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Morphological challenges: morphological impact
resulting from the demands of the individual interests



                                    RESTORE – WORKSHOP
                                           Part 2
                Sharing River restoration knowledge and experience in Europe,
                                  Iaşi-ROMANIA, 9-11 May 2012




                                   Hendrik Havinga
                                                                                1




  Dutch Ministry of Infrastructure and Environment
  Rijkswaterstaat              Oost Nederland
River restoration topics

•   Goals (increase bio-diversity)
•   River functions
•   Current situation (natural river, regulated river, physics)
•   Restoration measures problems (challenge..)
•   Mitigating measures
•   Monitoring
•   Maintenance
•   Administration processes
Mitigating measures/maintenance

• Removal of vegetation
• Dredging
• Structural measures
Removal of vegetation

• Cutting trees, etc.
• Concept of cyclic rejuvenation in the floodplains
   – Measures are taken to restore the discharge capacity
     and increase natural diversity. These measures
     “rejuvenate” the area, e.g. silted up floodplains are
     excavated, on the bare ground pioneer vegetation will
     start to develop, thus restarting vegetation succession.
General concept of Cyclic
                Rejuvenation
• Cyclic sediment- and vegetation management: solution to
  combine flood protection and ecological rehabilitation
• Measures to restore the discharge capacity and to
  increase natural diversity, “rejuvenate” the area, e.g.
  excavation of silted up floodplains. On the bare ground
  pioneer vegetation will start to develop, thus restarting
  vegetation succession
• Tailormade approaches
• Demands: Expertise of hydraulics + morphology,
  ecological processes, flexibility
Design of Cyclic rejuvenation
                measures
•   Knowledge of ecological processes
•   Knowledge of river engineering
•   Socio-economic factors
•   Success factors
     – Legislation: Flood protection, dike stability, flora and
       fauna, forestry, bird- and habitat, environment, soil
       management, water pollution, Water Framework
       Directive (WFD).
     – Small environmental impact
     – Reduced maintenance. Innovative techniques are
       important:
        • Precise dealing with (contaminated) soil
        • Sub-suction of sand (leaving the top layer intact)
        • Complete removal of trees (including roots).
Cyclic rejuvenation of
               floodplains




Use of innovative techniques: Subsuction of sand
Dredging

• ..and dumping to reduce bed erosion
Dredging instead of structural measures
• Consequences of dredging: hampering of navigation, increase of
  maintenance, decrease of flood protection, CO2 emissions
• However, dredging is cheaper than structural measures




                                                                   9
Manners to cope with the
                   situation
1. Accept the consequences of dredging.
2. Start with dredging operations and begin developing mitigating
   measures. In time reduce dredging efforts by executing structural
   measures
3. Include mitigating structural measures in the Room for the River and
   WFD projects
1. Accept the consequences

•   Natural banks and side channels will enforce dynamic river
    management concepts. This means regular monitoring of vegetation
    succession and morphological changes, checks of floodlevels and
    sailing depths. On an irregular basis maintenance is required.
•   Estimated increase in maintenance costs (Netherlands): 3 M
    Euro/year for 200 km of river, or 15,000 euro/km/yr.
•   5-10 % of time the sailing depth’s will be less than optimal, leading to
    higher transport costs, estimated 15 M Euro/yr. This may effect a
    change in the transport modal split, i.e. more cargo by truck (>CO2).
•   If maintenance is neglected also flood safety is at stake.
2. Start dredging, develop
                     structural measures
•   Dredged material has to be redeposited in the low water bed, to limit
    further longitudinal bed erosion.
•   As dredging has become rather cheap, capitalisation of this
    maintenance results in limited capital for structural measures.
•   Reduction of dredging amounts are achieved by structural measures.
    Irrigation scheme solutions might help.
•   The dredged spoil and vegetation waste could be used to build
    temporariy structures that limit shoaling.
Structural measures

•   Groyne adaptations near inlets and outlets
•   Guide bunds
•   Longitudinal dams
•   Inlet structures
Mitigating measures to
                 reduce impact of free
•                banks:
    Forebank protection, longitudinal dams, Island groynes
Example of temporary
 sructure
Groyne field protections made of vegetation
palenrij
                  Doorsnede
wilgenschern
geotextiel
sedimentvulling
The idea is to use these structures to minimise dredging,
                 within a program called
              Self Supporting River System
The Self Supporting River System
                           (SSRS)
• Natural morpho-dynamics and available ‘spoil’ (sand and
  vegetation) are used to solve bottle-necks in a structural way
• This leads to reduction of cost
• The use of natural products like biomass, sand and clay is
  optimised to finance maintenance efforts
Maintenance according to
•                 SSRS
    Small-scale changes in the river lay-out create a natural
  equilibrium locally (e.g. local constrictions)
• SSRS means: search for the local natural equilibria that
  solve local problems
• This is called “maintenance (building) with nature”,
SSRS-example: natural longitudinal
•                               dam
    “Gabions” can be made from vegetation waste and
  dredged spoil
• Estimated lifetime: 2-6-10 (?) years
• Can be the basis for a tradional dam made of tissue
  and stone revetment, that is made later on, when more
  budget is available
• In the meantime research can be carried out
Reduction of maintenance

• Adequate design of structures/measures
• No attitude “we will see what happens..”
• Example of this attitude in next slides of Gameren side
  channels
Increasing flow conveyance :
  The Gameren floodplain
           June 2000
Upstream view
South and East channels
Downstream view
 South and West channels
Erosion at intakes
Erosion of groyne root
Dealing with side channels:
                limiting uncertainties
Applying a Dynamic River Management System:
   – Quick-scan monitoring systems
   – Adequate Data storage and presention (GIS)
   – Impact assesment/design of measures
     using 2-D hydraulic and morphological models
   – Quick implementation of correcting measures
Use of inlet structures to limit
           sedimentload
• Use sandtraps near the upstream end of side channels
• Use surface screens and bottom vanes to direct the
  sediment to a preferred (dredging-) site.
• Sills
Surface screen (‘bandall’)




From MSc. Thesis of Siem Troost (TU-Delft):
“Experimental research on the effects of surface screens on a mobile bed”
                                                                            33
Solutions for intakes for side
                channels

• Limited sediment inflow
• No hampering of navigation
• Moderate cost of construction and later adjustments
Sediment control methods



                       Curative




Preventive




   Overview of sediment handling methods
   (Eichenberger, 2001)
Preventive measures
Siting of intake at outer bend


                                 Intake at
                                 outer bend



 Alignment of intake
Sediment excluding methods


Raised entrance sill
Bottom vanes

Submerged vanes in front of intake




           Conceptual flow pattern
Vortex tubes Across the river
                                   Partially from the river bank

                                                            Secondary channel


                                                 Bed material
                                    River flow




Other preventive measures:
Skimming wall
Sloped training walls
Bottom/surface deflectors
Concave- convex guide walls
Undersluices
Tunnel (vortex) excluders
Barrage regulation
Monitoring

• Ecological monitoring
• Vegetation succession (flood levels)
• Morphology
Ecological monitoring

• In the Netherlands a Hydromorphological monitoring
  handbook is used. Description of 45 parameters to
  monitor.
• Some results from study ‘Rhine in the picture’ (Rijn in
  Beeld).
Project Ewijkse Plaat
Ewijkse Plaat




Situation 1989
Vegetation changes 1992- 2009
Plan for extra channels
Gameren side channels




                        Situation 1995
Actual situation
Developments in
special plants
1980-2009
Distribution of
special plants
2009
Development in Waterplants and pioneer
vegetation since 1987
Developments in birds
Developments in
Bankswallows
Processes organisation
The increase of ecological
                 potentials of riverbanks and
                 floodplains requires:
•   Application of a Dynamic River Management System:
•   Changes in river administration methods (cooperation, active
    management)
•   Conditions for succes are: money, research, adequate river
    management, tailor made approaches
Dynamic River Management

Separate presentation: DRM explanation
Monitoring

•   Hydraulic monitoring: waterlevels and discharges through side
    channels. Indications for silting up.
•   Echo-sounding for bathymetry
•   Frequency of Monitoring
Detailpeilingen Slijk-Ewijk - km 889 - 891 - (-3.20m)   2-8-1998
Multibeam echolood meting

                            • Kribben bij
                              Haaften
                            • November
                              2002
                            • Meetdienst
                              DON




1-11-2004
Parameter               Mapping scale   Frequency

Vegetation

Thicket and Forest      Visual survey   1 / year

Vegetation structures   1:5.000         1/5 year

Morphology

Bedlevel floodplain     1:5.000         1/10 year
(including
embankments)
Bedlevel of             1:5.000         1/5 year
secondary channels
and lakes
Erosion near            Visual survey   After every high
constructions                           discharge




Frequency of Monitoring
Administration processes

•   Different responsibilities:
     – Terrain manager -> nature management
     – River manager -> reliable river works, flood protection, good
       inland navigation
•   So… Transparent communication is necessary
•   Expert team to bridge the gap!
Planning and design of
                     projects

•   Use 1D and 2D morphological analyses
•   Projects in river system must be technically sound to safeguard all the
    functions of the river, otherwise opposition against river restoration
    may rise
•   Establish a masterplan with defined targets concerning:
     – The river’s dynamic equilibrium: bed levels, sedimenttransport
       capacities.
     – Navigation channel dimensions (width and Least Available Depth
       during low (5%) discharges). This requires a reference waterlevel
       going with this low discharge.
•   The impact of individual projects may not sustainably change these
    targets.
Discussion

• What is the first thing you will discuss at home ?
End of part 2




Thank you for your attention !
Literature

Breen, L.E. van, Jesse, P, Havinga, H 2005: River restoration from a river manager’s point
    of view. In: Rehabilitating large regulated rivers, Proceedings of Lownland River
    Rehabilitation Conference (Archiv für Hydrobilologie), Wageningen, 2003.
    Schweizerbart’sche Verlagsbuchhandlung, Stuttgart.
Ghimire, B. 2003: No-regret solutions for intakes for secondary channels. M.Sc. Thesis.
    International Institute for Infrastructural, Hydraulic and Environmental Engineering
    (IHE), Delft.
Havinga, H. & Smits, A.J.M. 2000. River management along
    the Rhine: a retrospective view. In: Smits, A.J.M., Nienhuis, P.H. & Leuven, R.S.E.W.
    (Eds.). New Approaches to River Management, Backhuys Publishers, Leiden, pp. 15-32
Havinga, H. & Smits, A.J.M. 2000: River management along the Rhine: A retrospective
    view. In: Smits, A.J.M., Nienhuis, P.H. & Leuven, R.S.E.W. (Editors.) - New Approaches
    to River Management. Backhuys Publishers, Leiden.
Peters, B., Kater, E., Geerling, G. 2006: Cyclic management in floodplains (in Dutch).
    Centrum voor Water en Samenleving, Radboud University, Nijmegen.
PIANC, EnviCom Working Group 107 2009. Sustainable Waterways Within The Context of
    Navigation and Flood Management.
PIANC, 2003. Guidelines for sustainable inland waterways and navigation, Report of
    working group 6.
Sustainable Development of Floodplains, report:
    http://www.ecrr.org/sdfproject/sdfproject.htm

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120512 Iasi morphology part 2 - Mr Hendrik Havinga

  • 1. Morphological challenges: morphological impact resulting from the demands of the individual interests RESTORE – WORKSHOP Part 2 Sharing River restoration knowledge and experience in Europe, Iaşi-ROMANIA, 9-11 May 2012 Hendrik Havinga 1 Dutch Ministry of Infrastructure and Environment Rijkswaterstaat Oost Nederland
  • 2. River restoration topics • Goals (increase bio-diversity) • River functions • Current situation (natural river, regulated river, physics) • Restoration measures problems (challenge..) • Mitigating measures • Monitoring • Maintenance • Administration processes
  • 3. Mitigating measures/maintenance • Removal of vegetation • Dredging • Structural measures
  • 4. Removal of vegetation • Cutting trees, etc. • Concept of cyclic rejuvenation in the floodplains – Measures are taken to restore the discharge capacity and increase natural diversity. These measures “rejuvenate” the area, e.g. silted up floodplains are excavated, on the bare ground pioneer vegetation will start to develop, thus restarting vegetation succession.
  • 5. General concept of Cyclic Rejuvenation • Cyclic sediment- and vegetation management: solution to combine flood protection and ecological rehabilitation • Measures to restore the discharge capacity and to increase natural diversity, “rejuvenate” the area, e.g. excavation of silted up floodplains. On the bare ground pioneer vegetation will start to develop, thus restarting vegetation succession • Tailormade approaches • Demands: Expertise of hydraulics + morphology, ecological processes, flexibility
  • 6. Design of Cyclic rejuvenation measures • Knowledge of ecological processes • Knowledge of river engineering • Socio-economic factors • Success factors – Legislation: Flood protection, dike stability, flora and fauna, forestry, bird- and habitat, environment, soil management, water pollution, Water Framework Directive (WFD). – Small environmental impact – Reduced maintenance. Innovative techniques are important: • Precise dealing with (contaminated) soil • Sub-suction of sand (leaving the top layer intact) • Complete removal of trees (including roots).
  • 7. Cyclic rejuvenation of floodplains Use of innovative techniques: Subsuction of sand
  • 8. Dredging • ..and dumping to reduce bed erosion
  • 9. Dredging instead of structural measures • Consequences of dredging: hampering of navigation, increase of maintenance, decrease of flood protection, CO2 emissions • However, dredging is cheaper than structural measures 9
  • 10. Manners to cope with the situation 1. Accept the consequences of dredging. 2. Start with dredging operations and begin developing mitigating measures. In time reduce dredging efforts by executing structural measures 3. Include mitigating structural measures in the Room for the River and WFD projects
  • 11. 1. Accept the consequences • Natural banks and side channels will enforce dynamic river management concepts. This means regular monitoring of vegetation succession and morphological changes, checks of floodlevels and sailing depths. On an irregular basis maintenance is required. • Estimated increase in maintenance costs (Netherlands): 3 M Euro/year for 200 km of river, or 15,000 euro/km/yr. • 5-10 % of time the sailing depth’s will be less than optimal, leading to higher transport costs, estimated 15 M Euro/yr. This may effect a change in the transport modal split, i.e. more cargo by truck (>CO2). • If maintenance is neglected also flood safety is at stake.
  • 12. 2. Start dredging, develop structural measures • Dredged material has to be redeposited in the low water bed, to limit further longitudinal bed erosion. • As dredging has become rather cheap, capitalisation of this maintenance results in limited capital for structural measures. • Reduction of dredging amounts are achieved by structural measures. Irrigation scheme solutions might help. • The dredged spoil and vegetation waste could be used to build temporariy structures that limit shoaling.
  • 13. Structural measures • Groyne adaptations near inlets and outlets • Guide bunds • Longitudinal dams • Inlet structures
  • 14. Mitigating measures to reduce impact of free • banks: Forebank protection, longitudinal dams, Island groynes
  • 16. Groyne field protections made of vegetation
  • 17.
  • 18. palenrij Doorsnede wilgenschern geotextiel sedimentvulling
  • 19. The idea is to use these structures to minimise dredging, within a program called Self Supporting River System
  • 20. The Self Supporting River System (SSRS) • Natural morpho-dynamics and available ‘spoil’ (sand and vegetation) are used to solve bottle-necks in a structural way • This leads to reduction of cost • The use of natural products like biomass, sand and clay is optimised to finance maintenance efforts
  • 21. Maintenance according to • SSRS Small-scale changes in the river lay-out create a natural equilibrium locally (e.g. local constrictions) • SSRS means: search for the local natural equilibria that solve local problems • This is called “maintenance (building) with nature”,
  • 22. SSRS-example: natural longitudinal • dam “Gabions” can be made from vegetation waste and dredged spoil • Estimated lifetime: 2-6-10 (?) years • Can be the basis for a tradional dam made of tissue and stone revetment, that is made later on, when more budget is available • In the meantime research can be carried out
  • 23. Reduction of maintenance • Adequate design of structures/measures • No attitude “we will see what happens..” • Example of this attitude in next slides of Gameren side channels
  • 24. Increasing flow conveyance : The Gameren floodplain June 2000
  • 25. Upstream view South and East channels
  • 26. Downstream view South and West channels
  • 29.
  • 30.
  • 31. Dealing with side channels: limiting uncertainties Applying a Dynamic River Management System: – Quick-scan monitoring systems – Adequate Data storage and presention (GIS) – Impact assesment/design of measures using 2-D hydraulic and morphological models – Quick implementation of correcting measures
  • 32. Use of inlet structures to limit sedimentload • Use sandtraps near the upstream end of side channels • Use surface screens and bottom vanes to direct the sediment to a preferred (dredging-) site. • Sills
  • 33. Surface screen (‘bandall’) From MSc. Thesis of Siem Troost (TU-Delft): “Experimental research on the effects of surface screens on a mobile bed” 33
  • 34. Solutions for intakes for side channels • Limited sediment inflow • No hampering of navigation • Moderate cost of construction and later adjustments
  • 35. Sediment control methods Curative Preventive Overview of sediment handling methods (Eichenberger, 2001)
  • 36. Preventive measures Siting of intake at outer bend Intake at outer bend Alignment of intake
  • 38. Bottom vanes Submerged vanes in front of intake Conceptual flow pattern
  • 39. Vortex tubes Across the river Partially from the river bank Secondary channel Bed material River flow Other preventive measures: Skimming wall Sloped training walls Bottom/surface deflectors Concave- convex guide walls Undersluices Tunnel (vortex) excluders Barrage regulation
  • 40. Monitoring • Ecological monitoring • Vegetation succession (flood levels) • Morphology
  • 41. Ecological monitoring • In the Netherlands a Hydromorphological monitoring handbook is used. Description of 45 parameters to monitor. • Some results from study ‘Rhine in the picture’ (Rijn in Beeld).
  • 45. Plan for extra channels
  • 46. Gameren side channels Situation 1995
  • 50. Development in Waterplants and pioneer vegetation since 1987
  • 54. The increase of ecological potentials of riverbanks and floodplains requires: • Application of a Dynamic River Management System: • Changes in river administration methods (cooperation, active management) • Conditions for succes are: money, research, adequate river management, tailor made approaches
  • 55. Dynamic River Management Separate presentation: DRM explanation
  • 56. Monitoring • Hydraulic monitoring: waterlevels and discharges through side channels. Indications for silting up. • Echo-sounding for bathymetry • Frequency of Monitoring
  • 57. Detailpeilingen Slijk-Ewijk - km 889 - 891 - (-3.20m) 2-8-1998
  • 58. Multibeam echolood meting • Kribben bij Haaften • November 2002 • Meetdienst DON 1-11-2004
  • 59. Parameter Mapping scale Frequency Vegetation Thicket and Forest Visual survey 1 / year Vegetation structures 1:5.000 1/5 year Morphology Bedlevel floodplain 1:5.000 1/10 year (including embankments) Bedlevel of 1:5.000 1/5 year secondary channels and lakes Erosion near Visual survey After every high constructions discharge Frequency of Monitoring
  • 60. Administration processes • Different responsibilities: – Terrain manager -> nature management – River manager -> reliable river works, flood protection, good inland navigation • So… Transparent communication is necessary • Expert team to bridge the gap!
  • 61. Planning and design of projects • Use 1D and 2D morphological analyses • Projects in river system must be technically sound to safeguard all the functions of the river, otherwise opposition against river restoration may rise • Establish a masterplan with defined targets concerning: – The river’s dynamic equilibrium: bed levels, sedimenttransport capacities. – Navigation channel dimensions (width and Least Available Depth during low (5%) discharges). This requires a reference waterlevel going with this low discharge. • The impact of individual projects may not sustainably change these targets.
  • 62. Discussion • What is the first thing you will discuss at home ?
  • 63. End of part 2 Thank you for your attention !
  • 64. Literature Breen, L.E. van, Jesse, P, Havinga, H 2005: River restoration from a river manager’s point of view. In: Rehabilitating large regulated rivers, Proceedings of Lownland River Rehabilitation Conference (Archiv für Hydrobilologie), Wageningen, 2003. Schweizerbart’sche Verlagsbuchhandlung, Stuttgart. Ghimire, B. 2003: No-regret solutions for intakes for secondary channels. M.Sc. Thesis. International Institute for Infrastructural, Hydraulic and Environmental Engineering (IHE), Delft. Havinga, H. & Smits, A.J.M. 2000. River management along the Rhine: a retrospective view. In: Smits, A.J.M., Nienhuis, P.H. & Leuven, R.S.E.W. (Eds.). New Approaches to River Management, Backhuys Publishers, Leiden, pp. 15-32 Havinga, H. & Smits, A.J.M. 2000: River management along the Rhine: A retrospective view. In: Smits, A.J.M., Nienhuis, P.H. & Leuven, R.S.E.W. (Editors.) - New Approaches to River Management. Backhuys Publishers, Leiden. Peters, B., Kater, E., Geerling, G. 2006: Cyclic management in floodplains (in Dutch). Centrum voor Water en Samenleving, Radboud University, Nijmegen. PIANC, EnviCom Working Group 107 2009. Sustainable Waterways Within The Context of Navigation and Flood Management. PIANC, 2003. Guidelines for sustainable inland waterways and navigation, Report of working group 6. Sustainable Development of Floodplains, report: http://www.ecrr.org/sdfproject/sdfproject.htm