Suspended matter in the Scheldt estuary

The Scheldt estuary is characterised by a specific energy pattern resulting from the interaction of wave energy, tidal energy and river energy. It divides the estuary into three parts and governs suspended matter transport and distribution pattern. Observation of suspended matter transport shows the existence of three estuarine turbidity maxima (ETM), a marine-dominated ETM in the lower estuary at the river mouth, a river-dominated ETM in the upper estuary with suspended matter concentration reaching up to 300 mg/l, and the most important tide-dominated ETM in the middle estuary with suspended matter concentrations from several hundred milligrams per litre up to a few grams per litre. Resuspension is the dominant phenomenon in this last ETM due to the tidal related bottom scour, which is initiated when a critical erosion velocity of 0.56 m/s is exceeded. An assessment of residual current along the axis of the estuary shows distinctive pattern between the surface water flow and the near bottom water flow. Also the local morphology of the river, natural or man-made, has a prominent effect on the orientation and strength of the residual currents flowing along either side of the river or river bend. Evaluation of suspended matter concentration in relation to the current flow shows no systematic correlation either because of phenomena as scour lag and settling lag mainly in the middle estuary, or because of the current independency character of uniform-suspension mainly in the upper and lower estuary. Quantification of suspended matter load exhibits a net downstream transport from the upper estuary, a near-equilibrium sustainable status in the middle estuary and a net upstream transport of suspended matter from the lower estuary. The characteristic of suspended matter is induced by and is a function of e.g. tidal phase, spring-neap tide, longitudinal and vertical distribution mechanisms, seasons, short and long terms of anthropogenic influence and/or estuarine maintenance. Suspended matter is dominated by complex and cohesive organo-mineral aggregates. It consists of a variable amount of an inorganic fraction (average of 89%) and an organic fraction and occurs largely as flocs, the size of which is remarkably larger in the upper estuary and smallest within the ETM in the middle estuary. Independent time series measurements (1990–2000) of suspended matter property show an increasing sand fraction, a decreasing organic matter content, a rise in δ13C as well as a decrease in water transparency. These independent measurements exhibit coherent consequences of estuarine maintenance operations. Maintenance dredging of the shipping channel and harbours and dumping operation in the Scheldt strengthen marine influence further landward, resulting in a sustained tidal range increment and upstream flow and transport of suspended matter.

[1]  Johan C. Winterwerp,et al.  A new morphological schematization of the Western Scheldt estuary, The Netherlands , 2001 .

[2]  B. Fry,et al.  δ13C Measurements as Indicators of Carbon Flow in Marine and Freshwater Ecosystems , 1989 .

[3]  W. Baeyens,et al.  Mercury in the Southern North Sea and Scheldt estuary , 2001 .

[4]  R. Wollast The Scheldt Estuary , 1993 .

[5]  A. Sandee,et al.  Nutrients, light and primary production by phytoplankton and microphytobenthos in the eutrophic, turbid Westerschelde estuary (The Netherlands) , 1995, Hydrobiologia.

[6]  J. Salomon,et al.  Effects of tides on mixing and suspended sediment transport in macrotidal estuaries , 1980 .

[7]  S. Gale,et al.  Quaternary sediments : petrographic methods for the study of unlithified rocks , 1991 .

[8]  Jaak Monbaliu,et al.  Seasonal, neap-spring and tidal variation of cohesive sediment concentration in the Scheldt Estuary, Belgium , 1998 .

[9]  W. Vyverman,et al.  Spatial and Temporal Dynamics of Phytoplankton Communities in a Freshwater Tidal Estuary (Schelde, Belgium) , 2000 .

[10]  J. Dupont,et al.  Hydrodynamics of suspended particulate matter in the tidal freshwater zone of a macrotidal estuary (the Seine Estuary, France) , 1999 .

[11]  D. Huntley,et al.  Size and settling velocity distributions of flocs in the Tamar estuary during a tidal cycle , 1994, Netherland Journal of Aquatic Ecology.

[12]  P. Meire,et al.  Het "bijzondere" van de Schelde: de abiotiek van het Schelde-estuarium , 2001 .

[13]  CLAY MINERALS,et al.  Clay Minerals , 2004 .

[14]  J. Hayes,et al.  Refined estimation of marine and terrigenous contributions to sedimentary organic carbon , 1993 .

[15]  J. Middelburg,et al.  Carbon and nitrogen stable isotopes in suspended matter and sediments from the Schelde Estuary , 1998 .

[16]  J. Cloern The relative importance of light and nutrient limitation of phytoplankton growth: a simple index of coastal ecosystem sensitivity to nutrient enrichment , 1999, Aquatic Ecology.

[17]  C. Heip,et al.  Biogeochemistry of the MAximum TURbidity Zone of Estuaries (MATURE): some conclusions , 1999 .

[18]  Jeffrey E. Richey,et al.  Compositions and fluxes of particulate organic material in the Amazon River1 , 1986 .

[19]  M. Laan,et al.  A camera and image-analysis system for in situ observation of flocs in natural waters , 1990 .

[20]  P. Herman,et al.  Nitrogen dynamics in the Westerschelde estuary (SW Netherlands) estimated by means of the ecosystem model MOSES , 1995, Hydrobiologia.

[21]  W. Baeyens,et al.  Dissolved inorganic carbon in a highly polluted estuary (the Scheldt) , 2001 .

[22]  J. R. West,et al.  Depth-mean tidal current and sediment concentration relationships in three partially mixed estuaries , 1991 .

[23]  C. Heip,et al.  Production and consumption of biological particles in temperate tidal estuaries , 1995 .

[24]  J. Kromkamp,et al.  Estimation of phytoplankton photosynthesis and nutrient limitation in the Eastern Scheldt estuary using variable fluorescence , 1999, Aquatic Ecology.

[25]  C. Lambert,et al.  General description of the Scheldt estuary , 2004, Hydrobiologia.

[26]  P. Herman,et al.  Living in the twilight: estimating net phytoplankton growth in the Westerschelde estuary (The Netherlands) by means of an ecosystem model (MOSES) , 1994 .

[27]  J. Kromkamp,et al.  Primary production of phytoplankton in a turbid coastal plain estuary, the Westerschelde (The Netherlands) , 1993 .

[28]  M. Fettweis,et al.  The mud deposits and the high turbidity in the Belgian–Dutch coastal zone, southern bight of the North Sea , 2003 .

[29]  R. Gibbs,et al.  Coagulation and transport of sediments in the Gironde Estuary , 1989 .

[30]  P. Meire,et al.  δ15N and δ13C dynamics of suspended organic matter in freshwater and brackish waters of the Scheldt estuary , 2002 .

[31]  D. Schoellhamer Comparison of the basin-scale effect of dredging operations and natural estuarine processes on suspended sediment concentration , 2002 .

[32]  R. Dalrymple,et al.  Estuarine Facies Models: Conceptual Basis and Stratigraphic Implications: PERSPECTIVE , 1992 .

[33]  N. Flemming Multiple regression analysis of earth movements and eustatic sea-level change in the United Kingdom in the past 9000 years , 1982 .

[34]  W. Baeyens,et al.  Numerical Simulations of Salinity, Turbidity and Sediment Accumulation in the Scheldt Estuary , 1981 .

[35]  M. Donze,et al.  MarinevsFluvial Suspended Matter in the Scheldt Estuary , 1998 .

[36]  L. Taverne Sur la position systématique et les affinités de Greenwoodella tockensis Taverne, L. et Ross, P. H. 1973 (Pisces Elopiformes) de l'Aptien inférieur de l'île d'Helgoland (Allemagne) , 1973 .

[37]  Timothy G. Milligan,et al.  In situ particle (floc) size measurements with the benthos 373 plankton silhouette camera , 1996 .

[38]  K. Sabbe,et al.  Cyclotella scaldensis spec nov (Bacillariophyceae), a new estuarine diatom , 1996 .

[39]  P. Raymond,et al.  Use of 14C and 13C natural abundances for evaluating riverine, estuarine, and coastal DOC and POC sources and cycling: a review and synthesis , 2001 .

[40]  D. Eisma,et al.  Flocculation and de-flocculation of suspended matter in estuaries , 1986 .

[41]  J. Nihoul,et al.  Hydrodynamics of the Scheldt Estuary , 1978 .

[42]  H. A. Einstein,et al.  Experiments to determine modes of cohesive sediment transport in salt water , 1962 .

[43]  C. Baeteman,et al.  A synthesis of early and middle Holocene coastal changes in the western Belgian lowlands , 2002 .

[44]  E. Wolanski,et al.  DYNAMICS OF THE TURBIDITY MAXIMUM IN THE FLY RIVER ESTUARY, PAPUA-NEW-GUINEA , 1995 .