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The Oder Estuary - IOW

The Oder Estuary - IOW

The Oder Estuary - IOW

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ecalculated into salinity using formula calculated by MLODZINSKA (1980) for the Szczecin<br />

Lagoon waters:<br />

S‰ = 1,768 Cl ‰ + 0,072<br />

Sea water inflows from the Pomeranian Bight were calculated on the basis of the following<br />

relationship:<br />

salinity<br />

Szczecin−Lagoon<br />

( waterflow<br />

=<br />

sea−water<br />

* salinity<br />

( waterflow<br />

sea−water<br />

sea−water<br />

+ waterflow<br />

+ waterflow<br />

Assuming that the salinity of the riverine waters equals zero, we receive:<br />

salinity<br />

fresh−water<br />

fresh−water<br />

* salinity<br />

)<br />

sea−water<br />

waterflowsea− water =<br />

× waterflow fresh−water<br />

( salinitysea−water<br />

− salinitySzczecin−Lagoon<br />

)<br />

fresh−water<br />

where mean monthly salinity is expressed in PSU and monthly water inflow in cub. km. <strong>The</strong> annual<br />

amount of saline water (waterflowsea-water) entering the Lagoon calculated with that method<br />

amounted to 3.6 km 3 a -1 on average, ranging from 5.2 to 1.6 km 3 a -1 .<br />

Nutrient concentrations of the sea water entering the Szczecin Lagoon were calculated on the basis<br />

of data from the Baltic Environmental Data Base (Stockholm University), available from<br />

http://www.bed.su.se (BED 2002). Mean values, with monthly resolution, calculated from the area<br />

of the inner part of the Pomeranian Bight (53 o 54 - 54 o 10’ N and 13 o 47’ - 15 o 32’ E) for the period<br />

1993-98 were used. <strong>The</strong> average annual value of Ntot amounted to 34.8 mmol m -3 and Ptot<br />

amounted to 1.22 mmol m -3 .<br />

2.3 Parameterization of the biogeochemical processes<br />

2.3.1 Phytoplankton growth (nutrient uptake)<br />

<strong>The</strong> phytoplankton composition in the Lagoon changes throughout the vegetation season with<br />

spring diatom dominance and summer dominance of blue-green algae. Model represents all<br />

phytoplankton species as one group of phytoplankton and thus one state variable. Seasonal changes<br />

of phytoplankton composition are represented in the model through changing values of some<br />

parameters, such as light optimum and assimilation number, that mimic changing requirements of<br />

different species, or mortality ratio – representing increase of phytoplankton mortality due to<br />

grazing is summer months.<br />

<strong>The</strong> phytoplankton growth (= nutrient uptake) is equivalent to the net primary production in the<br />

model. Phytoplankton growth depends from temperature and can be limited by light and nutrient<br />

availability according to von Liebig’s law of the minimum. Since phytoplankton as a state variable<br />

is represented in the model in nitrogen units, phosphorus uptake is recalculated into nitrogen with a<br />

fixed Redfield ratio.<br />

growth (uptakeN)= µmax x f(Temp) x [MIN (f(PAR), f(DIN), f(PO4))] x PHYTOPLANKTON<br />

2.3.2 Temperature dependence of growth<br />

First part of the equation:<br />

µmax x f(Temp),<br />

105<br />

)

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