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The effect of shoreface nourishments on the coastal ecosystem of The Netherlands

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A shoreface nourishment supplies sand in between the outer breaker bars along ... food source to sea ducks, for instance the common scoter Melanitta nigra. ... – PowerPoint PPT presentation

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Title: The effect of shoreface nourishments on the coastal ecosystem of The Netherlands


1
The effect of shoreface nourishments on the
coastal ecosystem of The Netherlands
  • Authors Martin Baptist Mardik Leopold

2
Shoreface nourishments
  • A shoreface nourishment supplies sand in between
    the outer breaker bars along the coast, or on the
    offshore side of the outer bar, at depths of
    about 5 to 8 metres below sea level.

3
Shoreface nourishments
4
Possible ecosystem effects
  • Direct effects
  • burial of benthic species.
  • suffocation of nearby benthos.
  • increased turbidity, possibly affecting primary
    production and/or the foraging success of
    predating fish and birds.
  • disturbance by noise and ship maneuvering.
  • Indirect effects
  • habitat change the bed level, the penetrability,
    the organic matter, grain size and silt content
    change.

5
Objectives of this study
  • This study investigated the relationships for
  • nourishments ? Spisula subtruncata ? sea ducks
  • nourishments ? fish ? fish-eating predators
  • Spisula subtruncata is a bivalve, living in sandy
    sediment and serving as an important food source
    to sea ducks, for instance the common scoter
    Melanitta nigra.

www.birdpix.nl
6
Spisula research
  • Since 1994, the number and distribution of
    Spisula is being monitored by IMARES.
  • Bed samples are taken with a bottom dredge.
  • Spisula is subdivided into a 0-year class and an
    adult class.

7
Spisula numbers and nourishments over time
  • By combining the temporal trend of Spisula
    numbers with nourished volumes along the Dutch
    coast one can find the relationship between
    Spisula presence and nourishments.

8
Spisula rise and fall per region
9
Nourishments
  • The change in morphology directly after the
    nourishment is found to be very local, without
    widespread effects.
  • The plume of suspended sediment will be
    transported in an alongshore direction and may
    stretch over several kilometers.
  • The possible effects of nourishments on Spisula
    in cross-shore direction are probably very local.

10
Spisula and nourishments in more detail
  • With Inverse Distance Weighting the original
    point data were interpolated, and extrapolated to
    the beach line, to yield complete coverage of
    Spisula density (numbers per m2) for the entire
    Dutch coast.
  • For each nourished coastal section we calculated
    the Spisula density
  • at the exact location of the nourishment (but
    this may be based on extrapolated data).
  • at an extended section down to the -20 m NAP
    depth contour (but this reaches out of the
    nourished range).
  • The results for a number of sections are
    presented.

11
Kijkduin Ter-Heijde 2001
  • This 3.6 Mm3 nourishment was applied over a
    length of 4.9 km.

12
Bergen aan Zee 2000
  • This 1 Mm3 nourishment was located in an area
    with high densities of 0-year Spisula, which
    stretched further offshore as well.

13
Groote Keeten Zwanewater 2003
  • This 2.57 Mm3 nourishment was located in an area
    where high densities of Spisula have been found
    until 2001.

14
Texel De Slufter 2004
  • A 2.4 Mm3 nourishment was applied over a length
    of 2.8 km.

15
Terschelling 1993
  • This shoreface nourishment of 2 Mm3 was applied
    over a length of approximately 4 km in between
    two breaker bars at a depth of -5 to -8 m NAP, at
    a distance of 800-1400 m from the beach pole
    line.

16
Conclusions
  • High density Spisula-banks were found along the
    northern Dutch coast in the second half of the
    1990s.
  • Since 2001, Spisula numbers are declining.
    Although shoreface nourishment volumes are
    increasing since 2001, we cannot state that there
    is a causal relationship.
  • Other causes may have triggered the decline of
    Spisula along the Dutch coast.

17
Discussion
  • Adult Spisula has been fished away.
  • The reproduction success of Spisula is highly
    variable. Factors that influence the reproduction
    success are
  • the wind direction and force during the pelagic
    larval phase.
  • presence, or rather absence, of dense banks of
    adult specimens in the neighbourhood.
  • climate change, resulting in a shortage of food
    or in physiological stress.
  • predation on spatfall by shrimp.
  • competition with Ensis americanus.
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