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The Oder Estuary - IOW

The Oder Estuary - IOW

The Oder Estuary - IOW

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Schernewski, G. & T. Dolch (eds.): <strong>The</strong> <strong>Oder</strong> <strong>Estuary</strong> – against the background of the European Water Framework<br />

Directive. Marine Science Reports 57 (2004). ISSN: 0939-396X.<br />

A dynamic box model of the Szczecin Lagoon nutrient cycling<br />

and its first application to the calculation of the nutrient budget<br />

Magdalena Wielgat & Zbigniew Witek<br />

Sea Fisheries Institute, Kollataja 1, 81-332 Gdynia, Poland<br />

Email: wielgat@mir.gdynia.pl, zwitek@mir.gdynia.pl<br />

Summary<br />

In the present paper a dynamic biogeochemical box model of the nutrient cycling within the <strong>Oder</strong><br />

River estuary – the Szczecin Lagoon is presented. <strong>The</strong> model structure is described in detail and<br />

with some general results of the model application to the nutrient budget calculations for the<br />

1980-99 period are given.<br />

1 Introduction<br />

1.1 Introduction<br />

<strong>The</strong> Szczecin Lagoon (in German – <strong>Oder</strong> Haff, Stettiner Haff, in Polish – Zalew Szczeciński) is<br />

one of the key elements of the <strong>Oder</strong>/Odra River estuary (Figure 1.1). Biogeochemical processes<br />

which are part of the functioning of Szczecin Lagoon system influence the quality of the riverine<br />

waters when they finally enter the Baltic Sea. <strong>The</strong> impact of the <strong>Oder</strong> waters on the Baltic Sea is<br />

important, since it is the 5 th largest river in terms of water flow in the whole Baltic Sea drainage<br />

area. <strong>The</strong> <strong>Oder</strong> River drains over 120,000 km² of densely populated and industrialized catchment,<br />

where arable land covers about 50 % of its total area and<br />

the river discharges high loads of nutrients to the sea. In<br />

this paper we present a dynamic biogeochemical box<br />

model describing main processes contributing to the<br />

nutrient cycling within the estuary with the emphasis on<br />

the main part of the estuary – the Szczecin Lagoon. <strong>The</strong><br />

present model represents the approach undertaken by<br />

HUBMORG et al. (2000) to study long-term changes in<br />

biogeochemical processes contributing to the <strong>Oder</strong><br />

River nutrient loads modifications in the river estuary.<br />

However, we think that in this approach the seasonal<br />

pattern of nutrient concentrations and phytoplankton<br />

growth is represented better, as compared to the<br />

approach by HUBMORG et al. (2000). <strong>The</strong> present model<br />

is designed to be used to study nutrient budget of the<br />

<strong>Oder</strong> estuary. In previous works the nutrient transport<br />

and budget within the western part of the <strong>Oder</strong> estuary<br />

was modeled by a hydrodynamic model coupled with<br />

nutrient measurements (MEYER et al. 1998; LAMPE<br />

Fig. 1.1 <strong>The</strong> <strong>Oder</strong> <strong>Estuary</strong>.<br />

1999), this was, however, a short term calculation for<br />

the period 1993-95. In the present paper the model

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