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Denitrification, anammox, and dissimilatory nitrate reduction to ammonium across a mosaic of estuarine benthic habitats
Author(s) -
Chen JianJhih,
Erler Dirk V.,
Wells Naomi S.,
Huang Jianyin,
Welsh David T.,
Eyre Bradley D.
Publication year - 2021
Publication title -
limnology and oceanography
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.7
H-Index - 197
eISSN - 1939-5590
pISSN - 0024-3590
DOI - 10.1002/lno.11681
Subject(s) - anammox , denitrification , benthic zone , nitrification , estuary , seagrass , environmental science , nitrate , environmental chemistry , nitrogen cycle , ecology , ecosystem , nitrogen , chemistry , denitrifying bacteria , biology , organic chemistry
Estuaries play a key role in moderating the flow of nitrogen (N) to marine ecosystems. However, the magnitude of this N removal can vary dramatically both within and between estuaries due to the benthic habitats present. Here, we compare denitrification, coupled nitrification–denitrification, anammox, and dissimilatory nitrate reduction to ammonium (DNRA) across a mosaic of benthic habitats in the subtropical Noosa River Estuary, Australia. Using 15 N tracer techniques and passive pore‐water samplers, we show that coupled nitrification–denitrification was the dominant pathway for N 2 production across all habitats, with higher rates in vegetated habitats (10–70 μ mol N m −2 h −1 ) compared to bare sediments (0.9–2 μ mol N m −2 h −1 ). Unusual pore‐water profiles in the macroalgal sediments suggest the presence of sulfur‐driven anoxic nitrification of NH 4 + to NO 3 − and N 2 . A benthic N budget showed that combined denitrification and coupled nitrification–denitrification accounted approximately 96% of the N 2 production, while DNRA accounted for 9% of total NO 3 − reduction pathways in the Noosa River Estuary. The macroalgae habitat contributed 76% of total N removal via N 2 production and 65% of N retention via DNRA, despite accounting for only 25% of the total surface area. We show a strong relationship between seagrass and macroalgae area and N 2 production ( r 2 = 0.8; p < 0.01), and as such, the capacity to mitigate reactive N loads in estuaries may decrease with the large‐scale loss of seagrass and other vegetated habitats.