Abstract

Mitigation measures are needed for reducing chronic dissolved phosphorus (P) losses from agricultural soils with a legacy of excessive P inputs to surface waters. Since pipe drains are an important pathway for P transport from agricultural soils to surface waters in flat areas, removing P from drainage water can be an effective measure. During a 4.5 year-field experiment, we tested the performance of a pipe drain enveloped with Fe-coated sand for removing soluble P from drainage water. Iron-coated sand is a by-product of the drinking water industry and has a high ability to bind P. The P concentration in the effluent from the enveloped pipe drain remained at a very low level over the entire monitoring period, with a removal percentage amounting to 93% for total P. During the field experiment, the enveloped pipe drain was below the groundwater level for a prolonged time. Nevertheless, no reduction of Fe(III) in the Fe-coated sand occurred during the first two years, most likely due to preferential reduction of Mn oxides present in the coatings of the sand particles, as reflected in elevated effluent Mn concentrations. Thereafter, reductive dissolution of Fe oxides in the coatings caused a gradual increase in the Fe concentration in the enveloped pipe drain effluent over time. Concomitantly, the dissolved Mn concentration decreased, most probably due to the depletion in easily accessible Mn oxides in the Fe-coated sand. The Fe in the Fe-coated sand was identified as silicate-containing ferrihydrite (Fh). The submerged conditions of the enveloped pipe drain neither affected the stability of Fh in the Fe-coated sand nor the ability of this measure to capture P from drainage water. Enveloping pipe drains with Fe-coated sand is an effective method for reducing dissolved P inputs from agricultural soils to surface waters and holds great promise for implementation in practice.

Highlights

  • Surface water eutrophication, and dense blooms of cyanobacteria in surface waters as a possible consequence, are problems water managers are still facing worldwide (Stroom and Kardinaal, 2016)

  • Groenenberg et al (2013) described a field experiment with a pipe drain enveloped with sand, coated with Fe oxides, which is a by-product of the production of drinking water from anoxic groundwater (Sharma et al, 2002; van Beek, 2018)

  • Aeration of Fe(II)-containing water in the presence of silicate can lead to the formation of siliceous ferrihydrite (Fh) at which the adsorption of silicate suppresses the growth of Fh particles (Hiemstra, 2018; Kaegi et al, 2010; Koopmans et al, 2020; Voegelin et al, 2010) while at the same time these particles can densely aggregate under the influence of Ca (Kaegi et al, 2010; Voegelin et al, 2010)

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Summary

Introduction

Dense blooms of cyanobacteria in surface waters as a possible consequence, are problems water managers are still facing worldwide (Stroom and Kardinaal, 2016). The enveloped pipe drain in the field experiment of Groenenberg et al (2013) was installed on a site with a calcareous sandy soil located in a seepage polder (Griffioen, 1994) on which flower bulbs were grown and where concentrations of dissolved reactive phosphorus (DRP) in the water from pipe drains were excessive (2—4 mg L−1) This can at least partly be ascribed to high concentrations of DRP in seepage water at this location and a net P surplus of 18 kg P ha−1 yr−1 due to compost addition (Groenenberg et al, 2013) in combination with the generally low P binding capacity of calcareous sandy soils (Chardon and Schoumans, 2007; Koopmans et al, 2006; Schoumans, 2014). The main conclusions were: (i) the enveloped pipe drain was very effective in capturing DRP from drainage water, with an average DRP reduction of 94% and (ii) reductive dissolution of Mn oxides present in the

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