In hyperspectral images is desirable to classify images within the conventional
frame of reference of field and laboratory observations with methods that
avoid intrinsic singular problems. In this respect, spectral mixture analysis
(SMA) has become a well established procedure for analyzing imaging
spectrometry data [17, 16, 11, 12, 3]. SMA is a structured and integrated
framework that simultaneously addresses the mixed-pixel problem, calibration,
and variations in lighting geometry and displays the results in terms of
proportions of endmembers that can be related easily to standard ecological
observational units (e.g., cover). The general form of the SMA equation
for each band is expressed as:
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(1)
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Boardman [1], used a geometric approach based on the convex hull of
the spectra projected into the mixing space to find a solution that minimized
spectral variation for some features while accentuating others. His technique
is still a SMA approach that automatically derives the number of endmembers
and estimates their pure spectral composition [1], but it is suboptimal
in the presence of multiple mixing. More recently, Harsanyi and Chang [5]
developed a mixture technique that rejects undesired interference by performing
an orthogonal subspace projection (OSP). This technique simultaneously
reduces data volume and emphasizes the presence of a signature of interest.
Bolster et al. [2] seeking the same goals, instead use the first difference
partial least squares regression (PLS) that is based on a singular
value decomposition (SVD) of the whole spectrum data set. SVD reduces
noise-related interference, common in a first difference analysis, and
reduces the analysis into a smaller set of independent variables. Both,
OSP and PLS, achieve good performance in detecting material abundances
at low levels for a particular scenario by incorporating the variability
of the material abundance into the more important independent variables
(factors) but they are unable to extend the application to other scenarios.
In order to develop a directed search methodology to locate the desired
robustness (analytic) property, Smith et al. [14] proposed a revised SMA
technique, that they termed Foreground/Background Analysis (FBA).
Harsanyi's approach shares the properties of orthogonal space projection
and a similar rationale with the FBA technique. In this technique, spectral
measurements are divided in two groups of foreground and background spectra
that comprise a selected subset of spectra which emphasizes the presence
of a signature of interest. In defining both groups they do not include
intermediate mixtures between foreground and background. In that way, FBA
vectors should be sensitive to minor sources of foreground spectral variation
and insensitive to background spectral variation. The goal of FBA is to
project spectral variation along the most relevant axis of variance that
maximizes the spectral differences between the foreground and background,
while minimizing spectral variation within each group. Their FBA approach
defines a weighting vector w = (w1 , w2
, ..., wNb), with components wb at
each channel b = 1, ..., Nb, such that all foreground spectral
vectors, Rf = (Rf,1 , Rf,2
, ..., Rf,Nb), are projected to 1 while background
spectral vectors, Rb, to 0. This property is defined
by the FBA system of equations:
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(2)
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In this paper, we present a supervised classification technique that
discriminates broad categories of materials of the surface in terms of
ground truth features, such as vegetation characteristics, and soil properties.
The actual relationships between these two ecological units are often difficult
to resolve with respect to understanding which of many potential interacting
factors is significant in a particular locality. We decompose the interaction
between the spatial and spectral domains associated to these units by using
wavelet tools and a hierarchical foreground background analysis (HFBA).
Wavelets provide spatial coherence information that should allow us to
generalize the results from the spectral features extracted by HFBA.
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(3)
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(4)
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To improve the detection of minor sources of spectral variation, we can apply the process iteratively obtaining a system of equations that works at different levels of accuracy. We stop at the level of the system noise. Solving each equation in the iteration system is the so called hierarchical FBA technique (HFBA) which derives sequentially a series of FBA vectors, with different general discriminating features. In essence, the HFBA system is an iteratively decimation process which extracts details in each of the levels.
The power of the HFBA method becomes apparent as we begin to catalogue
more precisely the performance of the SVD in energy-packing and avoidance
of overfitting problems due to its stability properties. First, r,
the rank or dimension of the matrix R, could be estimated by examining
the number of non-zero singular values [4]. Second, the decomposition R
= US V* provide an approximation of the
matrix R by a sum of rank-one matrices [4]. That is,
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(5)
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2.2 Wavelets
Wavelets are mathematical functions that split data (image or signal)
into different scale components that provide the best approximation at
each scale. The wavelet analysis starts with a function
(x),
called mother wavelet that is well localized and oscillating. By localization,
we mean
(x) decreases
rapidly to zero as x tends to infinity. Oscillating requires that
behaves as a wave, that is, integrals of
and its firsts k moments be zero.
In summary, a wavelet decomposition can be seen as an application of a pair of complementary low and high pass filters, H and G respectively. Thus, a generic wavelet transform is depicted in Figure 1.
The properties of the wavelets are determined by the properties of the
filters H and G, and by the properties of the signal being analyzed. The
construction of wavelets then begins by designing the filters that could
be a basis of the space we want to transform. To lead to high compression
and get coherent information we use a coi ets with 4 vanishing moments,
avoiding at the same time to include noise into the estimated generalization
functional,
.
The statistics of the prediction indicates the good performance of HFBA
at the laboratory level: regressions of 0.71 and 0.75 with good fit of
the distribution of actual data.
It can be observed that the two spectral areas most important for discrimination
are between 1000nm and 2200nm (OH-AL and Mg-OH absorptions). The characteristic
of the vector between 600 and 800 nm also could be used to detect vegetation
and it will work like NDVI for this purpose. The first image in Figure
5 shows the HFBA spatial distribution. After applying coi et wavelets
(Figure 5, second row), the spatial coherence
is manifested and this allows noise reduction and improves the performance
of HFBA vectors. The final classification allows a better interpretation
of the ecological processes involved. Image classification follows known
spatial characteristics. Finally, Figure 6
shows the organic matter spatial distribution from AVIRIS data predicted
by HFBA and coi et noise reduction. High values are concentrated near ridges
of the mountains as expected. It can be observed that the pixels mapped
as La Jolla soils in the classification image also show high content of
organic matter which agrees with our laboratory data.
The power of the HFBA technique is based on the attractive properties of the SVD transform in information packing and avoidance of overfitting problems by minimizing extraneous noise in the analysis. The technique was trained over laboratory data and applied to AVIRIS images. It is clear from the above experiments that the proposed approach is promising.
By the iterative hierarchical procedure we force the system to account for important non-linear dependencies directly related to spectral scaling. In that respect, one of the strong points of the proposed method is that we can group together samples with similar anatomical properties manifested spectrally. However, if the distribution of these properties is continuous, samples near the boundaries of the discriminant regions could be misclassified weakening the helpfulness of the classification step. In particular, as spatial variation of vegetation is high, the selection of a training set that explains the mixing presented at different spatial scales is critical. This process seems to be a key factor for understanding the good performance of HFBA dealing with sub-pixel scaling issues in this application, although HFBA was not properly equipped to deal directly with these spatial issues. There are more appropriate image analysis methodologies concerning spatial scaling problems such as wavelet transforms. The wavelet decomposition gives a better representation of spatial distribution (at different scales) of the data, and especially a better description of the properties of samples near to discriminant boundaries. Clearly, these points have to be further investigated to identify the relationship between spatial-spectral scales.
As a conclusion, we consider that a combination of HFBA and wavelets
or other spatial scaling transforms has significant potential and certainly
deserves further investigation. There are many aspects for the discrimination
among materials that still need investigation. The aspects we have in mind
are aptly illustrated by Yves Meyer in his book Wavelets: algorithms
and applications [6]: "It is notable that Mandelbrot used the word
describe and not explain or interpret. We are going to follow him in this,
ostensibly, very modest approach. This is our answer to the problem about
the objectives of the choices: Wavelets, whether they are of the time-scale
or time-frequency type, will not help us to explain scientific facts, but
they will serve to describe the reality around us, whether or not it is
scientific. Our task is to optimize the description. This means that
we must make the best use of the resources allocated to us to obtain the
most precise possible description."
[2] K. L. Bolster, M. E. Martin, and J. D. Aber. Determination of Carbon fraction and Nitrogen concentration in tree foliage by near infrared reflectance: a comparison of statistical methods. Can. J. For. Res., 26:590-600, 1996.
[3] J. A. Gamon, C. B. Field, D. A. Roberts, S. L. Ustin, and R. Valentini. Functional patterns in an annual grassland during an AVIRIS overflight. Remote Sensing of Environment, 44(2):239-253, 1993.
[4] G. H. Golub and C. F. Van Loan. Matrix Computations. John Hopkins University Press, Baltimore, Maryland, 1989.
[5] J. C. Harsanyi and C. I. Chang. Hyperspectral image classification and dimensionality reduction: an orthogonal subspace projection approach. IEEE Transactions on Geoscience and Remote Sensing, 32(4):779-785, 1994.
[6] Y. Meyer. Wavelets: Algorithms and Applications. SIAM press, Philadelphia, 1993.
[7] J. E. Pinzón. Applications of spectrometry to vegetation studies using hierarchical foreground/background analysis. Master's thesis, University of California, Davis, June 1996. Master degree.
[8] J. E. Pinzón, S. L. Ustin, C. M. Castañeda, and M. O. Smith. Investigation of leaf biochemistry by hierarchical foreground/background analysis. IEEE Transactions on Geoscience and Remote Sensing, 36:1-15.
[9] J. E. Pinzón, S. L. Ustin, Q. L. Hart, S. Jacquemoud, and M. O. Smith. Using foreground/background analysis to determine leaf and canopy chemistry. In R. O. Green, editor, Proc. 5th. annual JPL Airborne Earth Science Workshop: AVIRIS Workshop, Jan 23-27, 1995, vol. 95-1, pp. 129-132, 1995.
[10] J. E. Pinzón, S. L. Ustin, Q. L. Hart, S. Jacquemoud, and M. O. Smith. Comparison of multivariate statistical techniques for estimating vegetation parameter. In Spectral Analysis Workshop: The Use of Vegetation as an Indicator of Environmental Contamination, Reno, Nevada, Nov 9-10, 1994.
[11] D. A. Roberts, J. B. Adams, and M. O. Smith. Predicted distribution of visible and near infrared radiant flux above and below a transmittant leaf. Remote Sensing of Environment, 34:1-17, 1990.
[12] D. E. Sabol, J. B. Adams, and M. O. Smith. Predicting the spectral detectability of surface materials using spectral mixture analysis. In Proceedings of the IEEE International Geoscience Remote Sensing Symposium 1990, volume 2, pages 967-970, 1990.
[13] D. E. Sabol, J. B. Adams, and M. O. Smith. Quantitative subpixel spectral detection of targets in multispectral images. Journal of Geophysical Research, 97(E2):2659-2672, 1992.
[14] M. O. Smith, D. A. Roberts, J. Hill, W. Mehl, B. Hosgood, J. Venderbout, G. Schmuck, C. Koechler, and J. Adams. A new approach to quantifying abundancies of materials in multispectral images. In IGARSS 94: Proceedings International Geosciences Remote Sensing Symposium, volume 4, pages 2372-2374, 1994.
[15] M. O. Smith, R. Weeks, and A. Gillespie. Using background factors to optimize roughness estimates from multipolarized SAR images. In ERIM 96: Second International Airborne Remote Sensing Conference and Exhibition, San Francisco, volume 1, 24-27 June, 1996.
[16] S. L. Ustin, Q. J. Hart, G. Scheer, and L. Duan. Estimating dry grass biomass residues using AVIRIS image analysis. In IGARSS 94: Proceedings International Geosciences Remote Sensing Symposium, volume 2, pages 1211-1212, 1994.
[17] S. L. Ustin, M. O. Smith, and J. B. Adams. Remote sensing of ecological processes: A strategy for developing and testing ecological models using spectral mixture analysis. In J. R. Ehleringer and C. B. Field, editors, Scaling Physiological Processes: Leaf to Globe, pages 339-357, San Diego, 1993. Academic Press.
[18] M. V. Wickerhauser. Adapted wavelet analysis from theory to software. A. K. Peters, Ltd., Wellesley, MA, 1994.