Impacts of Resampling and Downscaling Digital Elevation Model and Its Morphometric Factors: A Comparison of Hopfield Neural Network, Bilinear, Bicubic, and Kriging Interpolations
Abstract
:1. Introduction
2. Method and Data Used
2.1. Method Used
2.1.1. Hopfield Neural Network
2.1.2. Bilinear Interpolation Method
2.1.3. Bi-Cubic Interpolation Method
2.1.4. Kriging Interpolation Method
2.2. Data Used
2.3. Morphometric Factors
2.3.1. Slope and Aspect
2.3.2. Plan Curvature and Profile Curvature
2.3.3. Topographic Wetnet Index
2.4. Accuracy Assessment
3. Results and Discussion
3.1. Results of Downscaling and Resampling of the Digital Elevation Model
3.2. Slopes of the Resampled and Downscaled Digital Elevation Models
3.3. Aspects of the Resampled and Downscaled Digital Elevation Models
3.4. Plan Curvatures and Profile Curvatures of the Resampled and Downscaled Digital Elevation Models
3.5. Topographic Wetness Index of the Resampled and Downscaled Digital Elevation Models
3.6. Relationship between the Accuracy Improvement of Resampled Digital Elevation Model and Topographic Factors
4. Conclusions
- Both bi-cubic and HNN downscaling outperform Kriging and bilinear resampling techniques. Specifically, the results suggest that HNN has a slight advantage over bi-cubic resampling.
- Resampling approaches applied to DEMs have demonstrated their effectiveness in enhancing the quality of their derived derivatives, with remarkable improvements observed in the first derivatives of slope and aspect, as indicated by the reduction in RMSEs and other statistical metrics.
- Resampling techniques from low to medium resolutions have proven valuable in enhancing the accuracy of second derivatives, including plan and profile curvatures and the TWI. The resampling and downscaling approaches have shown their capability to improve the accuracy of these topographic factors, as evident in the results. However, the improvement of DEM’s accuracy, as indicated by reduced RMSEs, does not translate into enhancing accuracy for the second group of medium-to-high-resolution DEM data. Therefore, further investigations are required to understand the impacts of resampling and downscaling of DEMs from medium to high resolutions.
- Future investigations should be undertaken to explore the impacts of the other downscaling methods, such as deep learning for downscaling, which has been proven to positively impact to DEM’s accuracy enhancement recently. In addition, the direct downscaling of topographic factors, especially of the second derivatives such as curvatures and TWI, from lower resolution to higher resolution, also should be evaluated to find the best solutions for enhancing their accuracy.
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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DEM Datasets | Resolution of Reference DEM | Vertical Accuracy (RMSE) | Resolution before Resampling | Zoom Factor |
---|---|---|---|---|
30 m SRTM DEM in Nghe An Province | 30 m | 9.0 m | 90 m | 3 |
20 m DEM in Nghe An Province from a topographic map | 20 m | 7.5 m | 60 m | 4 |
5 m DEM in Lang Son Province from ground survey | 5 m | 0.5 m | 20 m | 4 |
10 m DEM in Kon Tum Province from a topographic map | 10 m | 1.2 m | 30 m | 3 |
5 m DEM in Cao Bang Province from photogrammetry | 5 m | 0.5 m | 20 m | 4 |
DEM Datasets | Resampling Method | RMSE (m) |
---|---|---|
Dataset 1: SRTM 30 m DEM in Nghe An Province | No resample (90 m) | 7.86 |
Bilinear | 4.96 | |
Bi-cubic | 3.72 | |
Kriging | 8.16 | |
HNN | 3.54 | |
Dataset 2: 20 m DEM in Nghe An Province from topographic map | No resample (60 m) | 5.82 |
Bilinear | 3.39 | |
Bi-cubic | 2.54 | |
Kriging | 7.07 | |
HNN | 2.61 | |
Dataset 3: 5 m DEM in Lang Son Province from ground survey | No resample (20 m) | 2.44 |
Bilinear | 1.27 | |
Bi-cubic | 1.14 | |
Kriging | 1.32 | |
HNN | 1.21 | |
Dataset 4: 10 m DEM in Kon Tum Province from topographic map | No resample (30 m) | 0.49 |
Bilinear | 0.57 | |
Bi-cubic | 0.38 | |
Kriging | 1.06 | |
HNN | 0.39 | |
Dataset 5: 5 m DEM in Cao Bang Province from photogrammetry | No resample (20 m) | 1.32 |
Bilinear | 0.83 | |
Bi-cubic | 0.65 | |
Kriging | 1.06 | |
HNN | 0.64 |
DEM Datasets | Resampling Method | Min | Max | Mean | RMSE | MAE |
---|---|---|---|---|---|---|
Dataset 1 | No resample (90 m) | 0.12 | 24.40 | 9.88 | 6.98 | 5.55 |
Bilinear | 0.05 | 34.29 | 12.03 | 4.10 | 3.19 | |
Bi-cubic | 0.03 | 37.34 | 12.85 | 3.27 | 2.46 | |
Kriging | 0.37 | 27.78 | 10.21 | 6.18 | 4.98 | |
HNN | 0.08 | 37.68 | 12.98 | 3.10 | 2.33 | |
Reference | 0.11 | 44.49 | 14.75 | |||
Dataset 2 | No resample (60 m) | 0.00 | 32.91 | 11.76 | 7.18 | 5.41 |
Bilinear | 0.00 | 40.95 | 13.52 | 4.86 | 3.43 | |
Bi-cubic | 0.00 | 44.73 | 14.26 | 4.13 | 2.80 | |
Kriging | 0.00 | 30.31 | 10.86 | 7.83 | 5.97 | |
HNN | 0.00 | 43.89 | 14.13 | 4.18 | 2.86 | |
Reference | 0.00 | 57.57 | 15.80 | |||
Dataset 3 | No resample (20 m) | 0.28 | 38.05 | 17.66 | 8.47 | 5.97 |
Bilinear | 0.00 | 37.57 | 16.70 | 7.90 | 6.09 | |
Bi-cubic | 0.00 | 40.00 | 17.35 | 7.60 | 5.77 | |
Kriging | 0.33 | 34.78 | 16.83 | 7.50 | 5.76 | |
HNN | 0.15 | 46.18 | 18.82 | 7.60 | 5.22 | |
Reference | 0.00 | 60.55 | 19.54 | |||
Dataset 4 | No resample (30 m) | 0.00 | 37.88 | 7.85 | 2.53 | 1.58 |
Bilinear | 0.00 | 41.23 | 7.91 | 1.81 | 1.08 | |
Bi-cubic | 0.00 | 42.91 | 8.06 | 1.51 | 0.88 | |
Kriging | 0.00 | 41.79 | 7.97 | 1.65 | 1.00 | |
HNN | 0.00 | 43.24 | 8.07 | 1.42 | 0.86 | |
Reference | 0.00 | 53.16 | 8.23 | |||
Dataset 5 | No resample (20 m) | 0.33 | 30.53 | 10.40 | 2.92 | 2.08 |
Bilinear | 0.07 | 31.42 | 10.40 | 3.27 | 2.16 | |
Bi-cubic | 0.07 | 36.89 | 10.64 | 2.61 | 1.87 | |
Kriging | 0.11 | 35.40 | 10.61 | 2.83 | 1.94 | |
HNN | 0.01 | 37.96 | 10.70 | 2.58 | 1.86 | |
Reference | 0.12 | 47.00 | 11.05 |
DEM Datasets | Resampling Method | RMSE (Degree) | Groups of Difference in Aspect Values (%) | ||||
---|---|---|---|---|---|---|---|
0–10° | 10–20° | 20–45° | 45–90° | 90–180° | |||
Dataset 1 | No resample (90 m) | 40.73 | 27.60% | 23.31% | 30.67% | 13.76% | 4.66% |
Bilinear | 23.88 | 49.49% | 27.11% | 18.22% | 4.00% | 1.18% | |
Bi-cubic | 21.21 | 57.83% | 24.57% | 13.73% | 2.94% | 0.93% | |
Kriging | 32.20 | 33.74% | 26.66% | 28.52% | 8.70% | 2.39% | |
HNN | 20.21 | 59.63% | 24.20% | 12.86% | 2.50% | 0.80% | |
Dataset 2 | No resample (60 m) | 34.45 | 33.66% | 25.87% | 28.45% | 9.24% | 2.78% |
Bilinear | 31.91 | 51.92% | 26.91% | 16.40% | 3.72% | 0.76% | |
Bi-cubic | 20.41 | 59.27% | 23.66% | 13.25% | 3.04% | 0.49% | |
Kriging | 31.91 | 32.47% | 25.40% | 30.58% | 9.51% | 2.05% | |
HNN | 20.35 | 59.93% | 23.23% | 12.79% | 3.42% | 0.64% | |
Dataset 3 | No resample (20 m) | 41.83 | 55.56% | 23.05% | 11.11% | 3.70% | 6.58% |
Bilinear | 38.04 | 55.14% | 20.99% | 13.17% | 5.35% | 5.35% | |
Bi-cubic | 37.80 | 57.61% | 20.58% | 11.93% | 4.53% | 5.35% | |
Kriging | 32.66 | 59.67% | 16.87% | 13.17% | 4.94% | 5.35% | |
HNN | 33.53 | 60.49% | 21.40% | 10.70% | 2.47% | 4.94% | |
Dataset 4 | No resample (30 m) | 17.08 | 71.92% | 16.86% | 8.59% | 2.11% | 0.52% |
Bilinear | 13.20 | 81.33% | 12.06% | 5.06% | 1.30% | 0.25% | |
Bi-cubic | 11.42 | 86.78% | 8.27% | 3.90% | 0.83% | 0.22% | |
Kriging | 11.90 | 83.99% | 10.46% | 4.43% | 0.89% | 0.22% | |
HNN | 11.03 | 87.19% | 8.29% | 3.56% | 0.75% | 0.21% | |
Dataset 5 | No resample (20 m) | 21.70 | 55.26% | 25.02% | 15.42% | 3.39% | 0.92% |
Bilinear | 20.52 | 57.70% | 24.41% | 14.14% | 2.97% | 0.79% | |
Bi-cubic | 19.63 | 59.85% | 23.57% | 13.24% | 2.64% | 0.70% | |
Kriging | 19.51 | 60.06% | 23.78% | 12.87% | 2.59% | 0.70% | |
HNN | 19.72 | 59.64% | 23.70% | 13.27% | 2.67% | 0.72% |
DEM Datasets | Resampling Method | Plan Curvature RMSE (m−1) | Profile Curvature RMSE (m−1) | Plan Curvature Classification | Profile Curvature Classification | ||
---|---|---|---|---|---|---|---|
Incorrect | Correct | Incorrect | Correct | ||||
Dataset 1 | No resample (90 m) | 0.01983 | 0.00169 | 46.30% | 53.70% | 43.68% | 56.32% |
Bilinear | 0.02173 | 0.00145 | 37.05% | 62.95% | 35.70% | 64.30% | |
Bi-cubic | 0.02556 | 0.00125 | 32.71% | 67.29% | 30.10% | 69.90% | |
Kriging | 0.02276 | 0.00193 | 46.96% | 53.04% | 44.60% | 55.40% | |
HNN | 0.01915 | 0.00125 | 31.97% | 68.03% | 29.75% | 70.25% | |
Dataset 2 | No resample (60 m) | 0.02255 | 0.00441 | 51.23% | 48.77% | 68.46% | 31.54% |
Bilinear | 0.02296 | 0.00439 | 51.00% | 49.00% | 67.08% | 32.92% | |
Bi-cubic | 0.02789 | 0.00419 | 48.76% | 51.24% | 66.09% | 33.91% | |
Kriging | 0.02296 | 0.00451 | 51.76% | 48.24% | 67.39% | 32.61% | |
HNN | 0.02789 | 0.00411 | 42.45% | 57.55% | 38.56% | 61.44% | |
Dataset 3 | No resample (20 m) | 0.07113 | 0.01512 | 44.44% | 55.56% | 51.39% | 48.61% |
Bilinear | 0.09452 | 0.01623 | 47.58% | 52.42% | 50.40% | 49.60% | |
Bi-cubic | 0.13607 | 0.01626 | 44.41% | 55.59% | 47.30% | 52.70% | |
Kriging | 0.13293 | 0.10244 | 45.20% | 54.80% | 50.06% | 49.94% | |
HNN | 0.06833 | 0.01539 | 44.28% | 55.72% | 46.89% | 53.11% | |
Dataset 4 | No resample (30 m) | 0.07390 | 0.00248 | 33.71% | 66.29% | 30.14% | 69.86% |
Bilinear | 0.05973 | 0.00272 | 42.07% | 57.93% | 33.23% | 66.77% | |
Bi-cubic | 0.04798 | 0.00223 | 32.71% | 67.29% | 27.06% | 72.94% | |
Kriging | 0.10244 | 0.00244 | 37.85% | 62.15% | 30.35% | 69.65% | |
HNN | 0.05147 | 0.00225 | 34.64% | 65.36% | 27.41% | 72.59% | |
Dataset 5 | No resample (20 m) | 0.04446 | 0.00454 | 50.26% | 49.74% | 66.40% | 33.60% |
Bilinear | 0.04561 | 0.00460 | 52.13% | 47.13% | 66.75% | 32.87% | |
Bi-cubic | 0.04522 | 0.00448 | 63.25% | 36.75% | 60.48% | 39.52% | |
Kriging | 0.04668 | 0.04668 | 47.51% | 52.49% | 62.04% | 37.96% | |
HNN | 0.04671 | 0.00449 | 66.40% | 33.60% | 59.69% | 40.31% |
DEM Datasets | Resampling Method | RMSE | MAE |
---|---|---|---|
Dataset 1 | No resample (90 m) | 1.499 | 0.985 |
Bilinear | 0.419 | 0.551 | |
Bi-cubic | 0.362 | 0.491 | |
Kriging | 0.591 | 0.686 | |
HNN | 0.334 | 0.475 | |
Dataset 2 | No resample (60 m) | 2.235 | 1.393 |
Bilinear | 1.016 | 0.754 | |
Bi-cubic | 0.994 | 0.731 | |
Kriging | 1.244 | 0.891 | |
HNN | 2.155 | 1.075 | |
Dataset 3 | No resample (20 m) | 2.341 | 1.023 |
Bilinear | 2.694 | 1.473 | |
Bi-cubic | 2.687 | 1.466 | |
Kriging | 2.683 | 1.469 | |
HNN | 2.657 | 1.446 | |
Dataset 4 | No resample (30 m) | 2.635 | 1.422 |
Bilinear | 2.086 | 0.993 | |
Bi-cubic | 2.699 | 1.431 | |
Kriging | 2.683 | 1.430 | |
HNN | 2.739 | 1.440 | |
Dataset 5 | No resample (20 m) | 3.538 | 1.837 |
Bilinear | 1.072 | 0.848 | |
Bi-cubic | 0.969 | 0.796 | |
Kriging | 1.114 | 0.870 | |
HNN | 0.960 | 0.791 |
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Minh, N.Q.; Huong, N.T.T.; Khanh, P.Q.; Hien, L.P.; Bui, D.T. Impacts of Resampling and Downscaling Digital Elevation Model and Its Morphometric Factors: A Comparison of Hopfield Neural Network, Bilinear, Bicubic, and Kriging Interpolations. Remote Sens. 2024, 16, 819. https://doi.org/10.3390/rs16050819
Minh NQ, Huong NTT, Khanh PQ, Hien LP, Bui DT. Impacts of Resampling and Downscaling Digital Elevation Model and Its Morphometric Factors: A Comparison of Hopfield Neural Network, Bilinear, Bicubic, and Kriging Interpolations. Remote Sensing. 2024; 16(5):819. https://doi.org/10.3390/rs16050819
Chicago/Turabian StyleMinh, Nguyen Quang, Nguyen Thi Thu Huong, Pham Quoc Khanh, La Phu Hien, and Dieu Tien Bui. 2024. "Impacts of Resampling and Downscaling Digital Elevation Model and Its Morphometric Factors: A Comparison of Hopfield Neural Network, Bilinear, Bicubic, and Kriging Interpolations" Remote Sensing 16, no. 5: 819. https://doi.org/10.3390/rs16050819
APA StyleMinh, N. Q., Huong, N. T. T., Khanh, P. Q., Hien, L. P., & Bui, D. T. (2024). Impacts of Resampling and Downscaling Digital Elevation Model and Its Morphometric Factors: A Comparison of Hopfield Neural Network, Bilinear, Bicubic, and Kriging Interpolations. Remote Sensing, 16(5), 819. https://doi.org/10.3390/rs16050819