Abstract

Abstract. Pelagic methane oxidation was investigated in dependence on differing hydrographic conditions within the redox zone of the Gotland Deep (GD) and Landsort Deep (LD), central Baltic Sea. The redox zone of both deeps, which indicates the transition between oxic and anoxic conditions, was characterized by a pronounced methane concentration gradient between the deep water (GD: 1233 nM, 223 m; LD: 2935 nM, 422 m) and the surface water (GD and LD < 10 nM). This gradient together with a 13C CH4 enrichment (δ13C CH4 deep water: GD −84‰, LD −71‰; redox zone: GD −60‰, LD −20‰; surface water: GD −47‰, LD −50‰; δ13C CH4 vs. Vienna Pee Dee Belemnite standard), clearly indicating microbial methane consumption within the redox zone. Expression analysis of the methane monooxygenase identified one active type I methanotrophic bacterium in both redox zones. In contrast, the turnover of methane within the redox zones showed strong differences between the two basins (GD: max. 0.12 nM d−1, LD: max. 0.61 nM d−1), with a nearly four-times-lower turnover time of methane in the LD (GD: 455 d, LD: 127 d). Vertical mixing rates for both deeps were calculated on the base of the methane concentration profile and the consumption of methane in the redox zone (GD: 2.5 × 10–6 m2 s−1, LD: 1.6 × 10–5 m2 s−1). Our study identified vertical transport of methane from the deep-water body towards the redox zone as well as differing hydrographic conditions (lateral intrusions and vertical mixing) within the redox zone of these deeps as major factors that determine the pelagic methane oxidation.

Highlights

  • Methane is an atmospheric trace gas that influences the climate and the atmospheric chemistry (Wuebbles and Hayhoe, 2002)

  • For the Gotland Deep it is known that O2 and H2S can co-occur at the redox zone (Labrenz et al, 2010)

  • In this intermediate depth interval one potentially active type I methanotrophic bacterium was identified at both sampling sites, indicating that the different hydrographic conditions apparently do not impact the diversity of methanotrophic communities

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Summary

Introduction

Methane is an atmospheric trace gas that influences the climate and the atmospheric chemistry (Wuebbles and Hayhoe, 2002) It is generated in terrestrial, limnic and marine ecosystems by biotic (Segers, 1998; Reeburgh, 2007) and abiotic mechanisms (Berndt et al, 1996; Keir et al, 2008). Oxidation processes have been proven by oxygen, sulfate, nitrate, nitrite, iron and manganese, and in the water column only by sulfate and oxygen (Reeburgh, 2007; Beal et al, 2009; Ettwig et al, 2010) According to their carbon assimilation, which can either be performed by the ribulose monophosphate (RuMP) or serine pathway, the aerobic MOB are separated into the main groups type I and type II, respectively. The thermophilic MOB type X represent a subgroup of type I and are capable of fixing methane as well

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