Predicting soil loss in small watersheds under different emission scenarios from CMIP6 using random forests

被引:3
作者
Chen, Yulan [1 ,2 ,3 ]
Wang, Nan [1 ,2 ,4 ]
Jiao, Juying [1 ,2 ,5 ]
Li, Jianjun [5 ]
Bai, Leichao [5 ,6 ]
Liang, Yue [7 ]
Wei, Yanhong [1 ,2 ]
Zhang, Ziqi [5 ]
Xu, Qian [5 ]
Zhang, Zhixin [5 ,8 ]
Wang, Jiaxi [1 ,2 ,5 ]
机构
[1] Chinese Acad Sci, Res Ctr Soil & Water Conservat & Ecol Environm, Yangling, Shaanxi, Peoples R China
[2] Minist Educ, Yangling, Shaanxi, Peoples R China
[3] Guizhou Univ Engn Sci, Sch Ecol Engn, Bijie, Guizhou, Peoples R China
[4] Guangdong Acad Sci, Inst Ecoenvironm & Soil Sci, Guangzhou, Peoples R China
[5] Northwest A&F Univ, Inst Soil & Water Conservat, State Key Lab Soil Eros & Dryland Farming Loess Pl, Yangling, Shaanxi, Peoples R China
[6] China West Normal Univ, Sch Geog Sci, Nanchong, Peoples R China
[7] China Inst Water Resources & Hydropower Res, State Key Lab Simulat & Regulat Water Cycle River, Beijing, Peoples R China
[8] Chayu water Conservancy Bur, Nyingchi, Peoples R China
基金
中国国家自然科学基金;
关键词
climate change; land use change; Loess Plateau; random forests; soil loss model; LOESS PLATEAU; CHECK DAMS; SPATIOTEMPORAL CHARACTERISTICS; CLIMATE-CHANGE; LAND-USE; SEDIMENT; EROSION; MODELS; VEGETATION; CATCHMENT;
D O I
10.1002/esp.5980
中图分类号
P9 [自然地理学];
学科分类号
0705 ; 070501 ;
摘要
Soil loss is a common land degradation process worldwide, which is impacted by land use and climate change. In this study, random forests (RF) were first used to establish a soil loss model at the scale of a small watershed in the hilly-gully region of the Loess Plateau based on the field observation data. Subsequently, the model was used to predict soil loss in the Chabagou watershed under the historical (1990-2020) and future emission scenarios, namely SSP1-2.6 (low-emission), SSP2-4.5 (medium-emission) and SSP5-8.5 (high-emission) (2030-2,100) from the Coupled Model Intercomparison Project Phases 6 (CMIP6). In the RF model, the coefficient of determination (R2) and Nash-Sutcliffe coefficient of efficiency (NS) were both greater than 0.86, and the RMSE-observations standard deviation ratio (RSR) was less than 0.36. Additionally, the RF-based model had higher simulation accuracy and robustness than those of the previous soil loss models, indicating its potential for wider applications in simulating soil loss. Compared with soil loss between 1990 and 1999, climate change led to a 35.36% increase in soil loss, while land use change resulted in an 11.13% reduction from 2000 to 2020 in the Chabagou watershed. This reveals that the current land use management could not effectively counterbalance the soil loss caused by rainstorms. Furthermore, compared with the historical period (1990-2020), under SSP1-2.6, SSP2-4.5 and SSP5-8.5 (2030-2,100), the soil loss rates without land use change would be increased by 6.01%, 19.11% and 35.35%, while the soil loss rates with land use change would be changed by -5.88%, +4.41% and +19.12%, respectively. These results help to provide a scientific basis for enhancing the capacity to respond to climate change and mitigation of soil and water loss on the Loess Plateau. An annual soil loss model of small watersheds was constructed by using random forests in the study. It was used to quantify the impact of land use and climate change on soil loss and predict the future soil loss rates under different emission scenarios from CMIP6.image
引用
收藏
页码:4469 / 4484
页数:16
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