Abstract

Abstract. The large stocks of soil organic carbon (SOC) in soils and deposits of the northern permafrost region are sensitive to global warming and permafrost thawing. The potential release of this carbon (C) as greenhouse gases to the atmosphere does not only depend on the total quantity of soil organic matter (SOM) affected by warming and thawing, but it also depends on its lability (i.e., the rate at which it will decay). In this study we develop a simple and robust classification scheme of SOM lability for the main types of soils and deposits in the northern permafrost region. The classification is based on widely available soil geochemical parameters and landscape unit classes, which makes it useful for upscaling to the entire northern permafrost region. We have analyzed the relationship between C content and C-CO2 production rates of soil samples in two different types of laboratory incubation experiments. In one experiment, ca. 240 soil samples from four study areas were incubated using the same protocol (at 5 ∘C, aerobically) over a period of 1 year. Here we present C release rates measured on day 343 of incubation. These long-term results are compared to those obtained from short-term incubations of ca. 1000 samples (at 12 ∘C, aerobically) from an additional three study areas. In these experiments, C-CO2 production rates were measured over the first 4 d of incubation. We have focused our analyses on the relationship between C-CO2 production per gram dry weight per day (µgC-CO2 gdw−1 d−1) and C content (%C of dry weight) in the samples, but we show that relationships are consistent when using C ∕ N ratios or different production units such as µgC per gram soil C per day (µgC-CO2 gC−1 d−1) or per cm3 of soil per day (µgC-CO2 cm−3 d−1). C content of the samples is positively correlated to C-CO2 production rates but explains less than 50 % of the observed variability when the full datasets are considered. A partitioning of the data into landscape units greatly reduces variance and provides consistent results between incubation experiments. These results indicate that relative SOM lability decreases in the order of Late Holocene eolian deposits to alluvial deposits and mineral soils (including peaty wetlands) to Pleistocene yedoma deposits to C-enriched pockets in cryoturbated soils to peat deposits. Thus, three of the most important SOC storage classes in the northern permafrost region (yedoma, cryoturbated soils and peatlands) show low relative SOM lability. Previous research has suggested that SOM in these pools is relatively undecomposed, and the reasons for the observed low rates of decomposition in our experiments need urgent attention if we want to better constrain the magnitude of the thawing permafrost carbon feedback on global warming.

Highlights

  • Permafrost has been recognized as one of the vulnerable carbon (C) pools in the Earth system (Gruber et al, 2004)

  • In recent studies dealing with the incubation of soil samples from the northern permafrost region, %C and C/N of soil samples were highlighted as the best parameters to predict C release (Elberling et al, 2013; Schädel et al, 2014)

  • The PAGE21 and CryoCarb incubation experiments confirm results from previous studies that simple geochemical parameters such as dry bulk density (DBD), %C and C / N can provide a good indication of soil organic matter (SOM) lability in soils and deposits of the northern permafrost region (Elberling et al, 2013; Schädel et al, 2014; Faucherre et al, 2018)

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Summary

Introduction

Permafrost has been recognized as one of the vulnerable carbon (C) pools in the Earth system (Gruber et al, 2004). In the last decade there has been a surge in papers dealing with the permafrost carbon feedback on climate change (e.g., Schuur et al, 2008; Kuhry et al, 2010) This increased interest was fueled by a new and high estimate of the total soil organic carbon (SOC) storage in the northern permafrost region (Tarnocai et al, 2009), which was received with great interest by the Earth system science community (e.g., Ciais, 2009). Recent studies have focused on reevaluating the spatial extent and SOC storage of the Yedoma “Ice Complex” and alas deposits (Strauss et al, 2013; WalterAnthony et al, 2014; Hugelius et al, 2016; Shmelev et al, 2017)

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