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www.azti.es 7/7/2015 1
Sea Level Rise: evidences,
scenarios and local
consequences
Marine Research Division
AZTI-Tecnalia
Sukarrieta (Spain)
Guillem Chust
13th- 15th of July (2015) Palacio Miramar - San Sebastián
www.azti.es 7/7/2015
Index
Sea Level Rise
• Measurements and projections for the Bay of Biscay
• Impacts in the Basque coast (urban, beaches, habitats, species)
• Species distribution shifts
• Sea level variability (storm surges)
• Interaction with extreme waves
2
www.azti.es 7/7/2015 3
Sea Level Rise
4
• Global mean sea-level rate: 1.8 ± 0.3 mm/yr between 1950 and 2000 (Church et al.,
2004), with large spatial variability at regional scales
Linear trends in mean sea level (mm yr–1) for 1955 to
2003 based on the past sea level reconstruction with
tide gauges and altimetry data (IPCC 4AR, 2007)
Global sea level trends
SLR = Thermal expansion + ice melting
5
Location Method Time
period
Rate and error
(mm yr-1
)
Reference
Vigo Tide gauge 1943 - 2001 2.910.09 Marcos et al. (2005)
La Coruña Tide gauge 1943 - 2001 2.510.09 Marcos et al. (2005)
Santander Tide gauge 1943 - 2001 2.1 Marcos et al. (2005)
Brest Tide gauge 1890 - 1980 1.30.5 Wöppelmann et al.
(2006)
Brest Tide gauge 1980 - 2004 3.00.5 Wöppelmann et al.
(2006)
Newlyn Tide gauge 1915 - 2005 1.770.12 Araújo and Pugh
(2008)
St. Mary’s Tide gauge 1968 - 2006 1.730.52 Haigh (2009)
Open water of
Bay of Biscay
Satellite altimeters
and Tide gauge
1993 - 2002 3.090.21 Marcos et al. (2007)
Open water of
Bay of Biscay
Satellite altimeters 1993 - 2005 2.7 Caballero et al. (2008)
Basque coast Foraminifera-
based transfer
functions
20th
century 2.0 Leorri et al. (2008)
Basque coast Foraminifera-
based transfer
functions
20th
century 1.9 Leorri and Cearreta
(2009)
Sea level rise within the Bay of Biscay
6
Year
1940 1960 1980 2000
Meansealevel(mm)
6800
6850
6900
6950
7000
7050
7100
St. Jean de Luz
Bilbao
Meansealevel(mm)
6800
6850
6900
6950
7000
7050
7100
7150
Santander
Sea-level measurements (tide gauge) along the Basque coast and nearby records
Santander
St Jean Luz
Bilbao
2.08 ± 0.33 mm yr-1
2.09 ± 0.42 mm yr-1
2.99 ± 1.08 mm yr-1
Chust et al. 2009. Estuarine, Coastal and Shelf Science 84:453-462
Regional sea level measurements
© AZTI-Tecnalia
7
San Sebastián
 Mean Sea Level Rise (thermal expansion + ice melting)
 Storm surges (meteorological tides)
 Wave extreme events (tides + run-up)
Deusto, 10 September 2010
Sea level
variability
Regional climate scenarios for the 21st century
© AZTI-Tecnalia 8
1. Column water
integration
2. Model selection
SRES A1B
WCRP
Tª ocean
Salinity
Sea level
Chust et al. 2010. Estuarine, Coastal and Shelf Science 87:113-124


01
H
dp
g
TSL 
Projections for the thermosteric sea level rise
9
Year
1940 1960 1980 2000 2020 2040 2060 2080 2100
Sealevelrise(cm)
-20
0
20
40
60
St. Jean de Luz
Santander
Bilbao
SRES A2 + MinMelt
SRES A1B + MaxMelt
Thermal expansion + ice melting (4 to 20 cm) => 29 to 49 cm
Mean Sea Level Rise for the bay of Biscay
Observations
Projections Ice melting
uncertainty
Chust, G., Borja, Á., Caballero, A., Irigoien, X., Sáenz, J., Moncho, R., Marcos, M., Liria, P., Hidalgo, J., Valle, M. & Valencia, V. (2011)
Climate change impacts on coastal and pelagic environments in the southeastern Bay of Biscay. Climate Research, 48, 307–332.
IPCC 5AR (Sep. 2013)
SLR: between 26 and 82 cm
IPCC 4AR (2007)
SLR: 18 and 59 cm
Special Report on Emissions Scenarios
(SRES)
• A1
• A2
• B1
• B2
Representative Concentration Pathway (RCP) scenarios
• RCP2.6
• RCP4.5
• RCP6.0
• RCP8.5
 Global: 1 m
(Rahmstorf et al., 2007. Science 316: 709)
© AZTI-Tecnalia 11
Expected impacts from sea level rise
using high-resolution cartographic data
12
• LIDAR-based Digital Terrain Model
(DTM)
– Spatial resolution: 1 x 1 m
– Vertical accuracy: 15 cm
• Habitat maps from ortophotography:
– Spatial res.: 25 x 25 cm
High-resolution airborne data
(M.A. Ortiz)
LIDAR: laser altimeter
© AZTI-Tecnalia 13
Bilbao I
PMA
NMMB
NMMA
BMA Cero Puerto
0,337 m (REDNAP2008)
2,063 m (REDNAP2008)
4,94
0,11
Alicante
Bilbao
LiDAR validation with GPS and MSL references
14
Tide
range:
4.94 m
SLR: +0.49 m
Tides in Bilbao I
KOSTASystem
Mean Sea Level
Maximum Astronomic High Tide
© AZTI-Tecnalia 15
Gipuzkoa
Area affected:
• 110 hectares
• 50% in estuaries
Flood risk map: Sea level rise of 49 cm
16
Flood risk map for urban areas
© AZTI-Tecnalia 17
Bruun rule
ActualFuturo
Retreat in beach width
25%
40%
Flood risk map for sandy beaches
18
Topographic LiDAR
(NIR: 1064 nm)
Bathymetric LiDAR
(Green: 532 nm)
Bathymetric LiDAR (Hawk Eye MK II)
© AZTI-Tecnalia 19
Digital Elevation Model of the Oka estuary
© AZTI-Tecnalia 20
Intertidal area
Subtidal area
21
Profile (m)
0 200 400 600 800 1000 1200
Height(m)
-4
-2
0
2
4
6
Neap Tide
High Tide
+ Sea level rise
+ Sea level rise
Phragmites
Juncus
Marshes
Spartina
Gracilaria
Zostera
Mudflats
Marshes
Main channel
Fixed
boundary
(A) (B)
Zostera noltii
Estuaries in a Changing Climate
5-8 Pril 2011, Porto, Portugal
Tide zonation of intertidal species communities
Chust et al. 2010 Estuarine, Coastal
and Shelf Science 89: 200-213
www.azti.es 7/7/2015
Hydromorphologic model
Simulations under 2 scenarios:
 S1: Scenario with an average SLR of 0.49 m
 S2: Scenario with an average SLR of 1 m
Coupling hydromorphologic and species distribution models
1. Maximum Entropy model (MaxEnt)
(Phillips et al. 2006)
2. Generalized Additive model (GAM)
(Hastie & Tibshirani, 1990)
3. Ecological Niche Factor Analysis (ENFA)
(Hirzel et al. 2002)
Species Distribution Models
Projection of the SDM to the future scenarios
Evaluation Best model selection
Coupling
Habitat suitability changes’ assessment comparing the current availability with that from the future
Threshold
www.azti.es 7/7/2015
MOHID Water
Tide and River
discharges
MOHID
Sand
Sediment
characteristics
Shear Stresses
New bathymetry
MOHID modelling system:
• Fully non-linear, 3D baroclinic water model
• Integrates hydrodynamic (Neves et al., 2000; Martins et al. 2011)
and sand transport (Silva et al. 2004) modules
• Able to simulate non-cohesive sediment dynamics in
estuaries driven by tide and river flows
Hydromorphologic modelling
Open source software:
www.mohid.com
Outputs: - Changes in maximum current velocities
- Changes in the estuary’s morphology
www.azti.es 7/7/2015
MOHID modelling system
Hydromorphologic modeling system (MOHID)Future hidrodynamic
SLR: 0.49 m SLR: 1 m
www.azti.es 7/7/2015
Changes in maximum current velocity (m·s -1)
Hydromorphologic modelling
S1: SLR 0.49 m S2: SLR 1 m
 Significant changes under both scenarios,
from 10 cm·s -1 up to 40 cm·s -1 :
 Mainly along the channel in S1
 Through the entire estuary in S2
www.azti.es 7/7/2015 26
Changes in morphology (m)
Hydromorphologic modelling
S1: SLR 0.49 m S2: SLR 1 m
 Morphologic changes not very significant:
 Accretion <10 cm in the entire estuary
 Erosion in the borders of the main
channel and accretion in the centre
© AZTI-Tecnalia 27
Field work: Zostera noltii distribution
Habitat
Suitability
Map
Habitat models:
• GAM
• MaxEnt
• ENFA
Presence data
Ecogeographical variables
Sediment characteristics
LiDAR derived topographic height
Ocean currents
Species ecological
niche
Environment
Species Distribution Modelling
www.azti.es 7/7/2015
Shift of the seagrass habitat to the inner estuary
Zostera noltii
Saltamarshes
Wall-enclosed areas
+ 14%
- 22%
+ 18%
- 63%
 SLR and derived changes in current velocities are expected to induce the landward
migration of the species, increasing the available suitable intertidal areas (14–18%) to
limits imposed by anthropogenic barriers.
30
Saltmarsh accretion
FitzGerald, 2008
Within the Basque estuaries, an
accretion rate of 3.7 mm yr−1 during
the 20th c. (Leorri et al., 2008)
suggests that marshes are
potentially able to adjust to the
projected SLR rates …
www.azti.es 7/7/2015
81.5%
18.5%
Colonisable 24.3%
Seagrass (Zostera noltii) habitat poleward shift under sea warming
Unsuitable -18.5% Stable 81.5%
888 km
24.3%
Valle et al. 2014 Biological Conservation
STRUCTURE analysis:
Z. noltei
Population genetic analysis
C. edule


Genetically
undifferentiated,
indicating they own to a
unique panmictic
population
- 3 clusters; 4 estuaries
- Populations genetically
fragmented
Chust, G., et al. (2013) Connectivity, neutral theories and the assessment of species vulnerability to global change in
temperate estuaries. Estuarine, Coastal and Shelf Science, 131, 52-63.
Seagrass populations are genetically fragmented  Dispersal limited  Limited Capacity for
recolonizing new estuaries and ecological adaptation to new conditions  Vulnerable to CC
Seagrass restoration experiments
Garmendia et al., 2012
© AZTI-Tecnalia 34
Sea level = Astronomic Tide + Meteorological Tide
Meteorological Tide depends on wind and pressure
Sea level expected by 2050-2100 as a consequence of 50-yr return level
Sea level rise + Storm surge (marejada ciclónica)  62 cm above Maximum Astron. High tide
(at present is at 22 cm above MAHT)
Flood risk from storm surges
Deusto, 10 September 2010
Sea level ~ Maximum Astronomic high tide
Marcos et al. (2012) Clim Res
35
Flood risk map expected by 2050-2100 as a consequence of 50-yr return level
Sea level rise + Storm surge  85 cm above Maximum Astron. tide
Marcos, M., Chust, G., Jordà, G., Caballero, A., 2012. Effect of sea level extremes on the western Basque coast during the
21st century. Climate Research, 51, 237-248
Flood risk from storm surges
Barakaldo
Erandio
© AZTI-Tecnalia 36
Flood risk from wave extreme events
© AZTI-Tecnalia 37
Flood risk from wave extreme events
38
Extreme wave (wave height)
flood level expected for a 50-yr
return period
FL: Flood level
TL: Tide level
RU: wave run-up (sum of the wave
set-up and the wave swash)
AT: Astronomic tide
MT: meteorological tide
RU0: theoretical run-up
Liria et al. 2011 Journal of Coastal Research
RUMTATRUTLFL 
Extreme wave events: methodology
39
Extreme wave events Sea-level rise
Liria et al. 2011 Journal of Coastal Research
Flood risk areas
40
Floods and impacts due to:
• Sea level rise (29-49 cm)
• Storm surges (+62 cm)
• Extreme wave events
 250 ha of the Basque coast is
at risk of flood, concentrated
within the estuaries (~50%)
 Retreat of beaches on 25-40%
of width
 The habitat of intertidal
species and salt-marshes can be
reduced
Scenarios Impacts Adaptations
• Maintenance and rebuilding
of coastal infrastructures
• Revision of drainage systems
• To promote coastal
resilience such as protection,
regeneration of dune plants
and intertidal species and
wetlands, sand stabilization,
establish buffer zones
Conclusions and Adaptation strategies
41
Climate Change Documentary:
www.vimeo.com/13292409
42
References
• Chust et al. (2009). Human impacts overwhelm the effects of sea-level rise on Basque coastal habitats (N Spain) between
1954 and 2004. Estuarine, Coastal and Shelf Science 84:453-462.
• Chust et al. . 2010. Regional scenarios of sea level rise and impacts on Basque (Bay of Biscay) coastal habitats, throughout the
21st century. Estuarine, Coastal and Shelf Science 87:113-124.
• Chust et al. 2010. Capabilities of the bathymetric Hawk Eye LiDAR for coastal habitat mapping: a case study within a Basque
estuary. Estuarine, Coastal and Shelf Science 89: 200-213.
• Chust et al. (2011) Climate Change impacts on the coastal and pelagic environments in the southeastern Bay of Biscay.
Climate Research 48:307–332.
• Liria et al. 2011. Extreme Wave Flood-Risk Mapping Within the Basque Coast. Journal of Coastal Research, SI 64.
• Valle et al., 2014. Projecting future distribution of the seagrass Zostera noltii under global warming and sea level rise.
Biological Conservation 170.
Acknowledgements
• Gobierno Vasco (ETORTEK, proyecto K-Egokitzen I & II)
• Ministerio de Medio Ambiente y Medio Rural y Marino, Gobierno de España (Proyecto Ref.: 0.39/SGTB/2007/4.1)
• Agencia vasca del Agua (URA), Gobierno Vasco, proyecto « Inundabilidad de los estuarios vascos »
• Ministerio de Ciencia y Tecnología: ZOSTERMODEL
Thank you for your attention!

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Sea Level Rise: evidence and scenarios (BC3 Summer School _July 2015)

  • 1. www.azti.es 7/7/2015 1 Sea Level Rise: evidences, scenarios and local consequences Marine Research Division AZTI-Tecnalia Sukarrieta (Spain) Guillem Chust 13th- 15th of July (2015) Palacio Miramar - San Sebastián
  • 2. www.azti.es 7/7/2015 Index Sea Level Rise • Measurements and projections for the Bay of Biscay • Impacts in the Basque coast (urban, beaches, habitats, species) • Species distribution shifts • Sea level variability (storm surges) • Interaction with extreme waves 2
  • 4. 4 • Global mean sea-level rate: 1.8 ± 0.3 mm/yr between 1950 and 2000 (Church et al., 2004), with large spatial variability at regional scales Linear trends in mean sea level (mm yr–1) for 1955 to 2003 based on the past sea level reconstruction with tide gauges and altimetry data (IPCC 4AR, 2007) Global sea level trends SLR = Thermal expansion + ice melting
  • 5. 5 Location Method Time period Rate and error (mm yr-1 ) Reference Vigo Tide gauge 1943 - 2001 2.910.09 Marcos et al. (2005) La Coruña Tide gauge 1943 - 2001 2.510.09 Marcos et al. (2005) Santander Tide gauge 1943 - 2001 2.1 Marcos et al. (2005) Brest Tide gauge 1890 - 1980 1.30.5 Wöppelmann et al. (2006) Brest Tide gauge 1980 - 2004 3.00.5 Wöppelmann et al. (2006) Newlyn Tide gauge 1915 - 2005 1.770.12 Araújo and Pugh (2008) St. Mary’s Tide gauge 1968 - 2006 1.730.52 Haigh (2009) Open water of Bay of Biscay Satellite altimeters and Tide gauge 1993 - 2002 3.090.21 Marcos et al. (2007) Open water of Bay of Biscay Satellite altimeters 1993 - 2005 2.7 Caballero et al. (2008) Basque coast Foraminifera- based transfer functions 20th century 2.0 Leorri et al. (2008) Basque coast Foraminifera- based transfer functions 20th century 1.9 Leorri and Cearreta (2009) Sea level rise within the Bay of Biscay
  • 6. 6 Year 1940 1960 1980 2000 Meansealevel(mm) 6800 6850 6900 6950 7000 7050 7100 St. Jean de Luz Bilbao Meansealevel(mm) 6800 6850 6900 6950 7000 7050 7100 7150 Santander Sea-level measurements (tide gauge) along the Basque coast and nearby records Santander St Jean Luz Bilbao 2.08 ± 0.33 mm yr-1 2.09 ± 0.42 mm yr-1 2.99 ± 1.08 mm yr-1 Chust et al. 2009. Estuarine, Coastal and Shelf Science 84:453-462 Regional sea level measurements
  • 7. © AZTI-Tecnalia 7 San Sebastián  Mean Sea Level Rise (thermal expansion + ice melting)  Storm surges (meteorological tides)  Wave extreme events (tides + run-up) Deusto, 10 September 2010 Sea level variability Regional climate scenarios for the 21st century
  • 8. © AZTI-Tecnalia 8 1. Column water integration 2. Model selection SRES A1B WCRP Tª ocean Salinity Sea level Chust et al. 2010. Estuarine, Coastal and Shelf Science 87:113-124   01 H dp g TSL  Projections for the thermosteric sea level rise
  • 9. 9 Year 1940 1960 1980 2000 2020 2040 2060 2080 2100 Sealevelrise(cm) -20 0 20 40 60 St. Jean de Luz Santander Bilbao SRES A2 + MinMelt SRES A1B + MaxMelt Thermal expansion + ice melting (4 to 20 cm) => 29 to 49 cm Mean Sea Level Rise for the bay of Biscay Observations Projections Ice melting uncertainty Chust, G., Borja, Á., Caballero, A., Irigoien, X., Sáenz, J., Moncho, R., Marcos, M., Liria, P., Hidalgo, J., Valle, M. & Valencia, V. (2011) Climate change impacts on coastal and pelagic environments in the southeastern Bay of Biscay. Climate Research, 48, 307–332.
  • 10. IPCC 5AR (Sep. 2013) SLR: between 26 and 82 cm IPCC 4AR (2007) SLR: 18 and 59 cm Special Report on Emissions Scenarios (SRES) • A1 • A2 • B1 • B2 Representative Concentration Pathway (RCP) scenarios • RCP2.6 • RCP4.5 • RCP6.0 • RCP8.5  Global: 1 m (Rahmstorf et al., 2007. Science 316: 709)
  • 11. © AZTI-Tecnalia 11 Expected impacts from sea level rise using high-resolution cartographic data
  • 12. 12 • LIDAR-based Digital Terrain Model (DTM) – Spatial resolution: 1 x 1 m – Vertical accuracy: 15 cm • Habitat maps from ortophotography: – Spatial res.: 25 x 25 cm High-resolution airborne data (M.A. Ortiz) LIDAR: laser altimeter
  • 13. © AZTI-Tecnalia 13 Bilbao I PMA NMMB NMMA BMA Cero Puerto 0,337 m (REDNAP2008) 2,063 m (REDNAP2008) 4,94 0,11 Alicante Bilbao LiDAR validation with GPS and MSL references
  • 14. 14 Tide range: 4.94 m SLR: +0.49 m Tides in Bilbao I KOSTASystem Mean Sea Level Maximum Astronomic High Tide
  • 15. © AZTI-Tecnalia 15 Gipuzkoa Area affected: • 110 hectares • 50% in estuaries Flood risk map: Sea level rise of 49 cm
  • 16. 16 Flood risk map for urban areas
  • 17. © AZTI-Tecnalia 17 Bruun rule ActualFuturo Retreat in beach width 25% 40% Flood risk map for sandy beaches
  • 18. 18 Topographic LiDAR (NIR: 1064 nm) Bathymetric LiDAR (Green: 532 nm) Bathymetric LiDAR (Hawk Eye MK II)
  • 19. © AZTI-Tecnalia 19 Digital Elevation Model of the Oka estuary
  • 20. © AZTI-Tecnalia 20 Intertidal area Subtidal area
  • 21. 21 Profile (m) 0 200 400 600 800 1000 1200 Height(m) -4 -2 0 2 4 6 Neap Tide High Tide + Sea level rise + Sea level rise Phragmites Juncus Marshes Spartina Gracilaria Zostera Mudflats Marshes Main channel Fixed boundary (A) (B) Zostera noltii Estuaries in a Changing Climate 5-8 Pril 2011, Porto, Portugal Tide zonation of intertidal species communities Chust et al. 2010 Estuarine, Coastal and Shelf Science 89: 200-213
  • 22. www.azti.es 7/7/2015 Hydromorphologic model Simulations under 2 scenarios:  S1: Scenario with an average SLR of 0.49 m  S2: Scenario with an average SLR of 1 m Coupling hydromorphologic and species distribution models 1. Maximum Entropy model (MaxEnt) (Phillips et al. 2006) 2. Generalized Additive model (GAM) (Hastie & Tibshirani, 1990) 3. Ecological Niche Factor Analysis (ENFA) (Hirzel et al. 2002) Species Distribution Models Projection of the SDM to the future scenarios Evaluation Best model selection Coupling Habitat suitability changes’ assessment comparing the current availability with that from the future Threshold
  • 23. www.azti.es 7/7/2015 MOHID Water Tide and River discharges MOHID Sand Sediment characteristics Shear Stresses New bathymetry MOHID modelling system: • Fully non-linear, 3D baroclinic water model • Integrates hydrodynamic (Neves et al., 2000; Martins et al. 2011) and sand transport (Silva et al. 2004) modules • Able to simulate non-cohesive sediment dynamics in estuaries driven by tide and river flows Hydromorphologic modelling Open source software: www.mohid.com Outputs: - Changes in maximum current velocities - Changes in the estuary’s morphology
  • 24. www.azti.es 7/7/2015 MOHID modelling system Hydromorphologic modeling system (MOHID)Future hidrodynamic SLR: 0.49 m SLR: 1 m
  • 25. www.azti.es 7/7/2015 Changes in maximum current velocity (m·s -1) Hydromorphologic modelling S1: SLR 0.49 m S2: SLR 1 m  Significant changes under both scenarios, from 10 cm·s -1 up to 40 cm·s -1 :  Mainly along the channel in S1  Through the entire estuary in S2
  • 26. www.azti.es 7/7/2015 26 Changes in morphology (m) Hydromorphologic modelling S1: SLR 0.49 m S2: SLR 1 m  Morphologic changes not very significant:  Accretion <10 cm in the entire estuary  Erosion in the borders of the main channel and accretion in the centre
  • 27. © AZTI-Tecnalia 27 Field work: Zostera noltii distribution
  • 28. Habitat Suitability Map Habitat models: • GAM • MaxEnt • ENFA Presence data Ecogeographical variables Sediment characteristics LiDAR derived topographic height Ocean currents Species ecological niche Environment Species Distribution Modelling
  • 29. www.azti.es 7/7/2015 Shift of the seagrass habitat to the inner estuary Zostera noltii Saltamarshes Wall-enclosed areas + 14% - 22% + 18% - 63%  SLR and derived changes in current velocities are expected to induce the landward migration of the species, increasing the available suitable intertidal areas (14–18%) to limits imposed by anthropogenic barriers.
  • 30. 30 Saltmarsh accretion FitzGerald, 2008 Within the Basque estuaries, an accretion rate of 3.7 mm yr−1 during the 20th c. (Leorri et al., 2008) suggests that marshes are potentially able to adjust to the projected SLR rates …
  • 31. www.azti.es 7/7/2015 81.5% 18.5% Colonisable 24.3% Seagrass (Zostera noltii) habitat poleward shift under sea warming Unsuitable -18.5% Stable 81.5% 888 km 24.3% Valle et al. 2014 Biological Conservation
  • 32. STRUCTURE analysis: Z. noltei Population genetic analysis C. edule   Genetically undifferentiated, indicating they own to a unique panmictic population - 3 clusters; 4 estuaries - Populations genetically fragmented Chust, G., et al. (2013) Connectivity, neutral theories and the assessment of species vulnerability to global change in temperate estuaries. Estuarine, Coastal and Shelf Science, 131, 52-63. Seagrass populations are genetically fragmented  Dispersal limited  Limited Capacity for recolonizing new estuaries and ecological adaptation to new conditions  Vulnerable to CC
  • 34. © AZTI-Tecnalia 34 Sea level = Astronomic Tide + Meteorological Tide Meteorological Tide depends on wind and pressure Sea level expected by 2050-2100 as a consequence of 50-yr return level Sea level rise + Storm surge (marejada ciclónica)  62 cm above Maximum Astron. High tide (at present is at 22 cm above MAHT) Flood risk from storm surges Deusto, 10 September 2010 Sea level ~ Maximum Astronomic high tide Marcos et al. (2012) Clim Res
  • 35. 35 Flood risk map expected by 2050-2100 as a consequence of 50-yr return level Sea level rise + Storm surge  85 cm above Maximum Astron. tide Marcos, M., Chust, G., Jordà, G., Caballero, A., 2012. Effect of sea level extremes on the western Basque coast during the 21st century. Climate Research, 51, 237-248 Flood risk from storm surges Barakaldo Erandio
  • 36. © AZTI-Tecnalia 36 Flood risk from wave extreme events
  • 37. © AZTI-Tecnalia 37 Flood risk from wave extreme events
  • 38. 38 Extreme wave (wave height) flood level expected for a 50-yr return period FL: Flood level TL: Tide level RU: wave run-up (sum of the wave set-up and the wave swash) AT: Astronomic tide MT: meteorological tide RU0: theoretical run-up Liria et al. 2011 Journal of Coastal Research RUMTATRUTLFL  Extreme wave events: methodology
  • 39. 39 Extreme wave events Sea-level rise Liria et al. 2011 Journal of Coastal Research Flood risk areas
  • 40. 40 Floods and impacts due to: • Sea level rise (29-49 cm) • Storm surges (+62 cm) • Extreme wave events  250 ha of the Basque coast is at risk of flood, concentrated within the estuaries (~50%)  Retreat of beaches on 25-40% of width  The habitat of intertidal species and salt-marshes can be reduced Scenarios Impacts Adaptations • Maintenance and rebuilding of coastal infrastructures • Revision of drainage systems • To promote coastal resilience such as protection, regeneration of dune plants and intertidal species and wetlands, sand stabilization, establish buffer zones Conclusions and Adaptation strategies
  • 42. 42 References • Chust et al. (2009). Human impacts overwhelm the effects of sea-level rise on Basque coastal habitats (N Spain) between 1954 and 2004. Estuarine, Coastal and Shelf Science 84:453-462. • Chust et al. . 2010. Regional scenarios of sea level rise and impacts on Basque (Bay of Biscay) coastal habitats, throughout the 21st century. Estuarine, Coastal and Shelf Science 87:113-124. • Chust et al. 2010. Capabilities of the bathymetric Hawk Eye LiDAR for coastal habitat mapping: a case study within a Basque estuary. Estuarine, Coastal and Shelf Science 89: 200-213. • Chust et al. (2011) Climate Change impacts on the coastal and pelagic environments in the southeastern Bay of Biscay. Climate Research 48:307–332. • Liria et al. 2011. Extreme Wave Flood-Risk Mapping Within the Basque Coast. Journal of Coastal Research, SI 64. • Valle et al., 2014. Projecting future distribution of the seagrass Zostera noltii under global warming and sea level rise. Biological Conservation 170. Acknowledgements • Gobierno Vasco (ETORTEK, proyecto K-Egokitzen I & II) • Ministerio de Medio Ambiente y Medio Rural y Marino, Gobierno de España (Proyecto Ref.: 0.39/SGTB/2007/4.1) • Agencia vasca del Agua (URA), Gobierno Vasco, proyecto « Inundabilidad de los estuarios vascos » • Ministerio de Ciencia y Tecnología: ZOSTERMODEL Thank you for your attention!