ApplicaonoftheOceanColourmethodsin … · 2021. 2. 25. · stations of the REPHY network ....
Transcript of ApplicaonoftheOceanColourmethodsin … · 2021. 2. 25. · stations of the REPHY network ....
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Applica'on of the Ocean Colour methods in coastal seas: Experience at Ifremer Brest
Francis Gohin
Laboratoire d’Ecologie Pélagique
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Complex but monitored waters
The coastal waters are opBcally complex but … there are more sampled than the open sea Example of a SeaWiFS/MERIS composition on a Karenia mikimotoi bloom in July 2003
Note about the Karenia event in 2010, MarCoast report http://archimer.ifremer.fr/doc/00178/28883/27369.pdf
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Procedures at Ifremer
The method for esBmaBng Chlorophyll-‐a is derived of OC4: Results iden+cal to OC4 for the Open Ocean, Lower for high reflectance in the
green R550 (related to Suspended Par+culate MaAers) and low reflectance R412 (related to overes+ma+on of the atmospheric content or yellow substances)
The error in remote-‐sensing is of two orders: Bias (overes+ma+on of Chl-‐a by OC4 in case of high R550 due to non-‐algal SPM) and noise (variability of the atmospheric correc+on, algal popula+on, yellow substances, ….)
Methods shared with PML/UK and ACRI-ST within the Ocean Colour TAC of Copernicus
http://www.ocean-sci.net/7/705/2011/os-7-705-2011.pdf
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Addressing the bias in Chl-‐a l
Boulogne
Highest levels observed at Cabourg
Ouest-Loscollo (Vilaine)
Lower levels at Bastia
Percentile 90 of Chl-a at the stations of the REPHY network
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Comparison to fluorescence
• A n
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Different validation procedures : here a Generalized Linear Model is applied to the in situ (blue) and satellite data (green) independently at Boulogne Station 2 and Boulogne Station 3 (offshore)
Chl-a Boulogne transect 2003-2014
Point 2 (coastal)
Point 3 (offshore)
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Merging The method iniBally applied to SeaWiFS and extended to MODIS, MERIS, VIIRS making
easier the merging by kriging example 2011/04/2 MERIS MODIS Merged Chl-a
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Annual cycle of the chlorophyll concentration (from SeaWiFS/MODIS/MERIS 1998-2008)
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Non-‐algal SPM
For forcing light in the coastal biogeochemical models it has been necessary to provide
non-‐algal SPM from OC data This is obtained from inversion of a semi-analytical model of the reflectance in the green (low turbidity) and the red (moderate to high turbidity) Gohin, F., Loyer, S., Lunven, M., Labry, C., Froidefond, J. M., Delmas, D., Huret, M.,
and Herbland, A.: Satellite-derived parameters for biological modelling in coastal waters: Illustration over the eastern continental shelf of the bay of biscay, Remote
Sensing of Environment, 95, 29-46, 10.1016/j.rse.2004.11.007, 2005.
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SPM validaBon SPM at the Liverpool Mooring (SmartBuoy)
SPM in g/m3 2003-2010
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SPM & Turbidity Validation from matchups at the
Liverpool mooring
Satellite SPM is better related to in-situ Turbidity than to in-situ SPM
Turbidity is an optical parameter
The ratio SPM:Turbidity depends on the nature and size of particles
Sat SPM vs in-situ SPM
In-situ SPM vs in-situ Turbidity Sat SPM vs in-situ Turbidity
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Derived products of SPM
Reconstruction of a Neap/Spring cycle of surface SPM from Ocean
Colour data
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SPM Variability during a spring-neap tidal cycle
MarchNeap Tide
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SPM Variability during a spring-neap tidal cycle
March
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SPM Variability during a spring-neap tidal cycle
March
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SPM Variability during a spring-neap tidal cycle
March
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SPM Variability during a spring-neap tidal cycle
March
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SPM Variability during a spring-neap tidal cycle
March
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March
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SPM Variability during a spring-neap tidal cycle
March
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MarchSpring Tide
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The quality indicator for the phytoplankton biomass in France is the percen+le 90 of the Chl-‐a during the
produc+ve period (March to October)
Ecological Status High Good Moderate Poor Bad
Level of the P90 chl-‐a (mg.m-‐3)
0 – 5 5 – 10 10 – 20 20 – 40 > 40
Limits of the P90 classes applied to the coastal water bodies for the Atlantic Coast
The Water Framework DirecBve
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But the best contribution of the satellite is clearly the spatial coverage
Limits of the WFD water bodies
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The Marine Strategy DirecBve
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Coastal waters are optically complex but strong needs and capacities for monitoring several parameters of the marine environment (eutrophication, turbidity and water clarity, HABs) help to apply remote-sensing methods.
Conclusion
As MERIS proved to be an excellent sensor, we are looking forward to working with OLCI/Sentinel-3 data