Abstract
The shallow, brackish (11–18‰ salinity) Roskilde Fjord represents a eutrophication gradient with annual averages of chlorophyll, ranging from 3 to 25 mg chl am−3. Nutrient loadings in 1985 were 11.3–62.4 g N m−2 yr−1 and 0.4–7.3 g P m−2 yr−1. A simple one-layer advection-diffusion model was used to calculate mass balances for 7 boxes in the fjord. Net loss rates varied from −32.2 to 17.9 g P m−2 yr−1 and from −3.3 to 66.8 g N m−2, corresponding to 74% of the external P-loading and 88% of the external N-loading to the entire estuary.
Gross sedimentation rates measured by sediment traps were between 7 and 52 g P m−2 yr−1 and 50 and 426 g N m−2 yr−1 respectively. Exchangeable sediment phosphorus varied in annual average between 2.0 and 4.8 g P m−2 and exchangeable sediment nitrogen varied from 1.9 to 33.1 g N m−2. Amplitudes in the exchangeable pools followed sedimentation peaks with delays corresponding to settling rates of 0.3 m d−1. Short term nutrient exchange experiments performed in the laboratory with simultaneous measurements of sediment oxygen uptake showed a release pattern following the oxygen uptake, the changes in the exchangeable pools and the sedimentation peaks.
The close benthic-pelagic coupling also exists for the denitrification with maxima during spring of 5 to 20 mmol N m−2 d−1. Denitrification during the nitrogen-limited summer period suggests dependence on nitrification. Comparisons with denitrification from other shallow estuaries indicate a maximum for denitrification in estuaries of about 250 µmol N m−2 h−1 achieved at loading rates of about 25–125 g N m−2 yr−1.
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Kamp-Nielsen, L. (1992). Benthic-pelagic coupling of nutrient metabolism along an estuarine eutrophication gradient. In: Hart, B.T., Sly, P.G. (eds) Sediment/Water Interactions. Developments in Hydrobiology, vol 75. Springer, Dordrecht. https://doi.org/10.1007/978-94-011-2783-7_39
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DOI: https://doi.org/10.1007/978-94-011-2783-7_39
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