Abstract

Fjords and estuaries exchange large amounts of solutes, gases, and particulates between fluvial and marine systems. These exchanges and their relative distributions of compounds/particles are partially controlled by stratification and water circulation. The spatial and vertical distributions of N2O, an important greenhouse gas, along with other oceanographic variables, are analyzed from the Reloncaví estuary (RE) (~41° 30′ S) to the gulf of Corcovado in the interior sea of Chiloé (43° 45′ S) during the austral winter. Freshwater runoff into the estuary regulated salinity and stratification of the water column, clearly demarking the surface (<5 m depth) and subsurface layer (>5 m depth) and also separating estuarine and marine influenced areas. N2O levels varied between 8.3 and 21 nM (corresponding to 80 and 170 % saturation, respectively), being significantly lower (11.8 ± 1.70) at the surface than in subsurface waters in the Reloncaví estuary (14.5 ± 1.73). Low salinity and NO3−, NO2−, and PO43− levels, as well as high Si(OH)4 values were associated with low surface N2O levels. Remarkably, an accumulation of N2O was observed in the subsurface waters of the Reloncaví sound, associated with a relatively high consumption of O2. The sound is exposed to increasing anthropogenic impacts from aquaculture and urban discharge, occurring simultaneously with an internal recirculation, which leads to potential signals of early eutrophication. In contrast, within the interior sea of Chiloé (ISC), most of water column was quasi homohaline and occupied by modified subantarctic water (MSAAW), which was relatively rich in N2O (12.6 ± 2.36 nM) and NO3− (18.3 ± 1.63 μM). The relationship between salinity, nutrients, and N2O revealed that water from the open ocean, entering into ISC (the Gulf of Corcovado) through the Guafo mouth, was the main source of N2O (up to 21 nM), as it gradually mixed with estuarine water. In addition, significant relationships between N2O excess vs. AOU and N2O excess vs. NO3− suggest that part of N2O is also produced by nitrification. Our results show that the estuarine and marine waters can act as light source or sink of N2O to the atmosphere (air–sea N2O fluxes ranged from −1.57 to 5.75 μmol m−2 day−1), respectively; influxes seem to be associated to brackish water depleted in N2O that also caused a strong stratification, creating a barrier to gas exchange.

Highlights

  • Nitrous oxide (N2O) is an important trace atmospheric greenhouse gas, with a greater radiative efficiency than CO2 (298 times) (IPCC 2013), and a high capacity to weaken the ozone layer (Ravishankara et al 2009)

  • Mainly salinity, clearly separated the study area into two sections; those influenced by river discharge, including the Reloncaví estuary (RE) and sound (Sts. 7b, 7c, 6, 5, 4, 3, 8, and 9), and the marine area associated with the interior sea of Chiloé (ISC), including the Gulf of Ancud and Gulf of Corcovado (Sts. 14, 16, 20, 21, 33, 36, and 38)

  • Our results were representative of an austral winter period in northern Chilean Patagonia that coincided with maximum precipitation in the area

Read more

Summary

Introduction

Nitrous oxide (N2O) is an important trace atmospheric greenhouse gas, with a greater radiative efficiency than CO2 (298 times) (IPCC 2013), and a high capacity to weaken the ozone layer (Ravishankara et al 2009). When O2 is low enough, a complete N oxide (e.g., NO3−) reduction to N2 occurs, causing the consumption of N2O (Cohen and Gordon 1978; Codispoti and Christensen 1985). Both nitrification and denitrification processes demonstrate different responses to O2 concentration (Kock and Bange 2015) and depend, respectively, on NH4+ or organic matter as electron donors and O2 and NO3− as electron acceptors. Inconsistent levels of O2, NO3−, and organic material (or ammonium as the degradation product), which are metabolized by nitrifying and/or denitrifying microorganisms, lead to spatially and temporally heterogeneous N2O production and emission across the air–sea interface

Objectives
Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call