Assessment of the impacts of dynamic soil properties and vegetation cover on soil erosion using distributed hydrological model Tan 1 Zi , Ciaran 2 Lewis , Gerard 2 Kiely , and John D. GC11A-0968 1 Albertson 1.Civil and Environmental Engineering, Duke University, Durham, US 2.Civil and Environmental Engineering, University College Cork, Cork, Ireland Contact Information Tan Zi tan.zi@duke.edu I. Introduction III. Scenarios Soil erosion is a common environmental problem in certain mountainous regions. Heterogeneity of soil properties and complex vegetation-soil interactions raise challenges in accurately simulating soil erosion processes. Six scenarios were selected to investigate the impacts of soil and vegetation. Time Soil Erosion + + Soil Degradation BVS2=B+V+S2 BVS1=B+V+S1 BV=B+V BS2=B+S2 BS1=B+S1 B Vegetation Loss Fig.1 Positive feedbacks of soil erosion VI. Conclusion and Application The erosion model was tested at an experimental watershed in Ireland. Area:1542 ha AAP:1400mm Vegetation: perenial ryegrassland Soil: gleys/podzols Measurement: Flux tower, flow gauge, and water sampler Fig.8 The DEM map of Dripsey watershed • The erosion model has expected behavior on soil particles movement by water on hillslope. • The temporal changes of both soil properties and vegetation covers have considerable impacts on soil erosion processes. • Temporal changes of vegetation covers have dominant effects on soil erosion simulations in short time simulation. • Temporal changes of soil properties should be considered in long time simulation, e.g. climate change application. • The coupled soil and vegetation model has the best performance compare with observed data, the spatial distribution of soil erosion also improved in coupled model. Fig. 4 Major components of erosion model BS + + V. Watershed Simulation BS2 IV. 1D Hillslope Tests The model was tested on a 1D hillslope. The driven meteorological data were generated by Wather generator according to the climate condition of experimental watershed. Three points were selected to show the soil texture changes due to erosion and deposition processes applied on the hillslope. 1. How to represent these feedbacks using modeling tools? 2. How important are those feedbacks in long term simulations? Fig.11 Soil conservation(left) and sediment transport(right), images acquired by using google search engine II. Model Structure GEOtop VII. Future work Typical Erosion Module • Vegetation dynamics • Spatial verification • Soil organic matter/nutrition losses by water erosion • Estimate the impacts of soil properties on soil erosion under climate change scenarios D50 Fig.5 The soil texture changes at different locations during simulation BS1 Fig.2 The structure of GEOtop model and typical soil erosion module Fig.9 Simulated soil erosion/deposition map of Dripsey watershed of year 2002 In order to capture the influences of changing soil properties on soil erosion, this model assumes a thin detached soil layer lays on the top of soil column, and this erosion process will occur on this layer. S2 Key References BS2 Scenarios B BV BS1 BS2 BVS1 BVS2 BVS2 Fig.6 The time series of soil erosion rate(E) of different scenarios NS 0.8807 0.8795 0.8802 0.8806 0.9477 0.9477 1. Rigon, R., Bertoldi, G. & Over, T. M. GEOtop: A distributed hydrological model with coupled water and energy budgets. J Hydrometeorol 7, 371-388 (2006). 2. Govers, G. Empirical relationships for the transport capacity of overland flow. Erosion,Transport and Deposition Processes 189, 45-63 (1990). 3. Everaert, W. Empirical Relations for the Sediment Transport Capacity of Interrill Flow. Earth Surf Proc Land 16, 513-532 (1991). 4. Lewis, C. Phosphorus, Nitrogen and Suspended Sediment loss from Soil to Water from Agricultural Grassland Master of Engineering Science thesis, University College Cork, (2003). Fig.10 Normalized cumulative soil loss of different scenarios Acknowledgement Tab.1 Annual soil erosion of Dripsey watershed S1 E (kg/ha) Fig.3 The structure of dynamic soil properties module Fig.7 Normalized cumulative soil losses of different scenarios BS1 111.2742 BS2 110.9986 BVS1 60.8619 BVS2 60.86053 This study is part of the Science, Technology, Research and Innovation for the Environment (STRIVE) Programme 2007-2013. We are appreciative of the financial support of Irish Government under the National Development Plan 2007-2013.