Biogeochemical and hydrological controls on phosphorus ......28 juni 2017 Biogeochemical and...

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  • 28 juni 2017

    Biogeochemical and hydrological controls on phosphorustransport in lowland catchments

    Bas van der Grift

    Martin WassenJasper Griffioen Paul SchotLeonard Osté

    With help from:Joachim RozemeijerYpe van der VeldeThilo BehrendsDeirdre Clark Arjen KratzEmma van PoptaWilbert BerendrechtMiguel de Lucas PardoHans Peter BroersErwin Meijers

  • 28 juni 2017

    What happens in between?Controls on P transport in catchment

    P loads from soil to surface water

    Phosphorus transport in catchments

    Data WSHA

  • Phosphorus in surface water

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    Observation 1:

    variable in time

    Data WSHA

    P-total in unfiltered samples:common practice in surface water monitoring

  • Phosphorus in surface water

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    Observation 2:

    Low dissolved P concentrations

    Particulate P• mineral P?• organic P?

    Data WSHA

  • Groundwater-fed lowland catchments

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    Data national monitoringnetwork groundwater quality2009

    Reactive subsurface• anoxic groundwater• Fe(II)-bearing• discharges to surface water

    high load of dissolved Fe(II) to surface water

  • Aeration of Fe-bearing groundwater

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    just after sampling 1 day later

    Fe2+(aq) + 2.5H2O + 0.25O2 Fe(OH)3(s) + 2H+

    Fe precipitates have a high affinity for binding PO4

  • Fe(II) oxidation experiments

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    PO4 added after Fe(II) oxidation PO4 present during Fe(II)

    Effect of formation Fe(III) precipitates on PO4 immobilisation

    Geochemical fundamentally different

  • Experiments with initial dissolved P/Fe2+ ratio of 0.18

    PO4 present: precipitation ofFe2.44PO4(OH)4.32P/Fe = 0.41

    PO4 depleted: precipitation ofFe(OH)3

    P/Fe initial = 0.18

    Formation of Fe hydroxyphosphates is very efficient process to immobilise dissolved phosphate

  • Effect of seepage of Fe-bearing groundwatermonitoring of phosphorus fractionation in surface water

    Sampling and chemical analysis of surface water and suspended particulate matter (SPM)• six catchments• 49 locations – from field ditch to catchment outlet• 96 samples – from winter to summer• Sampled SPM by filtration

  • Suspended Particulate Matter samples‘Fifty Shades of Brown’

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    Hunze Haarlemmermeer

  • Sequential chemical extraction

    Fractionate:• Dissolved P (ortho-P)• Loosely bound or

    exchangeable P • Organic P• Calcium-bound P• Iron-bound P• Residual P (apatite P)

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    high

    low

    bioavailability

    Particulate P

  • Results from field survey in six catchment

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    Fe-P = 0.62 x TPFe-P = 0.80 x PP

    Fractions of particulate P Fractions TP in surface water

  • Conceptual model of abiotic in-stream processes influencing phosphate transport

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    Removal of dissolved phosphate from solution by formation of Fe-hydroxyphosphate

    Transport of particulate phosphate as a function of hydrodynamics

  • Erodibility of soft sediments from drainage ditches and channels in polders

    Gust Erosion Microcosm System

    Van der Grift et al., 2017; In Prep.

    Samples from two areas

    • What forces are needed to erode bed sediment?• Where and how often are these forces reached in a polder?

    Undisturbed cylindrical sediment cores

    Erosion Chamber

  • Experimental results

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    Time interval vs. SPM concentration Critical bed shear stress (14 experiments)

  • Maximum bed shear stress during the period from March 2004 to April 2005

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    350 km watercourses (not including field ditches) 30 km where maximum bed shear stress > 0.1 Pa (erosion possible)

    Sobek-Delwaq model for polder Quarles van Ufford

    • Geographic setting of a polder tempers peak flow • Low maximum hydrodynamic forces that generally may not

    be strong enough to cause erosion of bed sediment• Polder function as peak runoff control system

  • Main conclusions

    • Discharge of Fe-bearing groundwater in combination the limited water flow in artificial and strongly managed watercourses reduce the environmental risk caused by P loads from diffuse agricultural sources.

    • Transport and ecological impact of P in surface waters are strongly controlled by the exfiltration of Fe-bearing groundwater

    • Flow-induced bed shear stress in watercourses in lowland catchment seldom exceeds the critical shear stress for erosion, which limits resuspension of particulate P

    • Sedimentation of particulate Fe-bound P results in a steady accumulation of a pool of ‘legacy P’ in bed sediments

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  • Van der Grift et al., 2014; HESS.

    Hupsel brook field experiment(Rozemeijer et al., 2010)

  • Measured and modelled PO4 concentrations upon aeration of groundwater

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    Maximum P/Fe ratio of Fe hydroxyphosphate ≈ 0.6

    • Experimental data from Griffioen (2006)• Modelled PO4 immoblisation by precipitation of Fe hydroxyphosphate (Fe2.5PO4(OH)4.5)

  • Fosfaat filtration steps

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