NITROGEN CYCLING ACROSS THE SEDIMENT-WATER INTERFACE IN AN EUTROPHIC,ARTIFICIALLY OXYGENATED LAKE

Citation
P. Hohener et R. Gachter, NITROGEN CYCLING ACROSS THE SEDIMENT-WATER INTERFACE IN AN EUTROPHIC,ARTIFICIALLY OXYGENATED LAKE, Aquatic sciences, 56(2), 1994, pp. 115-132
Citations number
43
Categorie Soggetti
Water Resources",Limnology,"Marine & Freshwater Biology
Journal title
ISSN journal
10151621
Volume
56
Issue
2
Year of publication
1994
Pages
115 - 132
Database
ISI
SICI code
1015-1621(1994)56:2<115:NCATSI>2.0.ZU;2-9
Abstract
Processes controlling the nitrogen (N) exchange between water and sedi ment in eutrophic Lake Sempach were studied using three different inde pendent methods: benthic flux chambers, interstitial water data and hy polimnetic mass balances. The sediments released NH4+ (1.1-16.1 mmoles m-2 d-1), NO2- (0.1-0.4 mmoles m-2 d-1) and dissolved organic N (<0.2 5 mmoles m-2 d-1). A net NO3- consumption (2.4-11.1 mmoles m-2 d-1) re lated to the NO3- concentrations in the overlying water was observed i n all benthic chamber experiments. The flux of the reactive species NO 3- and NH+ was found to depend on hydrodynamic conditions in the water overlying the sediment. For this reason, benthic chambers overestimat ed the fluxes of inorganic N compared to the other methods. Thus, in s hort-term flux chamber experiments the sediment may either become a si nk or a source for inorganic N depending on the O2 concentration in th e water overlying the sediment and the stirring rate. As demonstrated with a (NO3)-N-15 experiment, nitrate-ammonification accounted for les s than 12% of the total NO3- consumption. After six years of artificia l oxygenation in Lake Sempach, a decrease in hypolimnetic total inorga nic nitrogen (TIN) was observed in the last two years. The occurrence of dense mats of H2S-oxidizing Beggiatoa sp. indicated micro-aerobic c onditions at the sediment surface. Under these conditions, a shorter d istance between the ecological niches of nitrifying and denitrifying b acteria, and therefore a faster NO3--transport, can possibly explain t he lowering of TIN by enhanced net denitrification.