Abstract

Abstract. We present a method to simulate fluid flow with reactive solute transport in structured, partially saturated soils using a Lagrangian perspective. In this context, we extend the scope of the Lagrangian Soil Water and Solute Transport Model (LAST) (Sternagel et al., 2019) by implementing vertically variable, non-linear sorption and first-order degradation processes during transport of reactive substances through a partially saturated soil matrix and macropores. For sorption, we develop an explicit mass transfer approach based on Freundlich isotherms because the common method of using a retardation factor is not applicable in the particle-based approach of LAST. The reactive transport method is tested against data of plot- and field-scale irrigation experiments with the herbicides isoproturon and flufenacet at different flow conditions over various periods. Simulations with HYDRUS 1-D serve as an additional benchmark. At the plot scale, both models show equal performance at a matrix-flow-dominated site, but LAST better matches indicators of preferential flow at a macropore-flow-dominated site. Furthermore, LAST successfully simulates the effects of adsorption and degradation on the breakthrough behaviour of flufenacet with preferential leaching and remobilization. The results demonstrate the feasibility of the method to simulate reactive solute transport in a Lagrangian framework and highlight the advantage of the particle-based approach and the structural macropore domain to simulate solute transport as well as to cope with preferential bypassing of topsoil and subsequent re-infiltration into the subsoil matrix.

Highlights

  • Reactive substances like pesticides are subject to chemical reactions within the critical zone (Kutílek and Nielsen, 1994; Fomsgaard, 1995)

  • The main objectives of this study are as follows: 1. We develop a method for reactive transport, i.e. the sorption and degradation of solutes within the Lagrangian framework under well-mixed and preferential flow conditions, and implement this into the Lagrangian Soil Water and Solute Transport Model (LAST)-Model

  • In our previous work (Sternagel et al, 2019), we extended the scope of the Lagrangian approach (i) to account for simulations of water and solute transport in soils as well as (ii) by a structural macropore/preferential flow domain and included both extensions in the LAST-Model

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Summary

Introduction

Reactive substances like pesticides are subject to chemical reactions within the critical zone (Kutílek and Nielsen, 1994; Fomsgaard, 1995). To advance our understanding of reactive solute transport (RT) of pesticides, the joint controls of macropores, sorption, and degradation, a combination of predictive models and plot-scale experiments is often used (e.g. Zehe et al, 2001; Simunek et al, 2008; Radcliffe and Simunek, 2010; Klaus and Zehe, 2011; Klaus et al, 2013). Such methods allow for the assessment of the environmental risks aris-

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