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The long-term fate of permafrost peatlands under rapid climate warming

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Abstract

Permafrost peatlands contain globally important amounts of soil organic carbon, owing to cold conditions which suppress anaerobic decomposition. However, climate warming and permafrost thaw threaten the stability of this carbon store. The ultimate fate of permafrost peatlands and their carbon stores is unclear because of complex feedbacks between peat accumulation, hydrology and vegetation. Field monitoring campaigns only span the last few decades and therefore provide an incomplete picture of permafrost peatland response to recent rapid warming. Here we use a high-resolution palaeoecological approach to understand the longer-term response of peatlands in contrasting states of permafrost degradation to recent rapid warming. At all sites we identify a drying trend until the late-twentieth century; however, two sites subsequently experienced a rapid shift to wetter conditions as permafrost thawed in response to climatic warming, culminating in collapse of the peat domes. Commonalities between study sites lead us to propose a five-phase model for permafrost peatland response to climatic warming. This model suggests a shared ecohydrological trajectory towards a common end point: inundated Arctic fen. Although carbon accumulation is rapid in such sites, saturated soil conditions are likely to cause elevated methane emissions that have implications for climate-feedback mechanisms.

Introduction

Twenty-first century climatic warming is projected to be greatest in high-latitude areas of the Northern Hemisphere. IPCC AR5 climate models project that global mean surface temperatures are likely to increase by 0.3 °C to 4.8 °C by the end of the 21st century relative to 1986-2005, with a very high confidence that the Arctic region will warm more rapidly. Projected temperature increases over the Arctic land region have central estimates of 1.9 °C (RCP2.6), 3.9 °C (RCP4.5), 4.5 °C (RCP6.0) and 7.5 °C (RCP8.5)1. The implications for ecosystem structure and carbon budgets at high latitudes are likely to be of global importance through biosphere-climate feedbacks that have the potential to either accelerate or dampen the global warming effect2. Zones of permafrost have retreated rapidly poleward in recent decades, evidenced by the widespread development of degradation features such as thaw lakes3, increased active layer thickness4 and in some locations the complete disappearance of permafrost5,6.

Given their relatively small global areal extent, permafrost peatlands are disproportionately important to the future of global-scale ecosystem-climate feedbacks. Organic-rich permafrost peat stores approximately 277 Pg of carbon (C)7, equivalent to 14% of the global soil C store8. Until recently this huge soil C store has been rendered effectively inert, protected from decomposition by lethargic microbial activity in frozen soil conditions. The prospect of widespread permafrost thaw leaves this C store vulnerable to rapid decomposition, with a huge reciprocal global warming potential from increased fluxes of greenhouse carbon gases (GHGs) – chiefly CH4 from waterlogged soil conditions – to the atmosphere9. However, this global warming effect may be partially compensated or even outweighed entirely by increased CO2 sequestration through newly-invigorated ecosystem productivity and peat accumulation10.

Contemporary GHG flux rates from degrading permafrost peatlands, and their relationships to highly localised water-table and temperature measurements, have only been intensively monitored since the 1990s6. A dearth of palaeoecological studies into the response of permafrost peatlands to climatic change during the instrumental period (i.e., the last 100–150 years) leaves the future of degrading permafrost peatlands, and their likely feedbacks to the global climate system, highly unclear.

The Abisko region of northern Sweden (Supplementary material 1) is an area characterised by currently degrading permafrost peat11,12. Abisko has experienced rapid warming during the twentieth century13; mean annual air temperature exceeded the 0 °C threshold around AD 2000 leaving the region beyond the climatic envelope that can sustain permafrost. Climate model projections suggest continued marked temperature increases in the near future (Supplementary material 2). Active-layer deepening and increase in surface wetness through thawing of permafrost are both coincident with the sharp temperature rise in the last ~30 years (Fig. 1).

Figure 1
Figure 1

Recent changes in the Abisko region (a) deepening of the active layer since the 1980s (data from4,26). (b) Rapid shift to wetter conditions in an Arctic fen starting at ~1980 (this study, reconstructed using testate amoebae – see Fig. 2), blue line shows a locally-weighted scatterplot smoothing function; s.u. = standardised water table units25. (c) Annual maximum temperature from Abisko showing two distinct periods of warming in the twentieth century (see Supplementary material 1 and 2); the red line shows a locally-weighted scatterplot smoothing function.

Distinct forms of degraded permafrost peatlands can be identified in Abisko, despite similar climatic conditions across the region. These include partially collapsed palsas and peat plateaux, thermokarst lakes, and Arctic fens and bogs that no longer contain permafrost (Supplementary material 1). However, it is unclear whether these distinct forms represent divergent trajectories for degrading permafrost peatlands, or stages along a pathway towards a common end-point. The answer to this question has important implications for the future of permafrost peatlands and their global-scale ecosystem-climate feedbacks. Earlier research on permafrost peatlands suggested cyclical models of palsa development under steady climates14. Such an explanation for the distinct permafrost forms at our study area seems unlikely to hold given that the entire region has now surpassed the 0 °C threshold and continues to warm, making refreezing and development of new palsas all but impossible. We reconstruct the recent ecohydrological and carbon dynamics of currently degrading Abisko peatlands to assess the likely future trajectories of Northern Hemisphere permafrost peat in response to future warming in the arctic and subarctic.

We analysed peat cores from i) a desiccating permafrost bog; ii) an area of peatland that has recently collapsed due to permafrost degradation; and iii) an Arctic fen, currently devoid of permafrost (Supplementary material 1, 3-7). All three of our study sites have become drier over the last century (Figs 2 and 3). However, two sites (the collapsed peatland and Arctic fen) show a subsequent abrupt shift to wetter conditions. In the Arctic fen this wet shift tracks the temperature increase of the latter twentieth century (Fig. 1), whereas the collapsed peatland is influenced by water-table fluctuations in the surrounding fen. The desiccating bog exhibits a strong drying trend and has not undergone any rapid shift to wetter conditions.

Figure 2: Peat property and testate amoeba data from the three study sites.
Figure 2

Chronological determinations are from the age models are shown (see Supplementary material 7). Standardised water-table reconstructions are illustrated (see Supplementary material 5).

Figure 3
Figure 3

(ac) Standardised water-table reconstructions based on testate amoeba analysis from the three study sites. All sites show a marked drying trend until the latter twentieth century; however, the collapsed peatland and Arctic fen show a subsequent rapid shift to wetness. Linear regression statistics for the drying trends in each site are shown. (df) Annotated carbon accumulation data from the three sites.

Although the number of observations is limited, correlation analysis (Supplementary material 8) illustrates that in the case of the permafrost-free Arctic fen there are significant negative correlations between temperature data for several months throughout the year and reconstructed water-table depth. This indicates the site has become wetter due to thawing permafrost elsewhere in the catchment. The water-table depth reconstruction from the collapsed peatland is largely uncorrelated with instrumental temperature variables providing further evidence that the site has now passed a threshold beyond which its hydrology is controlled by autogenic mechanisms rather than climate. The desiccating bog is strongly linked to climate, where water-table depth exhibits positive correlations with temperature for several months of the year. This site has become drier due to temperature-driven increases in evapotranspiration.

Despite some similarities in hydrology, the three sites exhibit contrasting carbon accumulation (CA) regimes. CA rates are typically much higher in the upper peat profile in most peatland systems because full decomposition has yet to take place; however, the substantial differences in CA regime between the three sites here indicate a change in CA dynamics through time. In the desiccating bog CA has remained extremely low due to large decomposition lossescf.15. The collapsed peatland has a very high CA, seemingly prompted by early twentieth century warming; since the collapse, CA rates have become mostly disconnected from climate and exhibit variable temporal behaviour which we interpret as allogenic (climate) and autogenic (internal feedbacks) controls competing for dominance. In the Arctic fen CA has increased sharply in recent years, likely due to increased productivity from higher temperatures16 and reduced decomposition in anoxic, saturated peat.

We propose five distinct phases along a trajectory of degradation for permafrost peatlands (Fig. 4). We contend that genuinely pristine permafrost peatlands (Phase 1) are no longer present in our study region because mean annual temperature has been above 0 °C for more than a decade. The second stage (Phase 2; desiccating) is characterised by drying of surficial peat due to higher temperatures, leading to greater evapotranspirative losses, desiccation of the peat surface, slow lowering of the water table and high levels of decomposition. The system is driven by allogenic climatic forcing in Phase 2. Phase 3 represents a threshold of rapid change: continued drying leads to peat shrinkage and the peat surface begins to crack (very commonly observed in the field – Fig. 4, Phase 3 photo), increasing thermal connectivity between the atmosphere and what remains of the permafrost. The result is a collapsed peatland (Phase 4) due to runaway degradation of permafrost, causing rapid collapse of the peatland and saturation with thaw water. In the final stage (Phase 5; Arctic fen) the peatland is devoid of permafrost; it is now influenced by surface and groundwater flow into the system from adjacent areas and local hydrochemistry17. This final stage has the potential for large carbon sequestration through newly invigorated productivity and rapid peat accumulation (Fig. 3f); however, elevated methane fluxes also seem likely owing to saturated soils9,18,19.

Figure 4: Five phase model for degrading permafrost peatlands in response to increasing temperature.
Figure 4

Each column corresponds to one of five distinct phases, identified in the top row. Symbols in the conceptual model represent the following hydrological fluxes: R = runoff; D = shallow drainage; P = precipitation; ET = evapotranspiration; I = infiltration. The bottom row illustrates ecohydrological stability of the system using a ball-and-cup analogy27. The first phase (‘intact’) represents the only stable basin of attraction before climate-driven change alters the system state.

Although autogenic mechanisms have dominated ecosystem dynamics during certain periods of permafrost degradation, persistent warming has eventually forced inevitable collapse, followed by re-invigorated productivity and peat accumulation. This is in contrast to commonly held concerns about catastrophic loss of the peatland C stock under future climate change20. The temporal limit of ongoing monitoring campaigns provides only a partial record of the response of permafrost peatlands to recent warming. Palaeoecological studies such as ours and investigations of longer-term changes during the Holocene provide important baseline information over longer timescales that allows a fuller understanding of the fate of degrading permafrost peatlands.

Methods

We identified three different peatlands in the Abisko region in different states of permafrost decay, despite being subject to the same climate: 1) desiccating bog albeit with largely intact permafrost; 2) recently thawed and partially collapsed area of peatland surrounded by fen; and 3) Arctic fen with no current permafrost and abundant thaw pools (Supplementary material 3 and 4). We collected peat cores from the Arctic fen and desiccating bog using a Russian corer21. Refer to12 for information on sampling of the collapsed peatland. In the laboratory we carried out bulk density and loss-on-ignition analyses following standard methods22. Carbon accumulation was calculated following23. We analysed testate amoebae in each core following24 (Fig. 2), and the transfer function of17 was used for water-table depth reconstruction. Water-table depth data were standardised following25. The chronology of each core was based on 210Pb, AMS radiocarbon, spheroidal carbonaceous particles and tephrochronology (Supplementary material 6) and age-depth models were constructed using linear interpolation between dates (Supplementary material 7). We compiled available data on active layer thickness and instrumental climate data to compare with the peat-based data. For more detailed information on methods refer to Supplementary material 5.

Additional Information

How to cite this article: Swindles, G. T. et al. The long-term fate of permafrost peatlands under rapid climate warming. Sci. Rep. 5, 17951; doi: 10.1038/srep17951 (2015).

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Acknowledgements

We acknowledge the Worldwide University Network (WUN) for funding this project (Project: Arctic Environments, Vulnerabilities and Opportunities). We acknowledge NERC Training Grants NE/G52398X/1 to EW and NE/G52398X/1 to ET. An undergraduate student, Rachel Wiley, was funded by a Royal Geographical Society Fieldwork Apprenticeship and is thanked for her assistance in the field and laboratory. The School of Geography, University of Leeds is thanked for additional funding for ‘Enhancing the Student Experience’. The River Basins Processes and Management and Ecology and Global Change research clusters at the University of Leeds are thanked for funding helicopter time. We acknowledge the Abisko Scientific Research Station for assistance with field logistics and Kallax Flyg AB for helicopter support. We thank Andy Baird for useful discussions on peatland hydrology.

Author information

Affiliations

  1. water@leeds, School of Geography, University of Leeds, LS2 9JT, United Kingdom

    • Graeme T. Swindles
    • , Paul J. Morris
    • , Elizabeth J. Watson
    • , T. Edward Turner
    • , Jonathan L. Carrivick
    • , Clare Woulds
    •  & Joseph Holden
  2. School of Geography, Archaeology and Palaeoecology, Queen’s University Belfast, BT7 1NN, United Kingdom

    • Donal Mullan
  3. Geography, College of Life and Environmental Sciences, University of Exeter, EX4 4RJ, United Kingdom

    • Thomas P. Roland
    • , Matthew J. Amesbury
    • , Angela Gallego-Sala
    • , Dan J. Charman
    •  & Nicole Sanderson
  4. Department of Geosciences and Natural Resource Management, Center for Permafrost (CENPERM), University of Copenhagen, DK-1350, Denmark

    • Ulla Kokfelt
  5. Geological Survey of Sweden, Uppsala, Sweden

    • Kristian Schoning
  6. Département de Géographie and GEOTOP, Université du Québec à Montréal, Montréal, Québec, Canada

    • Steve Pratte
    •  & Michelle Garneau
  7. School of Interdisciplinary Studies, Dumfries Campus, University of Glasgow, Rutherford/McCowan Building, Crichton, Dumfries, DG1 4ZL, United Kingdom

    • Lauren Parry
  8. Natural Resources Canada/Ressources naturelles Canada, Geological Survey of Canada/Commission géologique du Canada, Calgary, Alberta, T2L 2A7, Canada

    • Jennifer M. Galloway

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Contributions

G.T.S. conceived the project, led the fieldwork, laboratory work and statistical analyses; P.J.M. and G.T.S. interpreted the data, developed the conceptual model of permafrost peatland degradation and wrote the manuscript; D.M. provided climate information and carried out statistical analysis; E.W., T.E.T., T.R. and M.A. carried out laboratory analysis; U.K. and K.S. provided data; S.P., A.G.-S., D.C., N.S. and M.G. assisted with core chronologies; J.C. and C.W. and J.C. helped run the field campaign; J.H., L.P. and J.M.G. helped with data interpretation and improvement of the manuscript. All authors contributed to manuscript development.

Competing interests

The authors declare no competing financial interests.

Corresponding author

Correspondence to Graeme T. Swindles.

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