labof remote sensing and spatial analysis lab of sea...
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Department of Physical Oceanography
Lab of Remote Sensing and Spatial Analysis
Lab of Sea Dynamic
Lab of Remote Sensing and Spatial AnalysisInvestigations based on:
satellite datadatadatadata (AVHRR, SeaWiFS, Meteosat)
own measured data by
HRPT Data Receiver Sonda STD
Tethered Spectral Radiometer Buoy
Fluorometer Tachymetr
Coulter counter Beam transmittance meter
exchange of data between: IO PAS, MI, MFI, RDANH
ModelsModelsModelsModels (M3D_UG, ICM, ECMWF, HIROMB)
ProjectsProjectsProjectsProjects::::
Analysis of solar energy inflow and temperature distribution at the Baltic Sea surface basing on satellite data
The consequence of coastal upwellings phenomenon for biological productivity along Polish coast
of the Baltic Sea
Application of the SeaWiFS data for studies of the water turbidity in the Baltic Sea
HRPT
Raw AVHRR
data
HRPT
Raw AVHRR
data
ASDIK
System of Automatic
Registration, Geometric
and Geographic
Correction of AVHRR
Data
ASDIK
System of Automatic
Registration, Geometric
and Geographic
Correction of AVHRR
Data
PRODUCTS
Quicklooks & UTM
maps of:
SST, Brightens
temperature, Albedo,
cloudiness
PRODUCTS
Quicklooks & UTM
maps of:
SST, Brightens
temperature, Albedo,
cloudiness
Data base of
raw data
Data base of
product
WWW interfaceWWW interface
The The sattelite monitoringsattelite monitoring
Lab of Sea Dynamic
•Long-term changes hydrometeorological of climate
•Long-term changes of the Baltic Sea level
•Patterns of circulation in the Baltic
•Ecohydrodynamic model of the Baltic Sea
•Coastal upwellings in the Baltic Sea
•Sea state modelling using system identification
methods
•Modelling of nearshore currents induced by wind
waves
•Modelling of the interaction between currents and
surface waves
Investigations focused on:
hydrology, waves and ecohydrodynamichydrology, waves and ecohydrodynamichydrology, waves and ecohydrodynamichydrology, waves and ecohydrodynamic
Correlation between the NAO index and runoff from selected
sub-catchment areas into the Baltic Sea
The examples of many years’ sea level changes of the following stations: Wismar, Warnemunde, Kunkolmsfort, Geteborg, Ratan, Oulu
The time series of the mean annual sea level in the period of 1900-2000
Principal components of time series variability
Spatially averaged changes of sea level in time (a) and the main three principal components of sea level variability, which explains 93.6% of total variance (b-d)
Spatial charge distribution of the three variability Components of mean sea level in 100 years’ period
Sea state modelling using system identification methodsComparison of System Identification modelling (right) and spectral wave model WAM results (left)
for significant wave height (upper) and mean wave period (down) for 1100 hrs UTC on March, 7th, 2000.
Methods are based on finding simple, mathematical transformations between two sets of variables
(e.g. wind field and wave characteristics).
Modelling of nearshore currents induced by wind waves
Example of the longshore current
model results (upper) along multi-
bar bottom crossection (down).
Incoming deep wave water parameters:
Ho = 0.8m, To = 6s, θo = 65o
Significant influence on the
coastal zone circulation has a
wave breaking. Energy, which is
dissipated in this process, causes
coastal wave-driven currents.
Analytical and numerical models
of coastal zone circulation are
based on radiation stress
concept.
Operational System for Coastal Waters
of Gdańsk Region
Hydrodynamic model
M3D
Meteorological forecasts
UMPL Model
ICM
ProDeMO
ecosystem model
Network ofNetwork of seasea level level
river discharges river discharges
chemical and biological chemical and biological
stationsstations
Remote
Sensing
Monitoring
Observations and
hydrological forecasts
IMWM
Operational
observations
BOOS
Ecohydrodynamic modelProcesses included in the ProDeMo:
1) nutrient uptake by phytoplankton,
2) phytoplankton grazing by zooplankton,
3) phytoplankton respiration,
4) phytoplankton decay,
5) sedimentation,
6) nutrients release from sediment,
7) atmospheric deposition,
8) denitrification,
9) mineralisation,
10) zooplankton respiration,
11) sedimentation of phosphorus
adsorbed on particles,
12) detritus sedimentation,
13) zooplankton decay
14) nitrogen fixation
15) nutrient deposition.
influenced the dissolved oxygen:
16) reaeration,
17) flux to atmosphere due to the over saturated
conditions,
18) zooplankton respiration,
19) phytoplankton respiration,
20) assimilation,
21) mineralisation,
22) nitrification,
23 ) denitrification
3D Hydrodynamic
Model
Meteorological Data:
Model UMPL (ICM)
River
Inflows
Data
Production and
Destruction of
Organic Matter
Model (ProDeMo)
Solar
Radiation
Model
Atmos-
pheric
Deposition
NUTRIENTS
N-NO3
P-PO4
Si-SiO4
N-NH4
DETRITUS
CDETR
PDETR
SiDETR
NDETR
ZOOPLANKTON
Zooplankton
C:N:P
PHYTOPLANKTON
Dinoflagellate
NSED PSED SiSED
DISSOLVED
OXYGEN
Water
Atmosphere
Sediment
1
2
3
4 53
6
7
8
7
10
11
12
13
16 17
18
19 20
21
22
23
Spring diatoms
Autumn diatoms
Blue-green algae
Green algae
Inactive layer
Active
layer
14
15 15 15
NH4[gm
-3]
0.00
0.02
0.04
0.06NH4_OBS
NH4_MOD
R=-0.037
Ntot[gm
-3]
0.00
0.10
0.20
0.30
0.40
Ntot_OBS
Ntot_MOD
R=0.480
PO4[gm
-3]
0.00
0.01
0.02
0.03
0.04PO
4_OBS
PO4_MOD
R=0.713
Ptot[gm
-3]
0.00
0.01
0.02
0.03
0.04
Ptot_OBS
Ptot_MOD
R=0.434
SiO
4[gm
-3]
0.00
0.10
0.20
0.30
0.40
0.50
SiO4_OBS
SiO4_MOD
R=0.269
O2[gm
-3]
8.0
11.0
14.0
17.0 O2_OBS
O2_MOD
R=0.852
Tw[oC]
0.0
8.0
16.0
24.0
Tw_OBS
Tw_MOD
R=0.976
P140
P39
P5 P63
Baltic Sea
KNP
P1
P101
P104
P110
P116
R4
ZN2
ZN4
Vistula
Gulf of Gdañsk
Gdañsk
grid step: 5 NM
grid step: 1 NM
Validation Validation
of the of the ProDeMoProDeMo modelmodelS[psu]
6.00
6.50
7.00
7.50
8.00S_OBS
S_MOD
R=0.503
1994 1995 1996 1997 1998 1999 2000 2001 2002
NO3[gm
-3]
0.00
0.04
0.08
0.12NO3_OBS
NO3_MOD
R=0.800
0 10 20 30 40 50
-100
-80
-60
-40
-20
0
Depth [m]
0 10 20 30 40 50
Distance [km]
-100
-80
-60
-40
-20
0
Depth [m]
observed
modelled
0.0
0.1
0.2
0.3
0.4
0.5
0.6
NO3 [g m3]
0 10 20 30 40 50
Distance [km]
-100
-80
-60
-40
-20
0
Depth [m]
observed
0 10 20 30 40 50
-100
-80
-60
-40
-20
0
Depth [m]
modelled
0.00
0.02
0.04
0.06
0.08
0.10
0.12
PO4 [g m3]
5 10 15 20 25
Salinity [PSU]
8 9 10 11
Dissolved oxygen
[g m-3]
0 0.005 0.01 0.01 5 0.02
N-NH4 [g m-3]
0.01 0.03
P-PO4 [g m-3]
0.1 0.4 0.7 1 1.3
Si-SiO4 [g m-3]
11 13 15 17 19 21 23
Temperature [°C]
Spatial Spatial distribution distribution
of the of the nutrientsnutrients –– JuneJune 19991999
0 0.05 0.1 0.15 0 .2 0.25
N-NO3 [g m-3]
The impact of the Vistula river on the
coastal water of the Gulf of Gdansk
Scenarios analysis by ecohydrodynamic
model
N:P 2002 N:P 2015
0 10 20 60 100 140 180 N:P
2002 2015
0 40 80 120 160 200
Primary production
[gC m-2/ year ]
P rimary production [106 kg/year]
800850900950
1000
Reference year
2002
Policy targets
low
Policy ta rgets
high
Deep green
The lowest biological productivity has been The lowest biological productivity has been
obtained for Deep green scenario obtained for Deep green scenario -- 7.5 % 7.5 %
less than in the reference year 2002.less than in the reference year 2002.
Due to reduction of phosphorus loads from Due to reduction of phosphorus loads from
40.9 % for the policy target low to 45.5 % 40.9 % for the policy target low to 45.5 %
for Deep green scenario and nitrogen loads for Deep green scenario and nitrogen loads
less than 10%, the phosphorus becomes less than 10%, the phosphorus becomes
a limiting nutrient in the Gulf of Gdansk a limiting nutrient in the Gulf of Gdansk
in the analyzed scenarios.in the analyzed scenarios.
15 20 25 30
54
56
58
60
62
64
66
Annually averaged circulation pattern in the Baltic Sea
0
0.1
0.2
0.3
0.4
0.5
0.6
Velocity [m/s]
0.05 0.1
15 20 25 30
54
56
58
60
62
64
66
surface
0
0.04
0.08
0.12
0.16
0.2
0.24
0.28
0.32
magnitude[m/s ]
∑= uN
1u
vectorial mean velocities
∑= vN
1v
∑=
+
+=
N
1i
2
1
2
i
2
i
2
122
)vu(N
1
)vu(B
∑=
+=N
1i
2
1
2
i
2
i )vu(N
1V
arithmetic mean velocities
stability
surface
15 20 25 30
54
56
58
60
62
64
66
spring
0
0.1
0.2
0.3
0.4
0.5
0.6
Velocity [m/s]
0.05 0.1
stability
15 20 25 30
54
56
58
60
62
64
66
0
0.1
0.2
0.3
0.4
0.5
0.6
Velocity [m/s]
0.05 0.1
stability
autumn