Abstract

The study and quantification of soil redistribution is a complex and difficult task and even a non-solved question at catchment scale both in field and numerical simulation studies. In this study we tackle this topic by coupling two different predicting models and a sound field-based dataset to assess the potential soil redistribution in a Mediterranean rain-fed agricultural and mountainous catchment (La Reina gully catchment, Cinco Villas region, NE Spain): the enhanced Modified-RMMF-2014 version of the “Modified Revised Morgan, Morgan and Finney” model (Morgan, 2001; López-Vicente and Navas, 2010) of soil erosion and the IC (Index of Connectivity; Borselli et al., 2008) model of sediment connectivity. In a cereal experimental plot (1.9 ha; 1 x 1 m of cell size), located in the lowlands of the La Reina gully catchment, we firstly ran the IC model under six different scenarios of runoff pathways and results were compared with field observations of soil redistribution. The best performance was obtained with the IC model when the map of geomorphic features (rills, ephemeral gullies and fan deposits) was used in the simulation. Predicted rates of both models were correlated at 613 control points and three areas where identified at the plot: erosive-, stable- and depositional- prone areas, affecting 30%, 22% and 48% of the soil surface, respectively. The average erosion rates in each area were 3.3, 1.5 and 1.1 Mg ha-1 yr-1 with standard deviation values of 20.3, 19.0 and 8.3 Mg ha-1 yr-1. Then, the IC model was run at La Reina gully catchment (231 ha; 5 x 5 m) and the IC values were analysed following the first approach. Stable areas and those mainly affected by processes of soil loss and deposition were identified. Results showed clear differences in the index of connectivity along the catchment though the extension of the areas with predominant processes of soil loss was under predicted (11% of the catchment area). Further research should be focused on the adjustment of the IC model to catchment scale. Our approach offers a simple and alternative method to assess spatially distributed processes of soil redistribution at catchment scale that can be of interest in ungauged catchments where calibration task of numerical models is difficult to be done.

Highlights

  • Soil erosion by water is a widespread problem throughout the world that causes the loss of fertile soil and crop yield in agricultural areas and a reduction in the overall quality and functions of the soils (Stavi and Lal, 2011)

  • We computed six different Index of Connectivity (IC) maps with different threshold values for the “stream mask” factor (Fig. 4): a) no stream-mask; b) automatic stream-mask starting at the beginning of the ephemeral gullies (130 cumulative pixels calculated downwards from the divide and using the overland flow pathway map and field observations (Fig. 2c and d); c) automatic stream-mask linked to the ephemeral gullies without affecting stable areas (231 pixels); d) automatic stream-mask starting at the beginning of the fans (562 pixels); e) stream-mask associated with the map of depositional areas; and f) stream-mask associated with the map of rills and ephemeral gullies

  • Cavalli et al (2013) found better results with the IC model when the information of the main water bodies and streams were added in the assessment of the runoff and sediment connectivity in comparison with the direct application of the IC

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Summary

Introduction

Soil erosion by water is a widespread problem throughout the world that causes the loss of fertile soil and crop yield in agricultural areas and a reduction in the overall quality and functions of the soils (Stavi and Lal, 2011). In fragile and complex systems like the Mediterranean region, intense erosion processes are widespread and a better understanding of the processes of soil redistribution is necessary to reduce the sediment yield (García-Ruiz et al 2013). Quantification of spatially distributed rates of soil redistribution (net soil loss and deposition) and sediment transfer and storage at catchment scale are non-resolved questions in soil erosion studies. As a consequence of these activities, numerous linear landscape elements (unpaved and paved trails, roads, land levelling, irrigation ditches, stone walls, dams, etc.) appear in landscapes, modifying the patterns of the overland flow and sediment connectivity

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