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Role of physical and biological processes in sediment dynamics of a tidal flat in Westerschelde Estuary, SW Netherlands
Widdows, J.; Blauw, A.; Heip, C.H.R.; Herman, P.M.J.; Lucas, C.H.; Middelburg, J.J.; Schmidt, S.; Brinsley, M.D.; Twisk, F.; Verbeek, H. (2004). Role of physical and biological processes in sediment dynamics of a tidal flat in Westerschelde Estuary, SW Netherlands. Mar. Ecol. Prog. Ser. 274: 41-56. https://hdl.handle.net/10.3354/meps274041
In: Marine Ecology Progress Series. Inter-Research: Oldendorf/Luhe. ISSN 0171-8630; e-ISSN 1616-1599, meer
Peer reviewed article  

Beschikbaar in  Auteurs 

Trefwoorden
    Aquatic communities > Benthos
    Erosion
    Modelling
    Physics > Mechanics > Dynamics > Sediment dynamics
    Sediment mixing > Bioturbation
    Sedimentation
    ANE, Nederland, Westerschelde, Molenplaat [Marine Regions]
    Marien; Brak water
Author keywords
    sediment dynamics; erosion; sedimentation; mixing; microphytobenthos;biostabilisation; bioturbation; modelling

Auteurs  Top 
  • Widdows, J., meer
  • Blauw, A.
  • Heip, C.H.R., meer
  • Herman, P.M.J., meer
  • Lucas, C.H., meer
  • Middelburg, J.J., meer
  • Schmidt, S.
  • Brinsley, M.D.
  • Twisk, F., meer
  • Verbeek, H., meer

Abstract
    This article synthesises a series of studies concerned with physical, chemical and biological processes involved in sediment dynamics (sedimentation, erosion and mixing) of the Molenplaat tidal flat in the Westerschelde (SW Netherlands). Total sediment accretion rate on the flat (sand to muddy sand) was estimated to be ~2 cm yr-1, based on 210Pb and 137Cs profiles. 7Be showed maximum activity in the surface sediments during summer, reflecting accretion of fine silt at this time of year, and total vertical mixing of sediment to be in the order of 50 cm2 yr-1. The extent to which different physical and biological processes (tidal currents, air exposure, bio-stabilisation, biodeposition and bioturbation) contributed towards sediment dynamics was estimated. A sediment transport model based on physical factors estimated sedimentation rates of 1.2 cm yr-1, but did not account for tidal or seasonal variation in suspended particulate matter (SPM), wind or effects of spring-neap tidal cycles. When the model was run with an increased critical bed shear stress due to the microphytobenthos, net sedimentation rates increased 2-fold. These higher rates were in closer agreement with the rates derived from the depth profiles of radionuclides for the central region of the tidal flat (2.0 to 2.4 cm yr-1). Therefore a significant part of the sedimentation rate (~50%) may be explained by spatial-temporal changes in biological processes, including 'bio-stabilisation' by microphytobenthos, together with the enhanced biodeposition of silt by suspension feeders, and offset by processes of 'bio-destabilisation' by grazers and bioturbators. In the centre of the tidal flat there was a shift from high sediment stability in spring-summer 1996 to low sediment stability in autumn 1997, quantified by a significant reduction in critical erosion velocity of 0.12 to 0.15 m s-1, and accompanied by a 30- to 50-fold increase in sediment erosion rate. The change was associated with a shift from a tidal flat dominated by benthic diatoms and a low biomass of bioturbating clams (Macoma balthica), to a more erodable sediment with a lower microphytobenthos density and a higher biomass of M. balthica. Vertical mixing of sediment and organic matter, studied using a variety of tracers, was rapid and enhanced by advective water flow at sandy sites and by burrowing polychaetes and bivalves at silty sites.

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