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The Oder Estuary - IOW

The Oder Estuary - IOW

The Oder Estuary - IOW

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structure is described in detail together with some general results of its application to the nutrient<br />

budget calculations for the 1980-99 period.<br />

1.2 <strong>The</strong> <strong>Oder</strong> River estuary<br />

<strong>The</strong> <strong>Oder</strong> River estuary is long and complex. It consists of many river branches, Dabie Lake and<br />

the largest water body – the Szczecin Lagoon with its three outlets (Figure 1.1). <strong>The</strong> Szczecin<br />

Lagoon, of an area 687 km 2 and an average depth of 3.8 m, is divided into two parts – the Kleines<br />

Haff (Maly Zalew) on the German side and the Grosses Haff (Wielki Zalew with Roztoka<br />

Odrzanska) located within the Polish territory. <strong>The</strong> Kleines Haff is separated from the Grosses Haff<br />

(Wielki Zalew) by a shallow sill and the water exchange between the two parts of the lagoon is<br />

limited. <strong>The</strong> Kleines Haff receives on average only 15–20 % of the <strong>Oder</strong> waters, passing to the<br />

Baltic Sea (MOHRHOLZ & LASS 1998). Most of the water exchange (from 60 to 75 %) between the<br />

Lagoon and the Baltic Sea takes place through the Swina outlet located in the central part of the<br />

Lagoon, or more precisely the artificially deepened shipping channel which runs through the<br />

Grosses Haff to the Szczecin harbor (MAJEWSKI 1980; MOHRHOLZ & LASS 1998).<br />

2 Model description<br />

2.1 General structure of the model<br />

<strong>The</strong> dynamic model is designed for long-term (decades) simulations which require long calculation<br />

time. This is the main reason why a box model was chosen and its structure is kept simple. Also,<br />

considering limitations posed by the resolution and quality of the long-term data, as well as taking<br />

into account that the lagoon is a shallow and well mixed water body, an application of a box model<br />

was considered as appropriate.<br />

<strong>The</strong> internal time scale of the model is one day. Model was coded in MATLAB 6.1 using the ode23<br />

solver based on a Runge-Kutta method. In the model seven state variables are considered:<br />

phytoplankton DIN, PO4, Ndet and Pdet (nitrogen and phosphorus in detritus - suspended organic<br />

matter in water column) and also Nsed, Psed (nitrogen and phosphorus in the active layer of<br />

sediment). <strong>The</strong>re is one phytoplankton group expressed in the model in nitrogen units (Figure 2.1).<br />

<strong>The</strong> nitrogen units in phytoplankton are recalculated into phosphorus according to constant<br />

Redfield stoichiometry. Constant ratio is also used to recalculate model results in nitrogen or<br />

phosphorus units into Chl_a or carbon units:<br />

N : P [mmol] = 16 : 1; N : C : Chl_a [mg] = 7 : 40 : 1

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