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Processes controlling the flux of legacy phosphorus to surface waters at the farm scale

Bibliographic Data

ID15550846
AuthorsVictoria Barcala (0000-0002-3245-2867, Deltares, corresponding author), Joachim Rozemeijer (0000-0001-8278-554X, Deltares), Leonard Osté (0000-0002-5303-1244, Deltares), B van der Grift (0000-0003-4069-6703, KWR Water Research Institute), Laurens Gerner, Thilo Behrends (0000-0002-0728-6545, Utrecht University)
Year2020
Volume16
Issue1
Pages015003-015003
Publication date2020-11-25
Peer ReviewedYes
Open AccessYes
TypeARTICLE
VenueEnvironmental Research Letters (JOURNAL)
Journal identifiersISSN: 1748-9326 • E-ISSN: 1748-9326
PublisherIOP Publishing (PUBLISHER • GB)
DOI10.1088/1748-9326/abcdd4
OpenAlexW3106943852
LanguageEN
Citations received1
References cited35

Phosphorus (P) leaching from agriculture is a major driver of water eutrophication in downstream rivers and lakes. In drained lowland areas with intensive agriculture, a reduction in the fertilizer applications may be insufficient to improve the water quality in the short term as the P accumulated in the soil during decades of high fertilization may continue leaching for many years. A complementary approach to reduce P exports from agriculture is to implement edge-of-field mitigation measures at the farm scale. The selection of effective measures requires a detailed insight into the chemical and hydrological transport mechanisms. Here, we determined the main P sources, processes, and transport routes at the farm scale to support the selection of appropriate mitigation measures. We quantified the legacy P, the different P pools stored in the upper soil, and related it to the yearly P export downstream. To do this, we combined high-resolution monitoring data from the soil, groundwater, surface water, and ditch sediments. The legacy P in the topsoil was high, about 2500 kg ha −1 . The predominant subsurface flow and the subsoils’ P sorption capacity retained the P mobilized from the topsoil and explained the relative moderate flux of P to surface waters (0.04 kg ha −1 during the 2018–2019 drainage season). The dissolved P entering the drainage ditch via groundwater discharge was bound to iron-containing particles formed due to the oxidation of dissolved ferrous iron. Once leached from the soil to the drainage ditch, resuspension of P-rich sediment particles during flow peaks were the most important P transport mechanism (78%). Therefore, we expect that hydraulic constructions that reduce flow velocities and promote sedimentation of P-containing particles could reduce the export of P further downstream

Ditch · Drainage · Eutrophication · Groundwater · Hydrology (agriculture · Leaching (pedology · Nutrient · Soil water · Surface water · Topsoil · Water quality · Aquatic Ecosystems and Phytoplankton Dynamics · Environmental Science · Soil and Water Nutrient Dynamics · Soil erosion and sediment transport · Ecology · Environmental Engineering · Geology · Soil Science

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Unique citing works1
Citations per year1
Citation span2025 - 2025 (1)
Citation velocityrecent
Highly citedNo
Citation typesNeutral: 1

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