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 
2.2 Analytical methods 
WA was implemented within Matlab 6.1 using the Wavelet 
Toolbox (v.2.1). Multilevel 1-D wavelet decompositions were 
performed on reflectance spectra using the range of different 
wavelet basis functions available in this package. 
Approximation and detail coefficients were extracted for each 
spectrum and a stepwise multiple linear regression was 
performed on the wavelet coefficients and pigment 
concentrations of the leaves and canopies under investigation. A 
95% confidence interval was used in the stepwise procedure 
and up to 9 terms were permitted in the regression model 
(however, in most cases the number of terms selected ranged 
between 3 and 6). The predictive capabilities of the regression 
model were evaluated by calculating the coefficient of 
determination for prediction - the averaged coefficient of 
determination with one observation removed from the model 
(leave-one-out cross validation). 
3. RESULTS 
For all leaves and canopies sampled a number of wavelet basis 
functions (wavelet families) produced coefficients from which 
multiple regression models could be derived that were 
correlated with pigment concentrations: Daubechies wavelets 
(shortened to 'db' subsequently); Symlets ('sym'); Coiflets 
('coif);  Biorthogonal wavelets  ('bior); and, Reverse 
biorthogonal wavelets ('rbio'. Generally the higher order 
wavelets within each family produced the highest correlation 
with pigments- hence the results for these wavelets are 
displayed below. 
3.1 Individual leaves and stacks of leaves. 
The range of pigment concentrations generated using the 
individual leaves and leaf stacks was large: 13 to 3235 mg.m? 
for Chl a, 8 to 2168 mg.m™ for Chl ^ and 80 to 1447 mg.m for 
Cars. Even over this large range of concentrations the multiple 
regression models derived from wavelet decomposition of 
reflectance spectra displayed high correlation with pigment 
concentrations. 
  
sym8 db8 coif$ bior6.8  rbio6.8 
Chla 0.863 0.935 0.925 0.899 0.872 
Chlb 0.863 0.863 0.891 0.886 0.847 
Cars 0.637 0.743 0.486 0.761 0.715 
Chltot 0.863 0.908 0.903 0.892 0.865 
Table 1. R^ values for multiple regression models, 
deciduous broadleaves. 
Table 1. shows the coefficients of determination derived from 
multiple regression models based upon spectral decomposition 
using five particular wavelets. In all cases the coefficient of 
determination for prediction was slightly lower than the values 
depicted in the table. Other wavelets within each family 
produced lower correlations. As the table, for most wavelets, 
there were lower correlations for Cars than for the chlorophylls 
= this concurs with previous findings in investigations of other 
spectral approaches. 
881 
3.2 Bracken canopies 
Table 2. demonstrates that for bracken canopies the wavelet 
decomposition can produce regression models with high 
correlations with pigments. Again, correlations are lower for 
Cars than Chis. 
  
sym8 db8 coif$ bior6.8  rbio6.8 
Chla 0.910 0.915 0.901 0.809 0.782 
Chib 0.902 0.873 0.882 0.812 0.798 
Cars 0.686 0.732 0.505 0.675 0.701 
Chltot 70.905 0.908 0.891 0.810. 0.791 
Table 2. R? values for multiple regression models, 
bracken canopies. 
3.3 Matorral canopies 
As table 3 demonstrates, correlations derived for the matorrral 
canopies are lower than those for bracken and deciduous 
broadleaves. 
sym8 db8 coif$ bior6.8 rbio6.8 
Chla 0.760 0.785 0.801 0.695 0.608 
Chib 0.755 0.764 0.789 0.687 0.599 
Cars 0.656 0.710 0.678 0.600 0.502 
Chltot 0.758 0.772 0.702 0.692 0.600 
Table 3. R? values for multiple regression models, matorral 
canopies. 
4. CONCLUSIONS. 
This initial investigation of wavelet decomposition has revealed 
that this technique can produce results that are comparable with, 
and in some cases superior to, existing spectral approaches to 
pigment quantification from reflectance spectra. This provides 
support for further work on the technique, particularly in the 
context of testing the robustness and extendibility of the 
approach. In the first instance this can be done by combining 
the data sets of the various leaf and canopy samples used in the 
present study, then by employing additional data sets pertaining 
to a wider range of vegetation types. Radiative transfer models 
will be of particular value in providing an experimental 
platform to investigate issues which are difficult to address 
comprehensively in lab or field investigations — notably, the 
effects of viewing and illumination geometry and canopy 
architecture (i.e. LAD) on the robustness of the wavelet 
decomposition techniques, together with the consequences and 
emergent properties of many different combinations of 
biochemical and biophysical leaf and canopy characteristics, 
differing sensor characteristics and atmospheric effects. 
Refinements to the wavelet decomposition technique will be 
made through the development of automated approaches for the 
selection of appropriate wavelet basis functions, application of 
 
	        
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