Challenges in modelling dissolved organic matter dynamics in agricultural soil using DAISY |
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Authors: | Birgitte Gjettermann Merete Styczen Hans Christian B. Hansen Finn P. Vinther Søren Hansen |
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Affiliation: | 1. Faculty of Life Sciences, Department of Agricultural Sciences, University of Copenhagen, Højbakkegård Allé 9, DK-2630 Taastrup, Denmark;2. DHI—Water and Environment, Department of Hydrology, Soil and Waste, Denmark;3. Faculty of Life Sciences, Department of Natural Sciences, University of Copenhagen, Denmark;4. Faculty of Agricultural Sciences, Institute of Agroecology and Environment, University of Aarhus, Denmark;1. CSIRO Entomology, PMB No 2, Glen Osmond, SA 5064, Australia;2. School of Environment and Natural Resources, Ohio State University, Columbus, OH 43210, USA;3. Odum School of Ecology, Ecology Annex, University of Georgia, Athens, GA 30602-2360, USA |
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Abstract: | Because dissolved organic matter (DOM) plays an important role is terrestrial C-, N- and P-balances and transport of these three components to aquatic environments, there is a need to include it in models. This paper presents the concept of the newly developed DOM modules implemented in the DAISY model with focus on the quantification of DOM sorption/desorption and microbial-driven DOM turnover. The kinetics of DOM sorption/desorption is described by the deviation of the actual DOM concentration in solution from the equilibrium concentration, Ceq. The Ceq is soil specific and estimated from pedotransfer functions taking into account the soil content of organic matter, Al and Fe oxides. The turnover of several organic matter pools including one DOM pool are described by first-order kinetics.The DOM module was tested at field scale for three soil treatments applied after cultivating grass–clover swards. Suction cups were installed at depths 30, 60 and 90 cm and soil solution was sampled for quantification of dissolved organic C (DOC) and dissolved organic N (DON). In the topsoil, the observed fluctuations in DOC were successfully simulated when the sorption/desorption rate coefficient k was low. In the subsoil, the observed concentrations of DOC were steadier and the best simulations were obtained using a high k. The model shows that DOC and DON concentrations are levelled out in the subsoils due to soil buffering. The steady concentration levels were based on the Ceq for each horizon and the kinetic concept for sorption/desorption of DOC appeared a viable approach. If Ceq was successfully estimated by the pedotransfer function it was possible to simulate the DOC concentration in the subsoil. In spite of difficulties in describing the DOC dynamics of the topsoil, the DOM module simulates the subsoil concentration level of DOC well, and also—but with more uncertainty—the DON concentration level. |
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