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Groundwater modelling
Schoonhovenseveer-LAngerak (SLA)
Regional to local modeling for dike stability
1 november 2016
Schoonhovenseveer - Langerak
Riverkilometers 965-983
983
965
Overview area with location of instable dikes
Dike instability
Water pressure exceeds weight of dyke body
Problem
• Sandy layers form connection between river and dike
• Water board Rivierenland prepares dike stability improvement
• Increasing height and width of dikes not always possible
• Other measures needed to lower water pressure
• Effect and efficiency of measures estimated in scenarios
• 3D dynamic groundwater model is needed
• Existing model (MORIA model) not suitable yet
• → Deltares refined the MORIA model
Stability under normal conditions
River
Sand layer
First aquifer
Dike
Instability under extreme conditions
River
Sand layer
First aquifer
Dike
Dike may become instable
Possible measure (1): increase river bed resistance
Sand layer
First aquifer
Dike
Possible measure (2): dam walls
River
Sand layer
First aquifer
Dike
Possible measure (3): horizontal drainage
River
Sand layer
First aquifer
Dike
Groundwatermodelling Waterschap Rivierenland
• Modellering Ondergrond Rivierenland Interactief en Actueel (since 2009)
• iMOD/ modeldatabase
• MORIA consortium: Waterschap Rivierenland, Provincie Gelderland, Vitens
• Several improvements have been made in recent years
 MORIA versie 3.2
Used on regional scale level
Average highest groundwaterlevel (m
below groundsurface)
Regional Exploration Freshwater Rivierenland
(Delta program)
For local applications: further detailing necessary
Sand extraction
Refinement of MORIA for the SLA project
• Holocene from 1 to 7 hydrogeological layers
→ 4 quasi-3D model layers
• From 25x25 to 5x5 meter resolution
• More detail in riverbed elevation
• More detail in other water courses
• Stability measure could be modelled (Grontmij, 2013)
• Groundwater monitoring filters
• Allocated vertically in the new layers
Example cross section
River cross section
GeoTOP and channel belts (sand)
• GeoTOP (TNO, 2012)
• Horizontal extent of hydrogeological
units
• Basic parameter values (K-values)
• Channel belts (“zandbanen”) (Cohen et
al., 2012)
Lek bottom elevation
Model layers
Hydogeological unit Sand (yellow) or clay/peat
(gray)
MORIA
model
SLA model
1 Antropogenic AN
1
1
2 Echteld sand/clay 1 EC1
2
3 Nieuwkoop peat NV
4 Echteld sand/clay 2a EC2a 3
5 Echteld sand/clay 2b EC2b
46 Basic peat (“basisveen”) BV
7 Wijchen clay WK
8 First aquifer (“WVP1”) WVP
2
5
3
4
6
5
6
7
7
8 8
9 9
Model layers 10 t/m 18
Vertical schematisation: use of iMOD
GEOTOP profiel
SECTION8KR.SPF (o.b.v. geotechnisch lengteprofiel, geïnterpoleerd met iMOD)
GeoTOP
Cross section
iMOD
Vertical schematisation
Insnijding in belangrijke
tussenzandlaag
Old MORIA model New SLA model
Surface water
kolkgaten
Old MORIA model New SLA model
Residuals: d(model, monitoringdata)
• Green: after calibration
• Red: before calibration
• Average: 0.018 meter
Scenario riverbed adjustment (Grontmij)
Effect during MHW (extremely high river level) on head in sandy layer
Scenario horizontal drainage (Grontmij)
Scenario dam walls (Grontmij)
Scenarios (Grontmij, 2013)
• River bed adjustment (closing holes) is only effective at one location
• Horizontal drainage has 20-50 cm effect on hydraulic head
underneath the dike
• This is potentially a usefull measure
• Dam walls are highly effective
• Effect is strongest at centre of dam wall
Discussion
• Model suitable to evaluate scenarios
• Always local research needed before measures are
constructed / carried out
• Resistance between river bed bottom and first aquifer is
very low:
• Erosion holes occur probably more frequently
• The basic peat layer is discontinuous?
• There still is a gap between monitoring data and model results:
• Still not enough detail?
• Problems in monitoring wells: position, construction, leaks?

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