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dc.contributor.author Gribsholt B.
dc.contributor.author Struyf E.
dc.contributor.author Tramper A.
dc.contributor.author Andersson M.G.I.
dc.contributor.author Brion N.
dc.contributor.author De brabandere L.
dc.contributor.author Van damme S.
dc.contributor.author Meire P.
dc.contributor.author Middelburg Ja.J.
dc.contributor.author Dehairs F.
dc.contributor.author Boschker H.T.S.
dc.date.accessioned 2024-10-18T08:57:39Z
dc.date.available 2024-10-18T08:57:39Z
dc.date.issued 2006
dc.identifier https://www.elibrary.ru/item.asp?id=51110573
dc.identifier.citation Biogeochemistry, 2006, 80, 3, 289-298
dc.identifier.issn 0168-2563
dc.identifier.uri https://repository.geologyscience.ru/handle/123456789/45982
dc.description.abstract The fate and transport of watershed-derived ammonium in a tidal freshwater marsh fringing the nutrient rich Scheldt River, Belgium, was quantified in a whole ecosystem 15N labeling experiment. In late summer (September) we added 15N-NH 4 + to the flood water entering a 3477 m2 tidal freshwater marsh area, and traced the ammonium processing and retention in four subsequent tide cycles. In this paper we present the results for the water-phase components of the marsh system and compare them to a similar experiment conducted in spring/early summer (May). Changes in concentration and isotopic enrichment of NO 3 −  + NO 2 − , N2O, N2, NH 4 + and suspended particulate nitrogen (SPN) were measured in concert with a mass balance study. All analyzed N-pools were labeled, and 49% of the added 15NH 4 + was retained or transformed. The most important pool for 15N was nitrate, accounting for 17% of 15N-transformation. N2, N2O and SPN accounted for 2.4, 0.02 and 1.4%, respectively. The temporal and spatial patterns of 15N transformation in the water phase component of the system were remarkably similar to those observed in May, indicating good reproducibility of the whole ecosystem labeling approach, but the absolute ammonium transformation rate was 3 times higher in May. While the marsh surface area was crucial for nitrification in May this was less pronounced in September. Denitrification, on the other hand, appeared more important in September compared to May.
dc.subject NITROGEN TRANSFORMATION
dc.subject TIDAL FRESHWATER MARSH
dc.subject 15N
dc.subject NITRIFICATION
dc.subject DENITRIFICATION
dc.title AMMONIUM TRANSFORMATION IN A NITROGEN-RICH TIDAL FRESHWATER MARSH
dc.type Статья
dc.identifier.doi 10.1007/s10533-006-9024-8


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