Presentation by Remi Caillibotte (Egis, France), Benjamin Jacob (Hereon, Germany) and Richard Marijnissen (Deltares, Netherlands) at the Delft3D User Days, during the Delft Software Days - Edition 2023 (DSD-INT 2023). Thursday, 16 November 2023, Delft.
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DSD-INT 2023 RESTCOAST ecotope quantification using D-Eco Impact - Caillibotte
1. This project receives funding from the European Union’s Horizon 2020 Research and Innovation action under grant agreement No 101037097.
RESTCOAST ecotope quantification
using D-Eco Impact
Richard Marijnissen (Deltares, Netherlands)
Remi Caillibotte (EGIS, France)
Benjamin Jacob (Hereon, Germany)
Delft 16/11/2023
2. REST-COAST
VISION:
Healthy and climate-resilient European coastal regions achieved through innovative large-scale
systemic restoration, enhance the delivery of ecosystem services and improve coastal biodiversity.
MISSION:
Demonstrate that upscaled coastal restoration can provide a low carbon footprint solution to climate
adaptation and disaster risk reduction for threatened coastal systems, combined with gains in their
biodiversity.
GOAL:
Overcome present hurdles to upscale coastal restoration interventions through new technical,
financial, management and transfer tools, aligned with the needs of coastal vulnerable regions and
society.
3.
4. • EUNIS ecotopes as a
“common language”
between pilots
• Provides semi-
quantitative insight in
ecosystem services
• Combined with IUCN
redlist provides
qualitative insight in
biodiversity
Ecotopes
Ecotope map for the the Wadden Sea, Baptist et al. (2019)
5. Use in REST-COAST
2) Local ecotope classes
3) Conversion to EUNIS ecostopes
1) Model results of scenario or measure
4) [Changes in] biotopes as indicator of restoration
success
Consistent application of
ecological rules using
D-Eco Impact
7. • Between 1989 and 2012, a decrease of the
spatial extent of eelgrass beds has been
observed:
• -38% for Zostera noltii
• -85% for Zostera marina
• Impact on:
• Tourism activities: 137 000 inhabitants but
400 000 people in summer; economic benefits
estimated at 346M€; recreational (bathing,
sport, …) and cultural (museums, Dune of
Pyla = 1.5M visitors) activities
• Dredging of harbour entrances
• Oyster farming: 780 ha; from 8 to 10 000
tons per year; Growing of juvenile oysters; 40
M€ of revenue; 1 000 employments)
• Fishery: 2000 tons/yr
• Land use w.r.t. coastal flooding: Klaus in
2009; Xynthia in 2010
Restoration of eelgrass beds in the Arcachon Bay
Source: Cognat, 2019
8. Impacts at stake
Ecosystem services targeted:
● (1) Coastal flooding control
● (2) Coastal erosion control
● (3) Water quality improvement
● (4) Carbon sequestration
Impacts considered:
● (1) Coastal flooding at coastal sites inside
the Arcachon lagoon
● (2) Erosion of main channels and
sedimentation of harbor entrances
● (3) Turbidity, Water renewal (flushing time)
● (4) Specific/classic sediment dynamics and
distribution inside the lagoon
→ Link with WP1
10. D-Flow FM module
• 2D computation on a curvilinear grid
• Processes involved:
• Tide-driven flows
• Wind-driven flows
• Wave-driven flows (coupling with D-Waves)
D-Morphology module
• Bedload and suspended load transport
of cohesive and non-cohesive sediment
• Bed level update
• Morphological acceleration factor
Coastal eco-morphodynamic model Bathymetry
Flow
Boundary
conditions
Sediment
transport
Bed update
Hydro. time
Morpho. time
x13
11. Vegetation module
• Trachytopes (Baptist 2005; Baptist et al. 2007):
• Inputs:
• Fixed vegetation: cover corresponding to 2012
• Sensitivity analysis (e.g. regarding seasonality)
• Minor differences on water levels
• Max differences of 4 cm.s-1 for tidal currents
Cover
Height
(cm)
Density
(m-1)
Drag
coefficient
< 0.25 12 13.6
0.7
0.25 < . < 0.75 16 27.3
> 0.75 20 53.5
12. ● Non-neutral impact of the vegetation on sediment dynamics within the Arcachon Bay
● Restoration of vegetation could lead to:
• A decrease of sediment deposition on the bottom on the Bay
• An erosion of secondary channels (improving hydrodynamics)
● Risk assessment for coastal flooding and erosion risk
● New restoration scenarios to be integrated
Conclusions and perspectives on modelling works
13. ● Future changes in term of biotopes as indicators of restoration
success
● Application of the D-Eco Impact tool with conditions adapted to
Wadden sea pilot site → Proof of concept
→ Improvements for Arcachon Bay must be made and particularly on
seagrass and salt marshes classifications
Ecotopes mapping for Arcachon Bay
15. Model
Hereon
15
source:
http://ccrm.vims.edu/schismweb/
SCHISM
• 3D, RANS-Equations on unstructured grids
• Robust matrix solver following an efficient
semi-implicit time stepping schemes
• Includes Higher-order transport solver: TVD2
• Includes a variety of functional modules
WWM -III
• Wave Action balance Equation on an unstructured mesh.
• 3rd generation wave model
• ST4 physics Ardhuin et al. (2010)
SED3D
• 3D Sediment model for non-cohesive sediments
• Based on Community Sediment Transport Model (Warner et al., 2008).
• unstructured grid adaption (Pinto et al. (2012)
• Erosion/deposition/bedload of 8 Sediment Classes (0.06-2 mm)
German Bight ugrid downscaling configuration
Hydrodynamic (h)
B.C.
AMM15
WW3
Elements/Nodes
900000/480000
1.5 km - 50 m dx
21 vertical S-layers
90s dt
Wave
Spectra(h)
16. Hereon
16
• Present day scnerios,
• End of the century climate
projections
Seagrass as nature based solution
Physical
Parameters
17. D-Eco Impact – Preliminary results
Early stage work in progress …
• SCHISM output not yet ugrid conform
• Preprocessing scripts for conversion of
schism output (further work required)
Hereon
17