###### Abstract
); [EMAIL_ADDRESS] (F.)  
Footnote †: journal: Medical Engineering, National Research Institute of Rural Engineering, Water and Forests (INRGCREP), University of Carthage, Rue Hedi El Karary El Marzah I/B-BP N' 10, Ariana 2080, Tunisia; [EMAIL_ADDRESS] (M.L.K. ); [EMAIL_ADDRESS] (F.)  
Footnote †: journal: Medical Engineering, National Research Institute of Rural Engineering, Water and Forests (INRGCREP), University of Carthage, Rue Hedi El Karary El Marzah I/B-N’ 10, Ariana 2080, Tunisia; [EMAIL_ADDRESS] (M.L.K. ); [EMAIL_ADDRESS] (F.)  
Footnote †: journal: Medical Engineering, National Research Institute of Rural Engineering, Water and Forests (INRGCREP), University of Carthage, Rue Hedi El Karary El Marzah I/B-BP N' 10, Ariana 2080, Tunisia; [EMAIL_ADDRESS] (M.L.K. on the availability and quality of its water resources, as well as the intricate process of erosion [4]. The interplay between ecosystem management and the choices made in how the land is used and maintained can either contribute positively to the sustainability of water sources and minimize erosion, or conversely, lead to detrimental effects on these critical natural processes [5]. Addressing erosion and managing water resources within a watershed requires a comprehensive approach addressing elements like land use, precipitation patterns, and land and soil types [6; 7]. Effective strategies can include conservation approaches such as sustainable agronomic practices, soil terracing, and vegetation management, as well as regulations and policies aimed at promoting sustainable soil and water management [8]. Advancements in remote sensing and geospatial technology have resulted in higher-quality and more accessible satellite imagery in recent years. The integration of remote sensing with geographic information systems (GIS) is a common practice used to categorize maps and track changes in land use patterns over time. One significant benefit of this approach is its ability to efficiently address the issues that arise from changes in land use, the implementation of sustainable land management practices, and the development of land use policies. Changes in land use and land cover are crucial factors in soil erosion, frequently exacerbating erosion processes [9]. SWC structures, such as terracing, contour plowing, strip cropping, and grassed waterways can have substantial impacts on reducing water erosion, as they reduce the velocity and volume of water flow, trap sediments, and reduce soil losses [10]. They can also help to increase water infiltration and reduce runoff, thereby reducing the amount of water available for erosion. As a result, the implementation of SWC structures leads to a reduction in water erosion, the preservation of soil quality and fertility, and enhances the overall ecological health of a watershed [11]. Predicting the changes in soil erosion that can be obtained using interventions aimed at changing land use/land cover or implementing SWC structures in a watershed is important in order to generate realistic planning scenarios. The Revised Universal Soil Loss Equation model predicts soil erosion based on several factors, particularly rainfall intensity, slope steepness, soil erodibility, and vegetation cover [12; 13]. By running the model using datasets generated in different time periods, the effectiveness of soil erosion interventions can be predicted and assessed [14]. Utilizing remote sensing data enables the retrieval of diachronic information about erosion factors that change over time [14; 15]. This technology allows for the monitoring and analysis of dynamic environmental changes, contributing to a deeper understanding of how erosion processes evolve and supporting the formulation of efficient strategies for soil conservation and management. The sediment delivery ratio (SDR) is a critical parameter utilized to assess the proportion of sediment generated from erosion at a specific location that is ultimately delivered to a downstream location.