Abstract
Abstract. Over the last decades, the impact of human activities on the global nitrogen (N) cycle has drastically increased. Consequently, benthic N cycling has mainly been studied in anthropogenically impacted estuaries and coasts, while in oligotrophic systems its understanding is still scarce. Here we report on benthic solute fluxes and on rates of denitrification, anammox, and dissimilatory nitrate reduction to ammonium (DNRA) studied by in situ incubations with benthic chamber landers during two cruises to the Gulf of Bothnia (GOB), a cold, oligotrophic basin located in the northern part of the Baltic Sea. Rates of N burial were also inferred to investigate the fate of fixed N in these sediments. Most of the total dissolved fixed nitrogen (TDN) diffusing to the water column was composed of organic N. Average rates of dinitrogen (N2) production by denitrification and anammox (range: 53–360 µmol N m−2 day−1) were comparable to those from Arctic and subarctic sediments worldwide (range: 34–344 µmol N m−2 day−1). Anammox accounted for 18–26 % of the total N2 production. Absence of free hydrogen sulfide and low concentrations of dissolved iron in sediment pore water suggested that denitrification and DNRA were driven by organic matter oxidation rather than chemolithotrophy. DNRA was as important as denitrification at a shallow, coastal station situated in the northern Bothnian Bay. At this pristine and fully oxygenated site, ammonium regeneration through DNRA contributed more than one-third to the TDN efflux and accounted, on average, for 45 % of total nitrate reduction. At the offshore stations, the proportion of DNRA in relation to denitrification was lower (0–16 % of total nitrate reduction). Median value and range of benthic DNRA rates from the GOB were comparable to those from the southern and central eutrophic Baltic Sea and other temperate estuaries and coasts in Europe. Therefore, our results contrast with the view that DNRA is negligible in cold and well-oxygenated sediments with low organic carbon loading. However, the mechanisms behind the variability in DNRA rates between our sites were not resolved. The GOB sediments were a major source (237 kt yr−1, which corresponds to 184 % of the external N load) of fixed N to the water column through recycling mechanisms. To our knowledge, our study is the first to document the simultaneous contribution of denitrification, DNRA, anammox, and TDN recycling combined with in situ measurements.
Highlights
Excess of fixed nitrogen (N) accumulating in aquatic ecosystems due to planktonic dinitrogen (N2) fixation, discharge of wastewater, and runoff of fertilizers constitutes one of the greatest eutrophication issues in coastal waters (Howarth and Marino, 2006), leading to water column anoxia and biodiversity loss (Vaquer-Sunyer and Duarte, 2008)
Sediment at GOB1 was dark olive brown in the top 3 cm, where few burrows of the amphipod Monoporeia affinis were visible against the walls of the plastic liners
Sediment at GOB2 was similar to GOB1 but with grey/black laminations instead
Summary
Excess of fixed nitrogen (N) accumulating in aquatic ecosystems due to planktonic dinitrogen (N2) fixation, discharge of wastewater, and runoff of fertilizers constitutes one of the greatest eutrophication issues in coastal waters (Howarth and Marino, 2006), leading to water column anoxia and biodiversity loss (Vaquer-Sunyer and Duarte, 2008). S. Bonaglia et al.: The fate of fixed N in marine sediments with low organic loading the global N loss due to the two anaerobic, microbial processes denitrification and anammox (Seitzinger et al, 2006). Denitrification is the stepwise reduction of nitrate to nitrous oxide and N2, while anammox produces N2 through ammonium oxidation coupled to nitrite reduction. These two processes help in counteracting eutrophication by permanent removal of fixed N from the system. A third N reducing process, dissimilatory nitrate reduction to ammonium (DNRA), leads to recycling and preservation of fixed N in the system and can increase the occurrence of algal blooms and exacerbate eutrophication if stimulated at the expense of the N2-producing pathways (An and Gardner, 2002; Bonaglia et al, 2014a)
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