Assessing Climate Change Impacts on Cropland and Greenhouse Gas Emissions Using Remote Sensing and Machine Learning
Abstract
:1. Introduction
- To analyze annual trends in agricultural land-use changes in South Sumatra, offering insights into the extent and rate of agricultural expansion;
- To investigate the relationship between land-use changes and C and N2O emissions, identifying patterns and variations over time;
- To support the development of sustainable agricultural policies through data-driven insights that balance food production with climate change mitigation.
2. Materials and Methods
2.1. Study Area
2.2. Data Sources
- Landsat 8 OLI: used to derive vegetation indices, including the normalized difference vegetation index (NDVI) and enhanced vegetation index (EVI);
- Soil Grids & Harmonized World Soil Database (HWSD): used to obtain soil properties and organic carbon content;
- DROSA-A and DROSE-A: used for modeling carbon emissions from agricultural areas and emission data;
- GLDAS-2.1: Global Land Data Assimilation System: used for soil moisture data;
- FLDAS: Famine Early Warning Systems Network (FEWS NET) Land Data Assimilation System: used for wind speed and humidity data;
- MODIS: used for albedo data.
2.3. Data Processing and Analysis
2.4. Machine Learning Models
- Classification and regression trees (CART): a decision tree-based model that applies a series of hierarchical decision rules for classification and regression tasks;
- Random forest (RF): an ensemble learning method that constructs multiple decision trees and averages their predictions to enhance accuracy;
- Gradient boosting trees (GBT): a boosting technique that sequentially improves model performance by correcting errors in weak learners;
- Support vector machines (SVM): a model that optimizes the decision boundary (hyperplane) for classification and regression, particularly useful for complex datasets.
- RF: the number of trees, maximum depth, and minimum samples per split were fine-tuned to balance accuracy and computational efficiency;
- GBT: learning rate, number of boosting stages, and maximum tree depth were adjusted to prevent overfitting while enhancing predictive power;
- CART: tree depth and pruning techniques were optimized to reduce model complexity while maintaining interpretability;
- SVM: the choice of kernel function (linear, polynomial, and radial basis function), regularization parameter (C), and gamma values were explored to improve performance.
- RF outperformed other models, demonstrating superior accuracy in capturing emission patterns;
- GBT exhibited moderate accuracy, indicating its potential for emission estimation;
- CART provided lower performance, suggesting limitations in handling complex relationships between environmental variables;
- SVM performed poorly, indicating that it may not be suitable for this dataset due to the nonlinear nature of emission processes.
2.5. Statistical Analysis
- Correlation coefficient (R): a statistical measure of the strength of a linear relationship between variables;
- Coefficient of determination (R2): evaluates the proportion of variance explained by the model;
- Mean absolute error (MAE): measures the average magnitude of errors between predicted and observed values;
- Root mean squared error (RMSE): assesses model prediction errors by emphasizing larger deviations.
3. Results
3.1. Changes in Cropland and Grassland Areas
- 1992–2000: No significant changes in cropland areas;
- 2000–2010: A declining trend in cropland areas;
- 2010–2018: Cropland areas began to increase again.
3.2. Carbon Emissions from Cropland and Grassland
- 1992–2016: A gradual increase in carbon emissions;
- 2017: A noticeable anomaly in emissions;
- 2018: Emissions resumed an increasing trend.
- 1992–2016: Stable carbon emissions with minimal fluctuations;
- 2017–2018: Minor fluctuations, but emissions remained consistent overall.
3.3. N2O Emissions from Cropland and Grassland
- 1992–2016: N2O emissions showed a steady upward trend;
- 2017: An anomaly was detected in the data;
- 2018: Emissions returned to a normal trend.
- 1992–2016: N2O emissions remained stable with slight fluctuations;
- 2017–2018: Aside from the anomaly in 2016, emissions generally remained steady.
3.4. Performance of Machine Learning Models for Cropland and Grassland Emissions
- GBT and RF are the best-performing models, with RF slightly outperforming GBT. The higher accuracy of RF indicates that it may be more suitable for predicting C emissions from cropland compared to GBT. Both models exhibit low error metrics, making them reliable choices for C emission predictions;
- CART shows a relatively lower correlation compared to GBT and RF, indicating it struggles more to capture the underlying trends in C emissions. Its performance in terms of accuracy is subpar;
- SVM performs the worst, with very low correlation and high error values. This suggests that SVM is not effective for predicting C emissions from cropland in this case.
- GBT leads again with the best accuracy and minimal error, showing its strong capability in predicting N2O emissions with precision;
- RF follows closely with nearly identical error metrics to GBT, reinforcing the fact that both models are highly effective in predicting N2O emissions from cropland;
- CART has a lower correlation and higher error metrics, suggesting it is not as efficient at capturing the relationships in the data as GBT and RF;
- SVM again shows the poorest performance with extremely high error values, making it unsuitable for this task.
- RF model performs the best for predicting grassland C emissions. It demonstrates a good ability to capture the relationships in the data, making it the most reliable model for this task;
- GBT also performs well but with slightly lower accuracy compared to RF. While GBT still provides reasonable predictions, it captures less of the variation in the emissions data compared to RF;
- CART and SVM show weaker performances. CART captures some of the trends but struggles compared to RF and GBT. On the other hand, SVM performs poorly, failing to effectively capture the patterns in grassland C emissions.
- For grassland N2O emissions, RF again outperforms other models, showing the best predictive capability. It is the most effective model for capturing the trends and patterns in the data;
- GBT also provides good results, though slightly less accurate than RF. It remains a strong alternative for predicting N2O emissions in grassland areas;
- CART demonstrates moderate performance but does not capture the underlying relationships as effectively as RF or GBT;
- SVM again shows the weakest performance, indicating that it is not well suited for this task, with poor accuracy and large errors.
4. Discussion
4.1. Agricultural Expansion and Environmental Impacts
4.2. Carbon and N2O Emission Trends
4.3. Policy Recommendations and Sustainable Agriculture
- Forest conservation and sustainable land management: Reforestation and agroforestry practices should be encouraged to mitigate the negative effects of agricultural expansion on natural ecosystems. Studies have shown that such strategies can effectively enhance carbon sequestration and reduce net emissions from land-use change [60];
- Adoption of low-carbon agricultural techniques: Sustainable farming methods such as no-till farming and composting, which help preserve soil organic matter and reduce carbon loss, should be promoted. Prior research has demonstrated that no-till farming can significantly improve soil carbon retention and decrease greenhouse gas emissions from cropland [61];
- Smart fertilizer management: Precision farming technologies and data analytics should be utilized to optimize fertilizer application and minimize excessive nitrogen-based fertilizer use.
4.4. Study Limitations and Future Research
4.5. Performance of Machine Learning Models
5. Conclusions
- Expansion of agricultural areas: Between 1992 and 2018, agricultural areas in South Sumatra expanded by approximately 1.57 million hectares. A small decrease was observed in the early 2000s, but after 2010, the expansion trend continued;
- Carbon emissions: Carbon emissions have generally shown a continuous increase, with a sharp decline in 2017. This decline may be attributed to data-related errors or changes in regional agricultural policies. Emissions increased again in 2018;
- N2O emissions: Nitrous oxide emissions showed a slight upward trend in parallel with the expansion of agricultural areas. This increase is primarily due to changes in fertilizer use and agricultural practices.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
Abbreviations
N2O | Nitrous oxide |
C | Carbon |
LU/LUC | Land use and land-use change |
SOC | Soil organic carbon |
GEE | Google Earth Engine |
RF | Random forest |
CART | Classification and regression trees |
GBT | Gradient boosting trees |
SVM | Support vector machines |
RBF | Radial basis function |
NDVI | Normalized difference vegetation index |
EVI | Enhanced vegetation index |
HWSD | Harmonized World Soil Database |
GLDAS | Global Land Data Assimilation System |
FLDAS | Famine Early Warning Systems Network Land Data Assimilation System |
LST | Land surface temperature |
R | Correlation coefficient |
R2 | Coefficient of determination |
MAE | Mean absolute error |
RMSE | Root mean squared error |
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Model | R | R2 | MAE | RMSE |
---|---|---|---|---|
GBT | 0.8430 | 0.7106 | 0.0632 | 0.0793 |
CART | 0.6893 | 0.4752 | 0.0834 | 0.1154 |
SVM | 0.4906 | 0.2406 | 29.4234 | 29.4289 |
RF | 0.7698 | 0.5927 | 0.0680 | 0.0894 |
Model | R | R2 | MAE | RMSE |
---|---|---|---|---|
GBT | 0.8430 | 0.7106 | 0.00007 | 0.00009 |
CART | 0.6893 | 0.4752 | 0.0001 | 0.0001 |
SVM | 0.4906 | 0.2406 | 29.7635 | 29.7701 |
RF | 0.7722 | 0.5963 | 0.00008 | 0.0001 |
Model | R | R2 | MAE | RMSE |
---|---|---|---|---|
GBT | 0.6264 | 0.3923 | 0.0094 | 0.0132 |
RF | 0.6225 | 0.3875 | 0.0099 | 0.0125 |
SVM | 0.3616 | 0.1308 | 29.7212 | 29.7274 |
CART | 0.4220 | 0.1781 | 0.0119 | 0.01791 |
Model | R | R2 | MAE | RMSE |
---|---|---|---|---|
GBT | 0.5166 | 0.2669 | 0.00005 | 0.00006 |
RF | 0.6248 | 0.3904 | 0.00005 | 0.00006 |
SVM | 0.0607 | 0.0036 | 29.7329 | 29.7386 |
CART | 0.3598 | 0.1295 | 0.00006 | 0.00008 |
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Uyar, N.; Uyar, A. Assessing Climate Change Impacts on Cropland and Greenhouse Gas Emissions Using Remote Sensing and Machine Learning. Atmosphere 2025, 16, 418. https://doi.org/10.3390/atmos16040418
Uyar N, Uyar A. Assessing Climate Change Impacts on Cropland and Greenhouse Gas Emissions Using Remote Sensing and Machine Learning. Atmosphere. 2025; 16(4):418. https://doi.org/10.3390/atmos16040418
Chicago/Turabian StyleUyar, Nehir, and Azize Uyar. 2025. "Assessing Climate Change Impacts on Cropland and Greenhouse Gas Emissions Using Remote Sensing and Machine Learning" Atmosphere 16, no. 4: 418. https://doi.org/10.3390/atmos16040418
APA StyleUyar, N., & Uyar, A. (2025). Assessing Climate Change Impacts on Cropland and Greenhouse Gas Emissions Using Remote Sensing and Machine Learning. Atmosphere, 16(4), 418. https://doi.org/10.3390/atmos16040418