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The Oder Estuary - IOW

The Oder Estuary - IOW

The Oder Estuary - IOW

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50<br />

µmol/l<br />

µmol/l<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

175<br />

150<br />

125<br />

100<br />

75<br />

50<br />

25<br />

0<br />

Jahresgang SiO4-Si im Kleinen Haff<br />

Jahre 1990 - 1999<br />

J F M A M J J A S O N D<br />

Jahresgang SiO4-Si in der Pommerschen Bucht<br />

Jahre 1990 - 1999<br />

J F M A M J J A S O N D<br />

95%<br />

5%<br />

75%<br />

25%<br />

Median<br />

95%<br />

5%<br />

75%<br />

25%<br />

Median<br />

µmol/l<br />

350<br />

300<br />

250<br />

200<br />

150<br />

100<br />

50<br />

0<br />

Jahresgang SiO4-Si im Großen Haff<br />

Jahre 1991 - 1999<br />

J F M A M J J A S O N D<br />

Figure 7.2: Annual course of silicate-Si concentrations (µmol/l) in the Kleines Haff (top, left),<br />

the Pomeranian Bay (bottom, left) 1990 – 1999 and the Wielki Zalew (top, right)<br />

1991 – 1999. Data source: State Agency of Environment, Protection of Nature and<br />

Geology Mecklenburg-Vorpommern (LUNG) and West Pomeranian Voivodeship<br />

Inspectorate in Szczecin (WIOS).<br />

<strong>The</strong> long-term development of silicate concentrations is very much dominated by the high<br />

variability of concentrations. <strong>The</strong> trends in the Kleines Haff and Wielki Zalew are not well in<br />

agreement and we refrain from an interpretation of the data (Fig. 7.1).<br />

Silicate is another element where the annual dynamic of the concentrations reflects the biological<br />

activity. During winter we observe high concentrations and a steady decrease towards May. Similar<br />

to phosphorus, silicate is taken up by the diatom bloom in spring and largely depleted in the water<br />

column (Fig. 7.2). Silicate is incorporated into diatoms shells and these shells are subject to<br />

sedimentation when the algae die. Due to dissolution, a steady increase in silicate concentrations is<br />

observed during the rest of the year. This process can be interrupted by diatom developments later<br />

in the year, when silicate is consumed again and partly removed from the water column.<br />

In spring, the spatial pattern of silicate concentrations is controlled by regional differences in<br />

uptake during algae blooms. During summer, regional differences in silicate dissolution create the<br />

spatial pattern in the lagoon. In the winter semi-annual gradients maintained by high <strong>Oder</strong> river<br />

discharge are prevailing (7.3). <strong>The</strong> data shows that the lagoon acts as an efficient sink for silicate.<br />

95%<br />

5%<br />

75%<br />

25%<br />

Median

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