Nitrogen fluxes and processes were estimated in sandy and muddy sediments f
rom the shallow eutrophic lake Nuldernauw, The Netherlands. N-2, NH4+, NOx-
and CH4 fluxes were measured from sediment samples collected throughout th
e year and incubated under both oxic and anoxic conditions at 2, 12 and 23
degrees C. Fluxes increased with temperature with a mean temperature factor
of 1.9 +/- 0.3 for a 10 degrees C increase for both sediment types. At the
same temperature the total N fluxes (N-2 + NOx- + NH4+) from the muddy sed
iments were generally larger than those from the sandy sediments. These dif
ferences are related to the relatively high availability of decomposable or
ganic matter in the muddy sediments compared to the sandy sediments. Especi
ally the denitrification was influenced by the organic matteI content: 75-9
0% of the total N flux was denitrified by the muddy sediment whereas only 4
5-65% was denitrified by the sandy sediments. NH4+ fluxes were much higher
and NOx- fluxes were much lower in cores collected just after spring bloom
of phytoplankton, compared to cores collected during other periods. This ef
fect was most pronounced at the high incubation temperature. The freshly se
ttled and easily degradable organic matter at the top of the sediment appea
red to be of great influence. Based on the results a general concept, combi
ning the effects of temperature and (easily degradable) organic matter on N
loss due to the coupled denitrification, was postulated. The concept impli
es that the coupled denitrification initially increases with increasing con
tents of (fresh) organic matter and/or temperature. By a further increase o
f organic matter or temperature, however, more oxygen is consumed by the ae
robic mineralization and the CH4 oxidation and little or no oxygen remains
available for the oxidation of nitrogen. Consequently no or less coupled de
nitrification can occur. Although high temperatures are not often found in
the Dutch surface waters, these conditions can occur in spring and summer.
Then nitrogen removal from the sediment-water system by the coupled nitrifi
cation-denitrification will be reduced and ammonium will be released to the
overlying water where it can be consumed by algae. (C) 1998 Elsevier Scien
ce Ltd. All rights reserved.