were calculated and corrected for 
the non-ideal properties of the reference panel as described by 
Robinson and Biehl (1979). In all experiments, radiometric data 
were collected close to solar noon; thus, changes in illumination 
conditions (solar zenith angle) were minimized. 
Crop LAI values corresponding to measured spectra were 
determined using both non-destructive and destructive methods 
using the Plant Canopy Analyzer (Li-Cor model LAI-2000) and 
an area meter (LI-3100, Li-Cor, Lincoln, NE), respectively. The 
latter was used to measure the LAI at the early growth stage, as 
well as to determine separately LAI of green and dead leaves 
during the senescence stage. 
2.2 CASI Hyperspectral Images and LAI Values for 
Validation 
The study area is located in Ottawa (Canada), at the former 
Greenbelt Farm of Agriculture and Agri-Food Canada. Over 
three successive “years, different crops (corn, wheat, soybean) 
were grown on a 30-ha field with a drained clay loam soil as 
well as on adjacent fields owned by farmers. The experiments 
consisted of dividing the main field into four regions receiving 
various nitrogen treatments: 100% of the recommended 
fertilization over a flat region, 100% of recommended nitrogen 
over a region with a gentle topographic slope, 60% of the 
recommended rate, and no nitrogen application (0%). They 
were thus laid out to promote development of remote sensing 
techniques for detection of plant stresses in precision 
agriculture, particularly stresses due to nitrogen deficiency, 
water deficit, and topographic influence. Within each region, a 
grid of georeferenced points spaced every 25 m was established 
109 
on a representative section of 150 m x 150 m. These locations 
were used to monitor crop biophysical parameters during the 
growing season, particularly during intensive field campaigns 
coinciding with image acquisition. Details on the experimental 
site and design are presented in Pattey et al. (2001). 
Hyperspectral images were acquired by the Compact 
Airborne Spectrographic Imager (CASI), flown by Centre for 
Research in Earth and Space Technology (CRESTech). 
Simultaneously, a set of field and laboratory data were 
collected for biochemical and geochemical analysis, along with 
optical and  biophysical measurements. Ground truth 
measurements included: (i) collection of leaf tissue for 
laboratory determination of leaf chlorophyll concentration, leaf 
area index (LAI) measurements using the Plant Canopy 
Analyzer (Li-Cor model LAI-2000), (ii) an area meter (LI- 
3100, Li-Cor, Lincoln, NE), and (iii) crop growth measures. 
During 2000 and 2001 growing seasons, CASI 
hyperspectral images were collected in three different 
deployments, using two modes of operation: the multispectral 
mode, with 1 m spatial resolution and 7 spectral bands selected 
for sensing vegetation properties (489.5, 555.0, 624.6, 681.4, 
706.1, 742.3, and 776.7 nm); and the hyperspectral mode, with 
2 m spatial resolution and 72 channels covering the visible and 
near infrared portions of the solar spectrum from 408 to 947 nm 
with a bandwidth of 7.5 nm. Acquisition dates were planned to 
coincide with different phenological development stages, 
providing image data covering the earliest, middle and latest 
periods of the growth season. 
The hyperspectral digital images collected by CASI were 
processed to at-sensor radiance using calibration coefficients 
determined in the laboratory by CRESTech (Centre for 
Research in Earth and Space Technology). Subsequently the 
CAMSS atmospheric correction model (O’Neill et al., 1997) 
was used to transform the relative at-sensor radiance to absolute 
ground-reflectance. To perform this operation, an estimate of 
aerosol optical depth at 550 nm was derived from ground sun- 
photometer measurements. Data regarding geographic position, 
illumination and viewing geometry as well as ground and 
sensor altitudes were derived both from aircraft navigation data 
records and ground GPS measurements. 
Reflectance curves derived from processed CASI images 
showed the presence of spectral anomalies associated with 
atmospheric absorption features at specific wavelengths. 
Although we applied model-based atmospheric corrections, the 
calculated reflectances are still affected by spectrally-specific 
errors owing mostly to an under-correction of some 
atmospheric components effects (oxygen and water vapour 
absorption). The flat field calibration is a correction technique 
used to remove the residual atmospheric effects from 
hyperspectral reflectance image cubes. Its aim is to improve 
overall quality of spectra and provide apparent reflectance data 
that can be compared with laboratory spectra (Boardman and 
Huntington, 1996). It requires the presence, and identification, 
in images of spectrally-flat uniform areas where the spectral 
anomalies can be unambiguously attributed, in narrow spectral 
ranges, to atmospheric effects and the solar spectrum. In CASI 
images, these features were observed over asphalt and concrete 
areas within the same image where the reflectance spectra are 
assumed to be flat or nearly flat over these features. Using 
signatures of such scene elements, we calculated coefficients 
that adequately compensate effects of atmospheric water and 
oxygen absorption. After those coefficients were applied to the 
entire image, but only in the specific spectral ranges affected, 
we checked the signatures of different components of the image 
and found that observed residual features have been 
successfully removed. 
 
	        
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