A Novel Active Contours Model for Environmental Change Detection from Multitemporal Synthetic Aperture Radar Images
"> Figure 1
<p>The flowchart of our proposed model.</p> "> Figure 2
<p>The SAR data sets include before change image, after change image, and reference change maps: (<b>Row 1</b>) Yellow River Estuary; (<b>Row 2</b>) Bern data set; (<b>Row 3</b>) Ottawa data set.</p> "> Figure 3
<p>The difference images generated from four operators. (<b>a</b>) Subtraction; (<b>b</b>) Log-ratio; (<b>c</b>) normal difference; (<b>d</b>) RMLND.</p> "> Figure 4
<p>The results of the DFLAC model and the reference image <b>(Row 1)</b> Results; <b>(Row2)</b> Reference Images.</p> "> Figure 5
<p>The variation of the Kappa according to the <math display="inline"><semantics> <mi>α</mi> </semantics></math> parameter.</p> "> Figure 6
<p>The variation of the Kappa according to the <math display="inline"><semantics> <mi>β</mi> </semantics></math> parameter.</p> "> Figure 7
<p>The variation of the Kappa according to the <math display="inline"><semantics> <mi mathvariant="sans-serif">γ</mi> </semantics></math> parameter.</p> "> Figure 8
<p>The variation of the Kappa for all operators in each data set.</p> "> Figure 9
<p>The Kappa change rate with respect to the number of training data of the changed region.</p> "> Figure 10
<p>The Kappa change rate with respect to the number of training data of the unchanged region.</p> ">
Abstract
:1. Introduction
2. Materials and Methods
2.1. New Difference Image Operator
2.2. DFLAC Model
2.3. Minimization of the Energy Function
2.4. Training Data Sampling
2.5. Evaluation Indices
3. Implementation Results
3.1. Algorithm’s Workflow
- At the first step of difference image generation, two SAR images of the data set (before and after change) are introduced to the model, and the difference image is then produced based on one of Equations (1) to (4). Secondly, in the training data sampling step, a threshold T was first estimated using Otsu’s method, then, the training data of changed and unchanged classes were selected based on this threshold. In the third step, the DFLAC model was implemented. The DFLAC model starts with defining the initial curve implicitly based on a level set theory, which is a simple shape as a square and circle. Then, the evolution of the DFLAC model’s curve was done over time using Equation (17). Next, the parameters , , and were then estimated according to Equations (22), (24), and (25). These last previous steps were repeated until the curve model reached stability and was not changed (i.e., ). Finally, the output of the model was generated by separating changed regions (pixels inside the curve that ) from unchanged areas (pixels outside the curve that ).
- The accuracy assessment was the last step of the workflow, in which the error image was computed by subtracting the output image from the reference image as follows:
- Finally, the accuracy assessment of the model using the error map and some accuracy criteria, such as PCC, OE, and the Kappa, were estimated based on Equations (26)–(28).
3.2. SAR Datasets
3.3. Difference Image
3.4. Model Implementation
3.5. Accuracy of the Proposed Model
4. Discussion
4.1. Accuracy Assessment
4.1.1. The Constant parameters
4.1.2. The Difference Image Operator Type
4.1.3. Numbers of Training Data
4.2. Running Time Comparison
5. Conclusions
Author Contributions
Funding
Acknowledgments
Conflicts of Interest
References
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Data Set | Size (Pixel) | Resolution (m) | Date of the First Image | Date of the Second Image | Location | Sensor |
---|---|---|---|---|---|---|
Yellow River Estuary | 289 × 257 | 8 | June 2008 | June 2009 | Dongying, Shandong Province of China | Radarsat 2 |
Bern | 301 × 301 | 30 | April 1999 | May 1999 | a region near the city of Bern | European Remote Sensing 2 satellite |
Ottawa | 350 × 290 | 10 | July 1997 | August 1997 | Ottawa City | Radarsat 2 |
Dataset | Changed Regions | Unchanged Regions | ||||
---|---|---|---|---|---|---|
Yellow river Estuary | 127.00 | 169.67 | 212.33 | 255 | 0 | 42.167 |
Bern | 112.40 | 159.94 | 207.47 | 255 | 0 | 32.44 |
Ottawa | 127.00 | 169.67 | 212.33 | 255 | 0 | 42.17 |
Dataset | Method | PCC % | OE % | Kappa % |
---|---|---|---|---|
Yellow River Estuary | SGK | 98.06 | 1.92 | 85.24 |
NR | 88.33 | 79.99 | ||
LN-GKIT | 69.60 | 30.82 | 33.78 | |
CV | 95.37 | 4.63 | 84.38 | |
DRLSE | 90.84 | 9.16 | 69.47 | |
DFLAC | 95.49 | 4.51 | 84.65 | |
Bern | SGK | 99.68 | 0.32 | 87.05 |
NR | 99.66 | 0.34 | 85.90 | |
LN-GKIT | 99.90 | 0.35 | 85.37 | |
CV | 99.61 | 0.39 | 85.32 | |
DRLSE | 98.70 | 1.30 | 63.32 | |
DFLAC | 99.68 | 0.32 | 87.07 | |
Ottawa | SGK | 98.95 | 1.05 | 95.98 |
NR | 97.91 | 2.09 | 92.2 | |
LN-GKIT | 98.35 | 2.22 | 91.87 | |
CV | 97.06 | 2.93 | 88.92 | |
DRLSE | 95.44 | 4.56 | 81.37 | |
DFLAC | 99.00 | 1.00 | 96.26 |
Subtraction | Log-Ratio | Normal Difference | RMLND | |
---|---|---|---|---|
Yellow River Estuary | 75.22 | 83.97 | 84.71 | 84.65 |
Bern | 32.44 | 81.26 | 83.14 | 87.07 |
Ottawa | 83.81 | 95.26 | 94.92 | 96.26 |
Average | 63.82 | 86.83 | 87.59 | 89.33 |
Data Sets | DFLAC Time Steps | SGK | SGK/DFLAC | |||||
---|---|---|---|---|---|---|---|---|
1 | 2 | 3 | 4 | 5 | Total Time | |||
Yellow River Estuary | 0.01 | 0.04 | 0.01 | 8.90 | 0.01 | 8.97 | 60.53 | 6.75 |
Bern | 0.02 | 0.05 | 0.01 | 8.31 | 0.01 | 8.40 | 86.60 | 10.31 |
Ottawa | 0.02 | 0.05 | 0.02 | 9.34 | 0.01 | 9.44 | 101.17 | 10.72 |
Average | 0.02 | 0.05 | 0.01 | 8.85 | 0.01 | 8.94 | 82.77 | 9.25 |
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Ahmadi, S.; Homayouni, S. A Novel Active Contours Model for Environmental Change Detection from Multitemporal Synthetic Aperture Radar Images. Remote Sens. 2020, 12, 1746. https://doi.org/10.3390/rs12111746
Ahmadi S, Homayouni S. A Novel Active Contours Model for Environmental Change Detection from Multitemporal Synthetic Aperture Radar Images. Remote Sensing. 2020; 12(11):1746. https://doi.org/10.3390/rs12111746
Chicago/Turabian StyleAhmadi, Salman, and Saeid Homayouni. 2020. "A Novel Active Contours Model for Environmental Change Detection from Multitemporal Synthetic Aperture Radar Images" Remote Sensing 12, no. 11: 1746. https://doi.org/10.3390/rs12111746
APA StyleAhmadi, S., & Homayouni, S. (2020). A Novel Active Contours Model for Environmental Change Detection from Multitemporal Synthetic Aperture Radar Images. Remote Sensing, 12(11), 1746. https://doi.org/10.3390/rs12111746