Abstract

Inland waters (lakes, rivers and reservoirs) are now understood to contribute large amounts of methane (CH4) to the atmosphere. However, fluxes are poorly constrained and there is a need for improved knowledge on spatiotemporal variability and on ways of optimizing sampling efforts to yield representative emission estimates for different types of aquatic ecosystems. Low-latitude floodplain lakes and wetlands are among the most high-emitting environments, and here we provide a detailed investigation of spatial and day-to-day variability in a shallow floodplain lake in the Pantanal in Brazil over a five-day period. CH4 flux was dominated by frequent and ubiquitous ebullition. A strong but predictable spatial variability (decreasing flux with increasing distance to the shore or to littoral vegetation) was found, and this pattern can be addressed by sampling along transects from the shore to the center. Although no distinct day-to-day variability were found, a significant increase in flux was identified from measurement day 1 to measurement day 5, which was likely attributable to a simultaneous increase in temperature. Our study demonstrates that representative emission assessments requires consideration of spatial variability, but also that spatial variability patterns are predictable for lakes of this type and may therefore be addressed through limited sampling efforts if designed properly (e.g., fewer chambers may be used if organized along transects). Such optimized assessments of spatial variability are beneficial by allowing more of the available sampling resources to focus on assessing temporal variability, thereby improving overall flux assessments.

Highlights

  • Methane is an important greenhouse gas (GHG) that accounts for approximately 20% of the radiative forcing, according to a 100-year time period, and the global warming potential of CH4 is approximately 25 times greater by weight in comparison with carbon dioxide (CO2) [1]

  • Methane can be oxidized under anaerobic conditions by syntrophic consortia using e.g. sulfate as electron acceptor [5]

  • As a consequence of these production and consumption pathways, high natural methane emissions can be expected from environments in which gases produced in anoxic zones can be transported to the atmosphere rapidly enough to escape complete oxidation before reaching the atmosphere

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Summary

Introduction

Methane is an important greenhouse gas (GHG) that accounts for approximately 20% of the radiative forcing, according to a 100-year time period, and the global warming potential of CH4 is approximately 25 times greater by weight in comparison with carbon dioxide (CO2) [1]. Methane is primarily formed by a terminal degradation step in anaerobic degradation of organic matter by methanogenic archea [2,3,4]. Acetate or molecular hydrogen (H2) and CO2, being formed in earlier fermentative degradation steps are considered to be the most important substrates for methanogenesis, the use of a handful of other small organic molecules have been demonstrated as well [2]. CH4 can be oxidized to CO2 and water by methane oxidizing bacteria. Methane can be oxidized under anaerobic conditions by syntrophic consortia using e.g. sulfate as electron acceptor [5]. As a consequence of these production and consumption pathways, high natural methane emissions can be expected from environments in which gases produced in anoxic zones can be transported to the atmosphere rapidly enough to escape complete oxidation before reaching the atmosphere

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