Crop Classification in Satellite Images through Probabilistic Segmentation Based on Multiple Sources †
Abstract
:1. Introduction
2. Previous Works
3. The Proposal
3.1. Training Stage
3.2. Segmentation Stage through Multiples Sources and Probabilistic Approach
- For a given image, we compute the feature spaces provided by the mapping , .
- Then, the likelihood is assigned according to the following equationsuch that , , . The likelihood is obtained by normalizing with respect to the classes.
- Here we propose a robust GMMF approach that generalizes the proposal in [28] including more feature spaces and with weight functions in both the data and regularization terms. Equations (10)–(12) indicate the modifications.where is an uncertainty measure of the information source f at pixel r, for example, the measure of entropy (5) used in [28]; is the regularization parameter, controls the relative importance of the likelihood for different sources. When is very large, the contribution of the likelihood for all sources tends to be the same and when it is close to zero, the functional in (10) tends to select the likelihood corresponding to the lowest uncertainty, i.e., this tends to the solution proposed in [28] when using the entropy as uncertainty measure. The weight function allows to control the edges between classes, here we usesuch that if the sites very probably belong to the same class and otherwise. The solution of the optimization problem (10) yields the following Gauss-Seidel scheme:which is similar to the Gauss-Seidel scheme (2), but now the term , Equation (14), is a mixture term that allows us to combine or fuse different likelihoods. In addition, the above formula also includes function weights to control the edges between classes. Note that, the first term in the numerator of the Equation (15) is a convex linear combination of likelihoods derived from different sources. Feature spaces with lower uncertainty have a greater and therefore they have a greater contribution to the data term in Equation (10).
3.3. Validation
4. Experiments and Discussion
4.1. Study Area
4.2. Data Sources
4.3. Studied Feature Spaces
- Space 2: it contains the first three principal components from the PCA applied on 10 vegetation indices, see Table 3. Such indices are based on mathematical operations on spectral bands and they allow to enhance the information related to vegetation. In order to compute the indices we calculate the reflectance values, , corresponding to the acquired images, using the algorithms in [48], see also the procedures given in [49,50,51,52]. The included indices appear in Table 3. Symbols , , and denote the reflectance values for the red, blue, green and infrared bands respectively. We followed the recommendation given in [35], and set to compute the SAVI and SARVI expressions. For SARVI we considered as authors in [34].
- Space 3: this space contains three principal components from PCA applied on the spectral bands TM1, TM2, TM3, TM4, TM5 and TM7, see Table 2. Although TM2, TM3 and TM4 bands more accurately describes information related to vegetation [30], in this investigation PCA on all six mentioned bands is applied in order to include information from other spectral regions.
4.4. Comparison Measures
4.5. Results and Discussion
5. Conclusions
Acknowledgments
Author Contributions
Conflicts of Interest
References
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| Class | Vegetation Name |
|---|---|
| C1 | Irrigation agriculture |
| C2 | Temporary agriculture |
| C3 | Forest |
| C4 | Scrub |
| C5 | Pastureland |
| TM Bands | Wavelength () | Features |
|---|---|---|
| TM1 | 0.45–0.52 | B (Blue) |
| TM2 | 0.52–0.60 | G (Green) |
| TM3 | 0.63–0.69 | R (Red) |
| TM4 | 0.76–0.90 | near infrared |
| TM5 | 1.55–1.75 | mid-infrared |
| TM6 | 10.4–12.50 | thermal infrared |
| TM7 | 2.08–2.35 | mid-infrared |
| Name VI | Formula | References |
|---|---|---|
| MSR | [31] | |
| CI | [32] | |
| midrule NDVI | [15] | |
| GNDVI | [16] | |
| EVI | [33] | |
| SARVI | [34] | |
| RDVI | [31] | |
| SAVI | [35] | |
| MSAVI | [36] | |
| WDRVI | [37] |
| Cohen’s Kappa | Interpretation |
|---|---|
| <0 | Poor agreement |
| 0.00–0.20 | Slight agreement |
| 0.21–0.40 | Fair agreement |
| 0.41–0.60 | Moderate agreement |
| 0.61–0.80 | Substantial agreement |
| 0.81–1.00 | Almost perfect agreement |
| N. Combination | Feature Space Combination |
|---|---|
| 1 | Space 1 |
| 2 | Space 2 |
| 3 | Space 3 |
| 4 | Space 1 + Space 2 |
| 5 | Space 1 + Space 3 |
| 6 | Space 2 + Space 3 |
| 7 | Space 1 + Space 2 + Space 3 |
| Experiment | Precision | Overall Accuracy | Cohen’s Kappa | ||||
|---|---|---|---|---|---|---|---|
| C1 | C2 | C3 | C4 | C5 | |||
| 1 | 0.86 | 0.83 | 0.89 | 0.85 | 0.63 | 0.8331 | 0.7520 |
| 2 | 0.84 | 0.81 | 0.89 | 0.87 | 0.62 | 0.8324 | 0.7528 |
| 3 | 0.83 | 0.82 | 0.91 | 0.89 | 0.65 | 0.8506 | 0.7801 |
| Experiment | Precision | Overall Accuracy | Cohen’s Kappa | ||||
|---|---|---|---|---|---|---|---|
| C1 | C2 | C3 | C4 | C5 | |||
| 4 | 0.86 | 0.83 | 0.92 | 0.87 | 0.67 | 0.8472 | 0.7726 |
| 5 | 0.89 | 0.84 | 0.94 | 0.88 | 0.70 | 0.8624 | 0.7955 |
| 6 | 0.85 | 0.83 | 0.91 | 0.89 | 0.64 | 0.8485 | 0.7770 |
| 7 | 0.87 | 0.84 | 0.93 | 0.88 | 0.67 | 0.8588 | 0.7904 |
| Experiment | Precision | Overall Accuracy | Cohen’s Kappa | ||||
|---|---|---|---|---|---|---|---|
| C1 | C2 | C3 | C4 | C5 | |||
| 8 | 0.88 | 0.83 | 0.92 | 0.87 | 0.67 | 0.8497 | 0.7767 |
| 9 | 0.90 | 0.84 | 0.94 | 0.89 | 0.71 | 0.8649 | 0.7993 |
| 10 | 0.88 | 0.82 | 0.91 | 0.89 | 0.66 | 0.8517 | 0.7812 |
| 11 | 0.90 | 0.83 | 0.93 | 0.89 | 0.69 | 0.8600 | 0.7923 |
| Method | Feature Space | C1 | C2 | C3 | C4 | C5 | Overall Accuracy | Kappa |
|---|---|---|---|---|---|---|---|---|
| MED [61] | Landsat-5 TM | 0.82 | 0.73 | 0.54 | 0.80 | 0.29 | 0.6244 | 0.4781 |
| ML [62] | Landsat-5 TM | 0.65 | 0.73 | 0.72 | 0.76 | 0.40 | 0.6928 | 0.5558 |
| FLL [63] | Landsat-5 TM | 0.88 | 0.74 | 0.71 | 0.75 | 0.46 | 0.7105 | 0.5743 |
| ESS [60] | Landsat-5 TM | 0.76 | 0.70 | 0.80 | 0.74 | 0.56 | 0.7257 | 0.5811 |
| SVM linear | Landsat-5 TM | 0.77 | 0.74 | 0.96 | 0.73 | 0.19 | 0.7498 | 0.6071 |
| SVM rbf | Landsat-5 TM | 0.79 | 0.83 | 0.90 | 0.90 | 0.66 | 0.8536 | 0.7859 |
| MICAI 2014 [29] | Space 1 | 0.86 | 0.83 | 0.89 | 0.85 | 0.63 | 0.8331 | 0.7520 |
| MICAI | Space 3 | 0.83 | 0.82 | 0.91 | 0.89 | 0.65 | 0.8506 | 0.7801 |
| MICAI 2015 [28] | Spaces 1 & 2 | 0.86 | 0.83 | 0.92 | 0.87 | 0.67 | 0.8472 | 0.7726 |
| MICAI | Spaces 1 & 3 | 0.89 | 0.84 | 0.94 | 0.88 | 0.70 | 0.8624 | 0.7955 |
| Proposal | Spaces 1 & 3 | 0.90 | 0.84 | 0.94 | 0.89 | 0.71 | 0.8649 | 0.7993 |
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Dalmau, O.S.; Alarcón, T.E.; Oliva, F.E. Crop Classification in Satellite Images through Probabilistic Segmentation Based on Multiple Sources. Sensors 2017, 17, 1373. https://doi.org/10.3390/s17061373
Dalmau OS, Alarcón TE, Oliva FE. Crop Classification in Satellite Images through Probabilistic Segmentation Based on Multiple Sources. Sensors. 2017; 17(6):1373. https://doi.org/10.3390/s17061373
Chicago/Turabian StyleDalmau, Oscar S., Teresa E. Alarcón, and Francisco E. Oliva. 2017. "Crop Classification in Satellite Images through Probabilistic Segmentation Based on Multiple Sources" Sensors 17, no. 6: 1373. https://doi.org/10.3390/s17061373
APA StyleDalmau, O. S., Alarcón, T. E., & Oliva, F. E. (2017). Crop Classification in Satellite Images through Probabilistic Segmentation Based on Multiple Sources. Sensors, 17(6), 1373. https://doi.org/10.3390/s17061373

