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Research Article

Fine-grained wetland classification for national wetland reserves using multi-source remote sensing data and Pixel Information Expert Engine (PIE-Engine)

ORCID Icon, , ORCID Icon, , , , , , , , , & show all
Article: 2286746 | Received 16 Jul 2023, Accepted 09 Nov 2023, Published online: 27 Nov 2023

Figures & data

Figure 1. The framework for wetland classification and analysis.

Figure 1. The framework for wetland classification and analysis.

Figure 2. Locations of five national wetland reserves in China. (a) Site 1 (Guangxi Beilun Estuary National Nature Reserve), (b) Site 2 (Yancheng National Nature Reserve), (c) Site 3 (Mai Po Marshes and Inner Deep Bay), (d) Site 4 (Zhalong), (e) Site 5 (Lalu National Nature Reserve). Google Earth imagery is shown in the background.

Figure 2. Locations of five national wetland reserves in China. (a) Site 1 (Guangxi Beilun Estuary National Nature Reserve), (b) Site 2 (Yancheng National Nature Reserve), (c) Site 3 (Mai Po Marshes and Inner Deep Bay), (d) Site 4 (Zhalong), (e) Site 5 (Lalu National Nature Reserve). Google Earth imagery is shown in the background.

Table 1. The wetland classification system used in this study.

Table 2. The detailed information of data utilized in this study.

Figure 3. Geographical distribution of the wetland sample set over China. The pie charts show the detailed distribution of wetland and non-wetland samples among categories.

Figure 3. Geographical distribution of the wetland sample set over China. The pie charts show the detailed distribution of wetland and non-wetland samples among categories.

Figure 4. The conception of the multi-stage wetland classification.

Figure 4. The conception of the multi-stage wetland classification.

Table 3. Pixel-based features adopted for wetland classification.

Table 4. Object-based features adopted for wetland classification.

Figure 5. The architecture of ensemble learning with multi-layer stacking strategy, shown here with n types of base classifiers and 2 stack layers.

Figure 5. The architecture of ensemble learning with multi-layer stacking strategy, shown here with n types of base classifiers and 2 stack layers.

Table 5. Comparison results of different classifiers according to first-stage pixel-based classification accuracy and running time×.

Table 6. Comparison results of different classifiers according to second-stage object-based classification accuracy and running time×.

Table 7. Overall wetland classification accuracy of the proposed multi-stage method.

Figure 6. The relative importance of features for (a) pixel-based classification and (b) object-based classification. Note: explanations of feature names can be found in . Suffixes in the feature names such as p50 and p75 denote quantile values. Suffixes including diss, contrast, var, and savg, refer to dissimilarity, contrast, variation, and sum average features. The suffix ‘_4’ stands for the wettest composites. Features including latsin, latcos, lonsin, and loncos represent sine and cosine values of latitude and longitude.

Figure 6. The relative importance of features for (a) pixel-based classification and (b) object-based classification. Note: explanations of feature names can be found in Tables 3 and 4. Suffixes in the feature names such as p50 and p75 denote quantile values. Suffixes including diss, contrast, var, and savg, refer to dissimilarity, contrast, variation, and sum average features. The suffix ‘_4’ stands for the wettest composites. Features including latsin, latcos, lonsin, and loncos represent sine and cosine values of latitude and longitude.

Table 8. Comparison of pixel-based classification accuracy with different combinations of features×.

Table 9. Comparison of object-based classification accuracy with different combinations of features×.

Figure 7. The wetland mapping results of five national wetland reserves in 2021. (a) Site 1, (b) Site 2, (c) Site 3, (d) Site 4, (e) Site 5. Figures in the first and second columns are Sentinel-2 and Sentinel-1 composite images in 2021, respectively.

Figure 7. The wetland mapping results of five national wetland reserves in 2021. (a) Site 1, (b) Site 2, (c) Site 3, (d) Site 4, (e) Site 5. Figures in the first and second columns are Sentinel-2 and Sentinel-1 composite images in 2021, respectively.

Figure 8. Comparison of global and local classifiers across five national wetland reserves using overall accuracy.

Figure 8. Comparison of global and local classifiers across five national wetland reserves using overall accuracy.

Figure 9. Comparison of our wetland mapping results, CAS_wetlands, and FROM-GLC10 in selected locations. (a) centered at 109.5°E, 21.5°N; (b) centered at 114.0°E, 22.5°N; (c) centered at 109.7°E, 21.6°N; (d) centered at 121.0°E, 33.0°N. Figures in the first column are Google Earth images.

Figure 9. Comparison of our wetland mapping results, CAS_wetlands, and FROM-GLC10 in selected locations. (a) centered at 109.5°E, 21.5°N; (b) centered at 114.0°E, 22.5°N; (c) centered at 109.7°E, 21.6°N; (d) centered at 121.0°E, 33.0°N. Figures in the first column are Google Earth images.

Figure 10. Comparison in classification accuracy of single-stage pixel-based method and our proposed multi-stage method. Class-level accuracies are F1 scores.

Figure 10. Comparison in classification accuracy of single-stage pixel-based method and our proposed multi-stage method. Class-level accuracies are F1 scores.

Figure 11. Sample robustness to size reduction and errors based on pixel-based ensemble learning classifier. Variation of the mean overall accuracy with the (a) sample size and (b) impurity percentage of samples.

Figure 11. Sample robustness to size reduction and errors based on pixel-based ensemble learning classifier. Variation of the mean overall accuracy with the (a) sample size and (b) impurity percentage of samples.
Supplemental material

wetland_sm_20231106_highlightCleanVersion.docx

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Data availability statement

The data that support the findings of this study are available upon request by contact with corresponding authors.