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Nisqually Delta Sediment Budget & Transport Dynamics
  to Inform Restoration and Climate Change Planning
               Eric Grossman, U.S. Geological Survey




Guy Gelfenbaum,
Andrew Stevens,
Chris Curran,
Steve Rubin,
Mike Hayes



PCMSC, WAWSC      Nisqually Indian Tribe
WERC, WFRC
How do physical processes redistribute sediment and organics
to shape marshes, channels, nearshore/tidal flats?
Tides/Hydrodynamics
Fish, Substrate,
Invertebrates (food-prey)
Elevation, Vegetation,
Water Quality
Conceptual Model and Methods

Methods:
1. GIS-Based “RAP” Model
2. Hydrodynamic Model
                                   lost
3. Field Measurements


                                 Sediment
                                 Delivery
1. “Rapid Assessment Protocol” - Potential Sediment Accretion
       Distribute sediment load scaled by transport connectivity

Data Needs:
1. Sediment load
2. Topography (DEM)
3. Tidal Data             lost


                      Sediment




                20-100K TY                              Czuba et al. 2011
              4.5-23.0K m3/yr                   20-100k TY
                                           USGS, 1974; This study
1. “Rapid Assessment Protocol” - Potential Sediment Accretion
       Distribute sediment load scaled by transport connectivity

Data Needs:
1. Sediment load
2. Topography (DEM)   lost
3. Tidal Data




          11-28%

                                       Grossman and Horne (in prep)



                20-100K TY
              4.5-23.0K m3/yr
1. “Rapid Assessment Protocol” - Potential Sediment Accretion
     Distribute sediment load scaled by transport connectivity



                   lost




        11-28%




              20-100K TY               Grossman and Horne (in prep)
            4.5-23.0K   m3/yr
2. Process-based hydrodynamic & sediment transport model
           Delft3D couples:
              wave - current
               interaction
    FLOW                   WAVES
       2 or
                               Bathymetry
       3D

   TRANSP                BOTTOM

 Sediment transport (van Rijn, 1993)
 Dynamic Morphology
 Wetting drying
 Vegetation – momentum
 (Baptist, 2005; Uittenboogaard, 2003)

                                            ~20-30 m grid resolution in
                                               the restoration area
2. Delft3D hydrodynamic & sediment transport model
                                 Tidal forcing well characterized




                              Tidal inundation reasonably modeled;
                              some channels not resolved properly




Tidal channel currents well
modeled for portions of the
tidal cycle. Roughness
(vegetation) not properly
characterized, yet!
Role of vegetation on
hydrodynamics & sediment
information need
Modeled Connectivity




                 1-Month time period,
                 Avg river discharge:
                       70 m3/s
3. Field Measurements - Methods
                                    Fluvial Inputs
                                    River Discharge, Sediment Load
                                    (2-yrs; 15-min)

                                  Nearshore Hydrodynamics
                                    Tides, Currents, Turbidity
                                    (2-yr, 3-mo; 5-min)
  WL   1             3
                                    Currents, SSC, X-Sections
                                    (Synoptic: tides, Qw)



           WL
                WL


    WL




    WL
3. Field Results: Fluvial inputs, WY2011
3. Field Results: Fluvial inputs, WY2011




      Fines (silts and clays)
      ~48% of total load
3. Field Results: River-Marsh Connectivity



           Marsh Turbidity
   mean                        = 0.19
           River Turbidity


                                 River Turbidity




                              Marsh Turbidity
3. Field Results: Channel Velocities, Discharge
3. Field Results: Channel Discharge
                                      McAllister
                                       -10.1 cms


          Small Net Flow in
        (1.6 cms, <6% river)          Area1
                                       2.1 cms



              2.1 1.1 3.1 2.2
                                      Madrone
       10.1
                                       1.1 cms



                                      Leschi
                                       3.1 cms



                                      Area3
                                       2.2 cms
3. Field Measurements: Nearshore Sediments & Flux

                                     Suspended sediment
                                     tracks ~1:1 with
                                     turbidity
                                     Nearshore turbidity
                                     20-50% of river
3. Field Results: Channel Sediment Flux

   Net Flux into Marshes
        (370 m3/yr)
    Potential Accretion
       ~0.12mm/yr



            2.1 1.1 3.1 2.2
     10.1


            0.12 mm/yr
Vulnerability? Cumulative Impacts? Adaptive Management?




                             44M m3 of sediment since 1945
                                 (14-70x annual load)
Nearshore Response: Extensive channel incision
     Feb 2009                 Aug 2011

                                         25 m

                                              2m




                                         1-2 m of incision
                                         10-40 m widening
                2009                     ~5 km of channels

                                         Sediment
                       2011              redistributed
                                         367,500 m3
Nearshore Response: Sand export
                                  Photo=Jul 2011

                      Mapping
                      Aug 2012




                       50m
Nearshore Response: Sand export
McAllister Creek

Jul 2009                     Jul 2010

                                         Leading edge



                                         Sand bar




                                        incision




                                                        Leading edge
“Functional” Channel Habitat – Salinity Gradients
“Functional” Channel Habitat – Salinity

         high tide

                     2 hrs into ebb
                                       River




                                      Salt Wedge
Climate Change and Sea Level Rise
                                                         Winds/Waves

     Observations
     following maximum
     model prediction




                                     Lower rate due
                                     to wind stress?

      Rate ~3.75 mm/yr (2x the 20th century
                            Will sea level rise
      Marshes and coastal habitats response?
                            accelerate if it
     Brominski et al. 2011  relaxes?




IPCC. 2007; Church and White, 2011
“Green” Infrastructure: Coastal habitats to buffer impacts

                      Example, Stillaguamish Delta


                                      1964	
  Low	
  Marsh	
  
                                     Low	
  Marsh	
  Boundary	
  
                                      Boundary	
  
                                     1964	
  
                                     2004	
  




                                                   2012
                                                   Restoration
GCM-RCM Dynamic Downscaling: Hydrology, Sediment

                              Variable Infiltration Capacity (6km)
ECHAM5* & CCSM3 (A1B, A2)




  WRF

                               DHSVM (100m2)
Projected Climate Impacts to Sediment Delivery
                           Increase and earlier                   Seasonal sediment transport model
                             seasonal runoff




                            4
                                2080s
Sediment Load (MT/month)




                                                                       Curran and Grossman (In Review)
                            3
                                     Increase	
  in	
  flood	
  
                                     and	
  sediment	
  
                            2


                            1
                                              2010
                            0

                           Hamlet and Grossman (in prep)
Adaptive Management
    Opportunity?
Simulated levee breach
Model Results – Mud Deposition
http://coastalresilience.org
Flow to marsh = 3-6% of the river
Suspended sediment concentrations = 20-50% river
Sand exporting from marshes
Potential Accretion Rate:
<2 mm/yr (RAP); <0.3 mm/yr (measurements)
 2010-2011 river flow was low

Adaptive Management:
1-Alder Lake traps >15x equiv. annual sediment load to delta
2-New Distributary?

Climate Change Adaptation and Resilience
1-Changes in Sediment delivery and fate
2-Sea level rise/waves (erosion, channel salinities)
3-Ecosystem functional response?

Information Needs
1-Interaction of vegetation-hydrodynamics-geomorphology
2-Test fish use of “functional” channels (salinity gradients)
egrossman@usgs.gov
          Western Washington University




Any interested students please contact Eric

Coastalresilience.org

Salishsearestoration.org
Simulated	
  Flood	
  Event	
  
    Modeling
 Approach – Fine
   Sediment
    Dispersal
Investigate three scenarios
   1.  Flow Only (tides and
       river flood)
   2.  Flow and Waves
       (tides, river flood,
       and waves)
   3.  Flow + River Breach
       (tides, river flood,
       and river breach)

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Nisqually Delta Sediment Budget & Transport Dynamics

  • 1. Nisqually Delta Sediment Budget & Transport Dynamics to Inform Restoration and Climate Change Planning Eric Grossman, U.S. Geological Survey Guy Gelfenbaum, Andrew Stevens, Chris Curran, Steve Rubin, Mike Hayes PCMSC, WAWSC Nisqually Indian Tribe WERC, WFRC
  • 2. How do physical processes redistribute sediment and organics to shape marshes, channels, nearshore/tidal flats?
  • 4. Conceptual Model and Methods Methods: 1. GIS-Based “RAP” Model 2. Hydrodynamic Model lost 3. Field Measurements Sediment Delivery
  • 5. 1. “Rapid Assessment Protocol” - Potential Sediment Accretion Distribute sediment load scaled by transport connectivity Data Needs: 1. Sediment load 2. Topography (DEM) 3. Tidal Data lost Sediment 20-100K TY Czuba et al. 2011 4.5-23.0K m3/yr 20-100k TY USGS, 1974; This study
  • 6. 1. “Rapid Assessment Protocol” - Potential Sediment Accretion Distribute sediment load scaled by transport connectivity Data Needs: 1. Sediment load 2. Topography (DEM) lost 3. Tidal Data 11-28% Grossman and Horne (in prep) 20-100K TY 4.5-23.0K m3/yr
  • 7. 1. “Rapid Assessment Protocol” - Potential Sediment Accretion Distribute sediment load scaled by transport connectivity lost 11-28% 20-100K TY Grossman and Horne (in prep) 4.5-23.0K m3/yr
  • 8. 2. Process-based hydrodynamic & sediment transport model Delft3D couples: wave - current interaction FLOW WAVES 2 or Bathymetry 3D TRANSP BOTTOM Sediment transport (van Rijn, 1993) Dynamic Morphology Wetting drying Vegetation – momentum (Baptist, 2005; Uittenboogaard, 2003) ~20-30 m grid resolution in the restoration area
  • 9. 2. Delft3D hydrodynamic & sediment transport model Tidal forcing well characterized Tidal inundation reasonably modeled; some channels not resolved properly Tidal channel currents well modeled for portions of the tidal cycle. Roughness (vegetation) not properly characterized, yet!
  • 10. Role of vegetation on hydrodynamics & sediment information need
  • 11. Modeled Connectivity 1-Month time period, Avg river discharge: 70 m3/s
  • 12. 3. Field Measurements - Methods Fluvial Inputs River Discharge, Sediment Load (2-yrs; 15-min) Nearshore Hydrodynamics Tides, Currents, Turbidity (2-yr, 3-mo; 5-min) WL 1 3 Currents, SSC, X-Sections (Synoptic: tides, Qw) WL WL WL WL
  • 13. 3. Field Results: Fluvial inputs, WY2011
  • 14. 3. Field Results: Fluvial inputs, WY2011 Fines (silts and clays) ~48% of total load
  • 15. 3. Field Results: River-Marsh Connectivity Marsh Turbidity mean = 0.19 River Turbidity River Turbidity Marsh Turbidity
  • 16. 3. Field Results: Channel Velocities, Discharge
  • 17. 3. Field Results: Channel Discharge McAllister -10.1 cms Small Net Flow in (1.6 cms, <6% river) Area1 2.1 cms 2.1 1.1 3.1 2.2 Madrone 10.1 1.1 cms Leschi 3.1 cms Area3 2.2 cms
  • 18. 3. Field Measurements: Nearshore Sediments & Flux Suspended sediment tracks ~1:1 with turbidity Nearshore turbidity 20-50% of river
  • 19. 3. Field Results: Channel Sediment Flux Net Flux into Marshes (370 m3/yr) Potential Accretion ~0.12mm/yr 2.1 1.1 3.1 2.2 10.1 0.12 mm/yr
  • 20. Vulnerability? Cumulative Impacts? Adaptive Management? 44M m3 of sediment since 1945 (14-70x annual load)
  • 21. Nearshore Response: Extensive channel incision Feb 2009 Aug 2011 25 m 2m 1-2 m of incision 10-40 m widening 2009 ~5 km of channels Sediment 2011 redistributed 367,500 m3
  • 22. Nearshore Response: Sand export Photo=Jul 2011 Mapping Aug 2012 50m
  • 23. Nearshore Response: Sand export McAllister Creek Jul 2009 Jul 2010 Leading edge Sand bar incision Leading edge
  • 24.
  • 25.
  • 26. “Functional” Channel Habitat – Salinity Gradients
  • 27. “Functional” Channel Habitat – Salinity high tide 2 hrs into ebb River Salt Wedge
  • 28. Climate Change and Sea Level Rise Winds/Waves Observations following maximum model prediction Lower rate due to wind stress? Rate ~3.75 mm/yr (2x the 20th century Will sea level rise Marshes and coastal habitats response? accelerate if it Brominski et al. 2011 relaxes? IPCC. 2007; Church and White, 2011
  • 29. “Green” Infrastructure: Coastal habitats to buffer impacts Example, Stillaguamish Delta 1964  Low  Marsh   Low  Marsh  Boundary   Boundary   1964   2004   2012 Restoration
  • 30. GCM-RCM Dynamic Downscaling: Hydrology, Sediment Variable Infiltration Capacity (6km) ECHAM5* & CCSM3 (A1B, A2) WRF DHSVM (100m2)
  • 31. Projected Climate Impacts to Sediment Delivery Increase and earlier Seasonal sediment transport model seasonal runoff 4 2080s Sediment Load (MT/month) Curran and Grossman (In Review) 3 Increase  in  flood   and  sediment   2 1 2010 0 Hamlet and Grossman (in prep)
  • 32. Adaptive Management Opportunity? Simulated levee breach
  • 33. Model Results – Mud Deposition
  • 35.
  • 36. Flow to marsh = 3-6% of the river Suspended sediment concentrations = 20-50% river Sand exporting from marshes Potential Accretion Rate: <2 mm/yr (RAP); <0.3 mm/yr (measurements) 2010-2011 river flow was low Adaptive Management: 1-Alder Lake traps >15x equiv. annual sediment load to delta 2-New Distributary? Climate Change Adaptation and Resilience 1-Changes in Sediment delivery and fate 2-Sea level rise/waves (erosion, channel salinities) 3-Ecosystem functional response? Information Needs 1-Interaction of vegetation-hydrodynamics-geomorphology 2-Test fish use of “functional” channels (salinity gradients)
  • 37. egrossman@usgs.gov Western Washington University Any interested students please contact Eric Coastalresilience.org Salishsearestoration.org
  • 38.
  • 39. Simulated  Flood  Event   Modeling Approach – Fine Sediment Dispersal Investigate three scenarios 1.  Flow Only (tides and river flood) 2.  Flow and Waves (tides, river flood, and waves) 3.  Flow + River Breach (tides, river flood, and river breach)