Identification of Abandoned Cropland and Global–Local Driving Mechanism Analysis via Multi-Source Remote Sensing Data and Multi-Objective Optimization
Abstract
1. Introduction
- Constructing a training sample system that fuses multiple land cover datasets to enhance reliability and spatiotemporal representativeness.
- Proposing an integrated modeling framework that combines XGBoost with the NSGA-II evolutionary optimization algorithm. This design leverages the predictive performance of XGBoost and the multi-objective optimization capacity of NSGA-II, while incorporating pruning algorithm to improve computational efficiency.
- Combining SHAP and LIME to conduct global and local multi-scale interpretation of abandonment drivers, thereby improving model transparency and its value for policy guidance. This study is expected to provide scientific support for the governance of abandoned cropland in mountainous counties and serve as a technical reference for implementing China’s cropland protection and rural revitalization strategies.
2. Study Area and Data
2.1. Overview of the Study Area
2.2. Data Sources and Preprocessing
- Remote sensing imagery: Remote sensing data were primarily acquired through the Google Earth Engine (GEE) platform. This includes Sentinel-1 synthetic aperture radar (SAR) imagery and Sentinel-2 multispectral data. Sentinel-1 backscatter coefficients and Sentinel-2 surface reflectance were preprocessed within GEE by applying cloud masking, noise filtering, and temporal compositing, which ensured data consistency and minimized atmospheric effects.
- Three authoritative datasets were integrated, including ESA WorldCover [21], ESRI Land Cover [22], and the China Resource and Environment Data Cloud Platform (CRLC) [23]. To harmonize differences among products, all land cover datasets were reclassified into a consistent category system and combined through overlay analysis, producing a unified land use dataset suitable for national-scale cropland studies.
- Topographic data: A 30 m resolution Digital Elevation Model (DEM) [24] was used to derive key topographic factors such as slope and aspect. The slope and aspect layers were generated using ArcGIS spatial analysis tools, and subsequently resampled to align with the spatial resolution of Sentinel imagery.
- Socioeconomic data: Variables such as population density, distance to roads, and distance to rivers were included to reflect the intensity of human activity and infrastructure distribution. These indicators help reveal the socioeconomic driving forces behind land use change. These datasets, originally at coarser resolutions, were resampled to 10 m to ensure spatial consistency with remote sensing and topographic variables.
- Meteorological data: Climate variables, including annual precipitation [25] and average temperature [26], were used to characterize the natural environment and assess its impact on land use patterns and evolution. The gridded climate data were resampled to a 30 m resolution to ensure comparability across all input layers.
2.3. Sample Point Construction
3. Methodology
3.1. Abandoned Cropland Definition and Overall Framework
3.2. Feature Construction
3.3. Feature Selection via RFECV
3.4. Cropland Classification Model and Algorithmic Foundations
- Population Initialization: Construct a diverse population composed of different combinations of feature subsets and hyperparameters.
- Fitness Evaluation: For each individual, train an XGBoost model and evaluate it using dual objectives—classification accuracy and model complexity.
- Evolutionary Operations: Apply tournament selection and use single-point crossover and mutation to generate offspring.
- Sorting and Updating: Identify Pareto-optimal solutions via non-dominated sorting and use crowding distance to preserve population diversity.
- Convergence Criteria: The process terminates once convergence is reached or the maximum number of generations is exceeded.
3.5. Interpretability Framework and Methods
4. Results and Analysis
4.1. Feature Optimization and Model Performance Improvement
4.2. Generalization Capability and Independent Validation
4.3. Spatial Distribution of Abandoned Cropland and Validation in Representative Areas
4.4. Interpretation of Driving Factors
4.4.1. Global Interpretation: SHAP Analysis
4.4.2. Interaction Effects: Variable Synergy Mechanisms
4.4.3. Local Interpretation: LIME-Based Sample Response Analysis
- (1)
- SAVG-dominated samples: In most cases, SAVG (mean image gray level) remains the primary or top-ranked explanatory variable, demonstrating strong stable dominance across predictions. This finding is consistent with the global feature importance ranking from SHAP. These samples are typically located in areas with low reflectance and coarse textures, where LIME assigns significant positive contributions to SAVG. This confirms SAVG’s fundamental role in distinguishing abandonment-prone land, particularly when spectral characteristics of degradation are apparent.
- (2)
- Socioeconomic-dominated samples: In some samples, the influence of SAVG decreases, while Road (distance to road) and Population (population density) emerge as the leading predictors. These cases often involve regions with low spectral brightness but high accessibility or population density. The model downweights the spectral features and instead emphasizes socioeconomic indicators, reflecting its adaptive capacity to contextual information. This adjustment helps prevent misclassification in atypical abandonment scenarios.
- (3)
- Contribution direction heterogeneity: Notably, the same feature may exhibit opposite contribution directions across samples. For instance, a given variable may increase the predicted probability of abandonment in some samples, while suppressing it in others. This highlights that abandonment classification is a typical multi-feature collaborative decision process, in which the model dynamically constructs differentiated logic based on sample context.
5. Discussion and Outlook
5.1. Methodological Advantages
- (1)
- High-performance and efficient identification framework: By applying NSGA-II to optimize XGBoost’s hyperparameter space and combining it with recursive feature and pruning, the proposed model achieves high recall and strong generalization on the test set, while significantly reducing model complexity and improving both deployment efficiency and computational adaptability.
- (2)
- Enhanced robustness through multi-source feature integration: By fusing remote sensing spectral features, terrain attributes, and socioeconomic indicators, the model constructs a semantically rich and spatially scalable feature set, improving its adaptability across diverse geomorphological types and land management regimes while maintaining classification stability [43,44,45].
- (3)
- Simplified structure with flexible deployment: Through effective feature compression and parameter control, the final model achieves an optimal balance between computational load and recognition performance while retaining key variables. This structure is well-suited for integration into regional-scale cropland monitoring systems, supporting dynamic updates and long-term operation.
5.2. Interpretability Architecture and Strengths
- (1)
- SHAP for global variable attribution: SHAP analysis reveals the ranking of features in terms of importance in the classification process, demonstrating that variables like mean image gray level, low values of red-edge bands, slope, and road accessibility consistently play a significant role in identifying abandoned land. These insights contribute to building a reusable knowledge-based rule system.
- (2)
- LIME for pixel-level heterogeneity analysis: Focusing on local neighborhoods at the pixel scale, LIME reveals marginal contributions and directionality of variables for individual samples. It enhances understanding of classification logic in complex boundary zones or rural–urban fringes, complementing SHAP’s global-level insights.
- (3)
- Improved model transparency and policy usability: The dual-path SHAP–LIME interpretability framework makes the variable–response–spatial object relationships explicit, transitioning the model from a “black box” to a “gray box.” This significantly enhances the model’s auditability and credibility in practical scenarios such as land supervision, cropland consolidation zoning, and policy design.
- (4)
- Verification of classification stability and cross-region consistency: SHAP and LIME consistently show similar variable response trends across multiple samples and regions, indicating strong stability and potential transferability of the model across environmental and geographic units.
5.3. Limitations and Challenges
- (1)
- Spatial mismatch in socioeconomic data: Some socioeconomic features (e.g., population density, road accessibility) are derived from statistical yearbooks or grid-based interpolation with coarser resolution than remote sensing pixels. This mismatch can induce classification errors, especially at the village scale or in mountainous fringe areas, weakening interpretability at fine spatial scales. Although the exact magnitude of this error was not directly quantified in this study due to the lack of pixel-level socioeconomic ground-truth data, existing studies have demonstrated that improving and harmonizing data resolution can effectively reduce such uncertainties and enhance classification accuracy. This underscores the importance of incorporating higher-resolution socioeconomic datasets or employing more detailed survey data for cross-validation in future research [46,47].
- (2)
- Lack of causal inference mechanisms: Current interpretability tools (e.g., SHAP, LIME) reveal associations rather than causal relationships [48]. Under correlated or noisy features, variable importance may be biased by confounding, reverse causality, or scale effects, meaning that signals such as VV/VH or NDVI could partly reflect consequences rather than true drivers. Differences in feature rankings across regions (e.g., Xundian vs. Binchuan) are therefore expected and should be interpreted cautiously. Future studies could integrate causal frameworks—such as temporal lags, panel data designs, matching/weighting, or instrumental-variable approaches—to identify more robust cause–effect pathways and provide stronger evidence for policy interventions.
- (3)
- Limited performance in transitional boundary zones: In zones with blurred boundaries (e.g., cropland vs. forest or built-up land), similar remote sensing features lead to confused or missed classifications. This issue is particularly prominent in fragmented plots or areas with unclear land ownership. Higher-resolution imagery and auxiliary geographic data are needed to enhance spatial boundary delineation [49,50,51]. Future research could benefit from higher-resolution remote sensing imagery, auxiliary geospatial datasets (e.g., cadastral maps), and multi-scale image fusion techniques to improve boundary delineation and enhance classification accuracy in transitional zones.
- (4)
- Although the integration of optical, radar, and topographic data significantly improves model accuracy and robustness, it may also introduce uncertainties due to differences in spatial resolution, sensor characteristics, and acquisition times. Such discrepancies can create noise or bias in feature extraction and classification. Nevertheless, previous studies indicate that when properly harmonized, multi-source approaches generally outperform single-source models. Future work should further explore methods to quantify and reduce these uncertainties, such as advanced data fusion techniques and cross-regional validation.
5.4. Future Research Directions
- (1)
- Building high-resolution socioeconomic data integration mechanisms: Incorporating frequent, fine-grained data such as land transaction records, rural e-commerce activity, or agricultural machinery trajectories can help reconstruct micro-scale socioeconomic maps, overcoming the coarse granularity and lag of traditional statistics and enhancing local-scale applicability and timeliness [52].
- (2)
- Introducing causal inference and graph-based modeling: Future work may explore Structural Equation Modeling (SEM), Causal Forests, or Graph Neural Networks (GNNs) to model causal relationships and spatial dependencies among variables, thereby enabling mechanism reasoning and decision forecasting, and enriching the theoretical depth of abandonment modeling.
- (3)
- Advancing transfer learning and regional adaptation mechanisms: Considering the variability in cropping systems, climate zones, and landforms, future models should incorporate domain adaptation, regional tuning, and model migration techniques to enable scaling from local to national levels, enhancing the model’s scalability and application potential.
6. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
References
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| Data Types | Data Name | Resolution | Year | Data Sources |
|---|---|---|---|---|
| Sentinel-2 | Blue (B2) | 10 m | 2020–2022 | https://developers.google.cn/earth-engine/datasets/catalog/sentinel-2?hl=zh-cn (accessed on 4 July 2025). |
| Green (B3) | 10 m | |||
| Red (B4) | 10 m | |||
| Red edge 1 (B5) | 20 m | |||
| Red edge 2 (B6) | 20 m | |||
| Red edge 3 (B7) | 20 m | |||
| Near Infrared (B8) | 10 m | |||
| Narrow Near Infrared (B8A) | 20 m | |||
| Short-Wave Infrared 2 (B11) | 20 m | |||
| Short-Wave Infrared 3 (B12) | 20 m | |||
| Sentinel-1 | VV VH | 10 m | Sentinel-1 SAR GRD: C-band Synthetic Aperture Radar Ground Range Detected, log scaling|Earth Engine Data Catalog|Google for Developers (accessed on 6 July 2025). | |
| LULC | ESA | 10 m | https://developers.google.com/earth-engine/datasets/catalog/ESA_WorldCover_v100 (accessed on 4 July 2025). | |
| ESRI | 10 m | https://www.arcgis.com/home/item.html?id=cfcb7609de5f478eb7666240902d4d3d (accessed on 8 July 2025). | ||
| CRLC | 10 m | https://github.com/LiuGalaxy/CRLC?tab=readme-ov-file (accessed on 11 July 2025). | ||
| Topographic data | DEM | 30 m | 2022 | https://doi.org/10.5523/bris.s5hqmjcdj8yo2ibzi9b4ew3sn (accessed on 6 July 2025). |
| Socioeconomic data | Road River | 1 km | 2020–2022 | The third national land resource survey |
| Population | ORNL LandScan Viewer—Oak Ridge National Laboratory (accessed on 12 July 2025). | |||
| Meteorological data | Temperature | 1 km | https://doi.org/10.5281/zenodo.3114194. (accessed on 1 July 2025). | |
| Precipitation | https://doi.org/10.5281/zenodo.3114194. (accessed on 1 July 2025). |
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Share and Cite
Gui, S.; Li, J.; Chen, G.; Zhao, J.; Tang, B.; Li, L. Identification of Abandoned Cropland and Global–Local Driving Mechanism Analysis via Multi-Source Remote Sensing Data and Multi-Objective Optimization. Remote Sens. 2025, 17, 3086. https://doi.org/10.3390/rs17173086
Gui S, Li J, Chen G, Zhao J, Tang B, Li L. Identification of Abandoned Cropland and Global–Local Driving Mechanism Analysis via Multi-Source Remote Sensing Data and Multi-Objective Optimization. Remote Sensing. 2025; 17(17):3086. https://doi.org/10.3390/rs17173086
Chicago/Turabian StyleGui, Side, Jiaming Li, Guoping Chen, Junsan Zhao, Bohui Tang, and Lei Li. 2025. "Identification of Abandoned Cropland and Global–Local Driving Mechanism Analysis via Multi-Source Remote Sensing Data and Multi-Objective Optimization" Remote Sensing 17, no. 17: 3086. https://doi.org/10.3390/rs17173086
APA StyleGui, S., Li, J., Chen, G., Zhao, J., Tang, B., & Li, L. (2025). Identification of Abandoned Cropland and Global–Local Driving Mechanism Analysis via Multi-Source Remote Sensing Data and Multi-Objective Optimization. Remote Sensing, 17(17), 3086. https://doi.org/10.3390/rs17173086

