4.6 Article

Denitrification and nitrous oxide effluxes in boreal, eutrophic river sediments under increasing nitrate load: a laboratory microcosm study

期刊

BIOGEOCHEMISTRY
卷 91, 期 2-3, 页码 105-116

出版社

SPRINGER
DOI: 10.1007/s10533-008-9262-z

关键词

Stable isotopes; Eutrophication; NO(3)(-) removal; N(2)O/N(2) ratio; Bothnian Bay; River sediment

资金

  1. Academy of Finland [202429]
  2. Graduate School of Environmental Science and Technology (EnSTe)
  3. Ella and Georg Ehrnrooth Foundation
  4. Academy of Finland (AKA) [202429, 202429] Funding Source: Academy of Finland (AKA)

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Intact sediment cores from rivers of the Bothnian Bay (Baltic Sea) were studied for denitrification based on benthic fluxes of molecular nitrogen (N(2)) and nitrous oxide (N(2)O) in a temperature controlled continuous water flow laboratory microcosm under 10, 30, 100, and 300 mu M of (15)N enriched nitrate (NO(3) (-), similar to 98 at. %). Effluxes of both N(2) and N(2)O from sediment to the overlying water increased with increasing NO(3) (-) load. Although the ratio of N(2)O to N(2) increased with increasing NO(3) (-) load, it remained below 0.04, N(2) always being the main product. At the NO(3) (-) concentrations most frequently found in the studied river water (10-100 mu M), up to 8% of the NO(3) (-) was removed in denitrification, whereas with the highest concentration (300 mu M), the removal by denitrification was less than 2%. However, overall up to 42% of the NO(3) (-) was removed by mechanisms other than denitrification. As the microbial activity was simultaneously enhanced by the NO(3) (-) load, shown as increased oxygen consumption and dissolved inorganic carbom efflux, it is likely that a majority of the NO(3) (-) was assimilated by microbes during their growth. The (15)N content in ammonium (NH(4) (+)) in the efflux was low, suggesting that reduction of NO(3) (-) to NH(4) (+) was not the reason for the NO(3) (-) removal. This study provides the first published information on denitrification and N(2)O fluxes and their regulation by NO(3) (-) load in eutrophic high latitude rivers.

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