Mapping Soil Organic Carbon Stock and Uncertainties in an Alpine Valley (Northern Italy) Using Machine Learning Models
Author:
Agaba Sara1ORCID, Ferré Chiara1ORCID, Musetti Marco1ORCID, Comolli Roberto1ORCID
Affiliation:
1. Department of Earth and Environmental Sciences (DISAT), University of Milan Bicocca, 20126 Milan, Italy
Abstract
In this study, we conducted a comprehensive analysis of the spatial distribution of soil organic carbon stock (SOC stock) and the associated uncertainties in two soil layers (0–10 cm and 0–30 cm; SOC stock 10 and SOC stock 30, respectively), in Valchiavenna, an alpine valley located in northern Italy (450 km2). We employed the digital soil mapping (DSM) approach within different machine learning models, including multivariate adaptive regression splines (MARS), random forest (RF), support vector regression (SVR), and elastic net (ENET). Our dataset comprised soil data from 110 profiles, with SOC stock calculations for all sampling points based on bulk density (BD), whether measured or estimated, considering the presence of rock fragments. As environmental covariates for our research, we utilized environmental variables, in particular, geomorphometric parameters derived from a digital elevation model (with a 20 m pixel resolution), land cover data, and climatic maps. To evaluate the effectiveness of our models, we evaluated their capacity to predict SOC stock 10 and SOC stock 30 using the coefficient of determination (R2). The results for the SOC stock 10 were as follows: MARS 0.39, ENET 0.41, RF 0.69, and SVR 0.50. For the SOC stock 30, the corresponding R2 values were: MARS 0.45, ENET 0.48, RF 0.65, and SVR 0.62. Additionally, we calculated the root-mean-squared error (RMSE), mean absolute error (MAE), the bias, and Lin’s concordance correlation coefficient (LCCC) for further assessment. To map the spatial distribution of SOC stock and address uncertainties in both soil layers, we chose the RF model, due to its better performance, as indicated by the highest R2 and the lowest RMSE and MAE. The resulting SOC stock maps using the RF model demonstrated an accuracy of RMSE = 1.35 kg m−2 for the SOC stock 10 and RMSE = 3.36 kg m−2 for the SOC stock 30. To further evaluate and illustrate the precision of our soil maps, we conducted an uncertainty assessment and mapping by analyzing the standard deviation (SD) from 50 iterations of the best-performing RF model. This analysis effectively highlighted the high accuracy achieved in our soil maps. The maps of uncertainty demonstrated that the RF model better predicts the SOC stock 10 compared to the SOC stock 30. Predicting the correct ranges of SOC stocks was identified as the main limitation of the methodology.
Reference51 articles.
1. Soil classification and mapping in the Alps: The current state and future challenges;Baruck;Geoderma,2016 2. Romeo, R., Vita, A., Manuelli, S., Zanini, E., Freppaz, M., and Stanchi, S. (2015). Understanding Mountain Soils: A Contribution from Mountain Areas to the International Year of Soils, FAO. 3. Hartemink, A.E., and McSweeney, K. (2014). Soil Carbon, Springer International Publishing. 4. The carbon sequestration potential of terrestrial ecosystems;Lal;J. Soil Water Conserv.,2018 5. Alfthan, B., Gjerdi, H., Puikkonen, L., Schoolmeester, T., Andresen, M., Gjerdi, H.L., Jurek, M., and Semernya, L. (2018). Mountain Adaptation Outlook Series: Synthesis Report, UN Environment & GRID-Arendal.
Cited by
1 articles.
订阅此论文施引文献
订阅此论文施引文献,注册后可以免费订阅5篇论文的施引文献,订阅后可以查看论文全部施引文献
|
|