Permafrost Peatlands Approaching Tipping Point

  • In 2024, permafrost temperatures reached their highest ever recorded levels at nine out of twenty long-term monitoring stations across Alaska, confirming what climate scientists have warned for years: permafrost peatlands are approaching a tipping point with consequences that extend far beyond the Arctic.
  • These frozen landscapes store up to 185 billion tonnes of carbon โ€” nearly half of all soil organic carbon held in northern hemisphere peatlands โ€” and are now destabilizing faster than most climate models predicted.
  • A University of Leeds study published in Nature Climate Change found that even under the most aggressive global emissions-reduction scenarios, the climates of Northern Europe will no longer be cold enough to sustain peat permafrost by 2040.
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Permafrost peatlands are among the most important yet vulnerable ecosystems on Earth. Found across Arctic and sub-Arctic regions, these frozen wetlands have stored enormous amounts of carbon for thousands of years, helping regulate the planetโ€™s climate. However, rising global temperatures are rapidly thawing permafrost layers, pushing many peatlands toward a dangerous ecological tipping point.

Why Permafrost Peatlands Are at Center of Climate Emergency

The term permafrost peatlands (ground that has stayed frozen for at least two consecutive years, covered by deep layers of partially decomposed organic plant material called peat) might sound like a remote scientific concern. It is not. These ecosystems function as the planetโ€™s largest natural carbon vault, and they are being unlocked by rising temperatures at a rate that threatens to amplify global warming far beyond what human emissions alone would cause.

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Scientists now speak openly about a tipping point โ€” a threshold beyond which the thaw becomes self-reinforcing and irreversible โ€” and recent data places us uncomfortably close to it. Permafrost peatlands approaching tipping point is not a hypothetical future scenario.

In 2024, NOAAโ€™s Arctic Report Card confirmed that the Arctic tundra region has shifted from being a net carbon sink โ€” absorbing more carbon than it releases โ€” to a net carbon source for the first time in recorded history.

For crop farmers, that shift matters because it directly accelerates the very warming that disrupts growing seasons, intensifies droughts, and raises the cost of agricultural production worldwide. Understanding this system is the first step toward demanding the policy responses that could still prevent the worst outcomes.

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What Are Permafrost Peatlands?

Peatlands (wetland ecosystems where waterlogged, oxygen-poor conditions slow the decomposition of dead plant material, allowing it to accumulate over centuries) cover roughly 3 percent of Earthโ€™s land surface but hold a disproportionate share of its terrestrial carbon.

When peatlands exist in regions cold enough to keep the ground permanently frozen, they become permafrost peatlands, and the stakes increase enormously. The frozen ground acts like a biological deep-freeze, preserving organic carbon that would otherwise decompose and return to the atmosphere.

Regular peatlands, like the bog systems of Ireland or the lowland fens of the UK, store large amounts of carbon but are not frozen. Permafrost peatlands are different because the frozen layer below the active surface prevents microbial decomposition of the accumulated carbon. This is why their degradation produces greenhouse gas emissions orders of magnitude greater than degradation of non-frozen peatlands.

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Geographic Distribution of Permafrost Peatlands: Permafrost peatlands are concentrated in the high latitudes of the Northern Hemisphere, spanning several major regions:

1. Siberia and Western Russia host the largest single block of permafrost peatlands on Earth, with the West Siberian Lowland alone containing an estimated 13.9 billion metric tons of peat carbon. This region is particularly vulnerable because its permafrost sits at temperatures close to the freezing threshold, meaning small temperature increases can push it over the edge.

2. Northern Canada and Alaska contain vast tracts of palsas and peat plateaus โ€” small elevated mounds of frozen peat that are already collapsing at observable rates. A 2025 study published in the Journal of Geophysical Research: Earth Surface projected that permafrost would disappear at all nine study sites along coastal Labrador by 2100, with some sites losing it as early as 2036.

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3. Scandinavia and Northern Europe, including Sweden, Finland, and Norway, contain comparatively smaller but scientifically well-monitored permafrost peatlands. The University of Leeds research found these areas to be the most immediately at risk, with climate suitability for peat permafrost projected to disappear by 2040.

How Permafrost Peatlands Form

Formation occurs over thousands of years through an extraordinarily slow process. Waterlogged, cold conditions prevent the full decomposition of dead plant matter โ€” mosses, sedges, and shrubs โ€” which instead compact into progressively thicker layers of peat. Over millennia, this peat accumulates at a rate of roughly one millimeter per year.

The result is peatlands that can be several meters thick, each layer representing centuries of accumulated biological carbon. Freezing transforms this deep, wet peat into a structurally stable frozen mass that locks away the stored carbon as effectively as a sealed container.

The Immense Importance of Permafrost Peatlands to Global Systems

The ecological and climatic functions of permafrost peatlands extend well beyond carbon storage. They regulate regional water cycles, support unique biodiversity, and provide essential resources to millions of people in Arctic and sub-Arctic communities. Losing them would set off a chain of consequences that reach every inhabited continent.

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On the carbon storage question, the numbers demand attention. Arctic permafrost soils hold an estimated 1,100 to 1,700 billion metric tons of carbon, roughly twice the amount currently in the atmosphere.

Permafrost peatlands specifically account for nearly half of the soil organic carbon held in northern hemisphere peatlands โ€” approximately 185 billion tonnes according to Carbon Briefโ€™s analysis of the Nature Climate Change literature. For comparison, total global fossil fuel emissions in 2023 were approximately 37 billion tonnes of COโ‚‚. The scale of what is locked in permafrost peatlands puts every other climate variable in perspective.

  • Water regulation: Permafrost acts as a hydraulic barrier, keeping surface water from draining into the ground. When it thaws, water tables shift dramatically โ€” some areas flood while others dry out โ€” disrupting river systems and groundwater supplies that communities and agricultural areas downstream depend on.
  • Biodiversity support: These ecosystems host rare and specialist species of plants, insects, birds, and mammals adapted to cold, nutrient-poor conditions. Many of these species have no alternative habitat if the ecosystem transforms.
  • Indigenous community resources: For Indigenous peoples across the Arctic โ€” including Inuit, Sami, and Nenets communities โ€” permafrost peatlands form the literal ground beneath traditional infrastructure, hunting routes, and cultural landscapes. Thaw-induced ground subsidence is already collapsing buildings and roads in these communities.

Understanding the Tipping Point in Permafrost Peatland Systems

An ecological tipping point (a threshold beyond which a system undergoes rapid, self-reinforcing change that cannot easily be reversed even if the original pressure is removed) is the concept at the heart of current scientific concern. Not all environmental change works this way. Some systems degrade gradually and can recover when conditions improve. Permafrost peatlands, once they pass their tipping point, do not work this way.

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The mechanism is a feedback loop. As warming thaws the frozen peat, microbial decomposition accelerates, releasing carbon dioxide and methane. These greenhouse gases warm the atmosphere further.ย  That additional warming thaws more permafrost, which releases more carbon, which warms the climate more. Once this loop gains momentum, removing the original human-caused warming pressure no longer stops it. The system drives itself.

Fewster et al. (2022, Nature Climate Change, University of Leeds) found that by 2040, the climates of Northern Europe will no longer be cold enough to sustain peat permafrost even under the most aggressive emissions-reduction scenario.

This means that for Northern European permafrost peatlands, some degree of tipping is now locked in regardless of near-term policy action โ€” making conservation of remaining intact systems in Siberia and Canada all the more critical.

The difference between gradual change and abrupt collapse matters enormously for planning. A gradual thaw over two centuries would be serious but potentially manageable within the context of broader climate action.

An abrupt collapse โ€” triggered when permafrost temperatures cross from minus one to zero degrees Celsius over a single decade โ€” releases the same carbon far more rapidly, overwhelming the atmosphereโ€™s capacity to absorb it and dramatically accelerating global warming in a compressed timeframe. Current evidence increasingly suggests that some regions are on an abrupt rather than gradual trajectory.

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The Main Causes Driving Permafrost Peatland Degradation

1. Climate Change and Rising Arctic Temperatures

The Arctic is warming approximately four times faster than the global average, a phenomenon documented consistently across NOAAโ€™s Arctic Report Card series. This amplified warming results from the Arctic amplification effect (a feedback where melting snow and ice expose darker ocean and land surfaces that absorb more solar energy, accelerating local warming).

For permafrost peatlands, this means they face temperature increases far steeper than the global average suggests, and their thermal threshold is being reached decades earlier than mid-latitude systems.

Heatwaves are also extending the thaw season. In recent years, prolonged summer warming events in Siberia and Canada have thawed the active surface layer more deeply than seasonal norms allow it to refreeze in winter. Over successive years, this ratchet effect pushes the permafrost table progressively deeper.

2. Permafrost Thaw and Thermokarst Formation

Thermokarst (ground subsidence and the formation of uneven, collapsed terrain caused by the melting of ice-rich permafrost) is one of the most visible signs of peatland degradation. When the frozen ground beneath peat melts, the surface loses structural support and collapses inward, forming depressions, ponds, and drainage channels.

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These water-filled thermokarst features then absorb more solar radiation than the original frozen surface, accelerating local warming and deepening the thaw. The process is self-amplifying at a landscape scale.

3. Wildfires: An Accelerating Threat

Circumpolar wildfire emissions have averaged 207 teragrams of carbon per year since 2003, the equivalent of emissions from 200 coal-fired power plants burning continuously. When peatlands burn, they do not just release surface carbon โ€” fires can burn deep into the peat body itself, releasing carbon that took centuries to accumulate in a matter of days. 2024 was the second-highest year on record for wildfire emissions north of the Arctic Circle.

4. Human Activities and Land Disturbance

Industrial activity compounds natural warming pressures. Oil and gas extraction in Arctic Russia and Canada requires roads, pipelines, and drilling platforms built directly on permafrost. Infrastructure development compresses and heats the ground surface, triggering localized thaw that spreads outward. Deforestation in boreal zones adjacent to peatlands removes shade and windbreaks, increasing surface temperatures and altering the moisture balance that peat systems depend on for stability.

Carbon Release and the Greenhouse Gas Feedback Problem

When permafrost peat thaws under aerobic (oxygenated) conditions โ€” such as in drained or dry landscapes โ€” microbes decompose the organic carbon into carbon dioxide. When thaw occurs under anaerobic (oxygen-poor) waterlogged conditions, the same organic matter is converted into methane.

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Methane is far more concerning in the short term: over a 20-year timescale, it warms the atmosphere approximately 100 times more potently than COโ‚‚ per unit of mass. Hugelius et al. found that the permafrost region is currently a weak COโ‚‚ sink but a significant CHโ‚„ and Nโ‚‚O source, with the net greenhouse gas balance tipping toward a warming contribution when all gases are calculated together in COโ‚‚-equivalent terms.

For climate modelers and policymakers, this confirms that accounting for methane and nitrous oxide from permafrost โ€” not just COโ‚‚ โ€” is essential for accurate climate projections and carbon budget calculations. The feedback loop structure is what makes this crisis qualitatively different from most other emission sources. Industrial emissions can be reduced through policy and technology choices.

Permafrost carbon feedback, once triggered at scale, operates independently of human decision-making. Research from the Permafrost Carbon Network, published in Annual Reviews, estimates that permafrost thaw could release between 12 and 174 billion tonnes of COโ‚‚-equivalent by 2100, potentially consuming up to 25 percent of the remaining carbon budget for limiting global warming to 1.5ยฐC above pre-industrial levels.

To put this in comparative terms: total annual global human greenhouse gas emissions in 2023 were approximately 54 billion tonnes of COโ‚‚-equivalent. Even the low-end estimate for cumulative permafrost emissions by 2100 represents more than one full year of global human emissions added to the atmosphere beyond what models account for.

Ecological Consequences of Permafrost Peatland Degradation

The transformation of permafrost peatlands produces ecological changes that cascade across entire landscapes. When ground ice melts, surface topography shifts dramatically โ€” stable flat terrain becomes a mosaic of collapsed hollows, temporary ponds, and drained channels.

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Vegetation communities adapted to cold, stable, waterlogged conditions are replaced by either open water or drier shrub communities, depending on local drainage patterns.

Arctic wildlife that depends on stable permafrost terrain โ€” caribou, reindeer, Arctic foxes, lemmings, and specialist shorebirds โ€” loses forage habitat and faces disrupted migration routes. Aquatic food webs in thermokarst ponds differ fundamentally from those in the intact peatland they replaced, supporting fewer of the species that northern predators and Indigenous hunters rely on.

At the microbial level, thaw dramatically increases the activity of methanogenic archaea (methane-producing microorganisms that thrive in anaerobic waterlogged conditions), shifting the ecosystem from a carbon store to a methane emitter in a way that is difficult to reverse once established. This microbial shift is the biological engine of the carbon feedback loop described above.

Global Climate Impacts: Beyond the Arctic

The consequences of permafrost peatlands approaching their tipping point do not stay in the Arctic. The carbon and methane released enter the global atmosphere, driving temperature increases in every region. For crop farmers in South Asia, sub-Saharan Africa, and Central America, this translates into more frequent and severe heatwaves, disrupted monsoon patterns, and increased drought risk โ€” precisely the conditions that destroy harvests and threaten food security.

The carbon stored in Arctic permafrost peatlands represents a climate risk that no amount of renewable energy deployment can offset if it is released rapidly โ€” the only solution is to prevent the thaw from happening in the first place.

Current climate models used for IPCC projections have historically underrepresented permafrost carbon feedback, partly because peatland permafrost behaves differently from mineral-soil permafrost due to the insulating properties of organic soils.

As Dr. Ruza Ivanovic of the University of Leeds noted in the Nature Climate Change study, peatlands remain poorly represented in Earth system models, meaning real-world warming may outpace model projections. Sea level rise, driven partly by melting Arctic ice accelerated by permafrost feedback warming, will also threaten coastal agricultural areas and river deltas that produce large shares of the worldโ€™s food.

Scientific Research and Monitoring

Tracking permafrost peatland change requires a combination of satellite remote sensing, ground-based monitoring, and climate modeling. The European Space Agencyโ€™s Copernicus programme and NASAโ€™s ABoVE (Arctic Boreal Vulnerability Experiment) mission use airborne and satellite sensors to measure surface temperature, land cover change, and methane plume distribution at continental scales.

Satellite systems scheduled to become operational by 2025 will provide higher-frequency data than previously available, allowing scientists to detect thermokarst formation and thaw-front advance in near-real time.

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Field studies conducted at long-term monitoring sites in Alaska, northern Canada, and Scandinavia provide the ground-truth data that calibrate satellite observations. NOAAโ€™s network of permafrost temperature boreholes across Alaska has documented a consistent warming trend over four decades, with 2024 recording the highest average borehole temperatures ever measured at the majority of stations.

These field measurements are also used to validate and improve the process-based models that simulate permafrost carbon dynamics under different climate scenarios. Major research programs driving this science forward include:

  • The Permafrost Carbon Network, an international consortium coordinating synthesis science across more than 100 research sites worldwide, which has produced several of the most comprehensive estimates of permafrost carbon stocks and future emissions.
  • The PAGE21 and Nunataryuk projects, funded by the European Union, which specifically focus on permafrost carbon-climate interactions and the human dimensions of permafrost thaw.
  • Northern Arizona Universityโ€™s permafrost modeling group, which published one of the most detailed projections of cumulative permafrost emissions through 2100 using region-based models.

One of the key challenges in predicting tipping timelines is the spatial heterogeneity of permafrost systems. A landscape that appears uniformly frozen from satellite imagery may contain warm, near-thaw patches at depth that will reach the threshold years before the average surface temperature suggests. This means that tipping may occur locally before global averages indicate it is happening.

Can the Permafrost Peatland Tipping Point Be Prevented?

1. Emission Reductions and the Paris Agreement

The most direct lever available is reducing the greenhouse gas emissions that drive Arctic warming. The Paris Agreementโ€™s target of limiting warming to 1.5ยฐC above pre-industrial levels is directly relevant: research shows that strong mitigation action could preserve suitable climate conditions for permafrost peatlands in northern parts of Western Siberia into the 2090s, and even allow new peatland formation after peak warming.

Under high-emission scenarios, by contrast, suitable permafrost peatland climates disappear across all of Europe and large parts of Siberia within this century. The window for meaningful action is narrow. The University of Leeds research confirms that Northern European permafrost peatlands will cross their tipping point by 2040 regardless of what happens to emissions โ€” that transition is already committed. The question now is whether Siberian and Canadian peatlands, which contain the vast majority of the carbon, can be preserved.

2. Conservation Strategies for Intact Peatlands

Where permafrost peatlands remain intact, preventing industrial disturbance is the most cost-effective conservation measure available. Every road, pipeline, and drilling platform built on permafrost creates a zone of localized thaw that can spread laterally for years after construction. Policies that redirect oil and gas development away from permafrost-rich zones and establish large-scale protected areas would prevent the most direct forms of anthropogenic disturbance.

3. Restoration Through Rewetting and Fire Management

Rewetting (the practice of blocking drainage channels and restoring high water tables to degraded peatlands) can slow microbial decomposition and in some cases allow peat to begin accumulating again. In non-permafrost contexts, rewetting has demonstrated significant reductions in COโ‚‚ emissions from degraded peatlands.

For permafrost peatlands, the principle is similar but complicated by the fact that refreezing the active layer requires cold enough temperatures that may no longer prevail in many regions.

Fire management โ€” including prescribed burns to reduce fuel loads, rapid fire-suppression responses in peatland areas, and post-fire monitoring โ€” can limit the contribution of wildfires to permafrost carbon loss. Given that 2024 was the second-highest year on record for wildfire emissions north of the Arctic Circle, scaling fire management capacity in Arctic and boreal regions represents an urgent practical priority.

Policy and International Responses to the Permafrost Peatland Crisis

Permafrost peatlands occupy a gap in international climate policy. Most carbon accounting frameworks, including the national inventory systems used under the UNFCCC, do not adequately account for permafrost carbon feedback, meaning that national emissions targets โ€” however ambitious โ€” systematically underestimate the carbon that will enter the atmosphere from thawing peatlands. Several important policy developments are emerging to address this gap:

  • The Global Peatlands Initiative, launched under the UN Environment Programme, provides a platform for coordinating international peatland conservation and restoration funding and has begun integrating permafrost peatland science into its framework.
  • Arctic Council working groups, including the Arctic Monitoring and Assessment Programme (AMAP), publish regular assessments of permafrost status and provide scientific input to Arctic-state governments on permafrost-related risks.
  • Indigenous-led conservation in northern Canada, Alaska, and Siberia offers some of the most effective on-the-ground protection for intact permafrost peatlands. Indigenous communities with legally recognized land rights have demonstrated the capacity to prevent industrial incursion and implement land management practices consistent with peatland preservation.

Funding remains a major constraint. The scientific monitoring networks, restoration programs, and fire management operations needed to respond adequately to permafrost peatland degradation are chronically underfunded relative to the scale of the carbon risk they are managing.

Best-Case and Worst-Case Scenarios for Permafrost Peatlands

Under the best-case scenario โ€” aggressive global emissions reductions aligned with or exceeding Paris Agreement commitments โ€” the most carbon-rich permafrost peatlands in northern Siberia and Canada could remain stable through much of this century.

Some Northern European peatlands will still cross their tipping point by 2040, as this is now unavoidable, but the total carbon release would be limited to the lower end of the 12 to 174 billion tonne range projected by the Permafrost Carbon Network.

Under the worst-case scenario โ€” continued high emissions through mid-century โ€” permafrost peatlands across Europe, western Siberia, Alaska, and large parts of Canada cross their tipping points in rapid succession. The self-reinforcing feedback loop takes over, and cumulative carbon release through 2100 approaches the upper end of projections, adding a warming increment to the global temperature trajectory that no subsequent human action can undo for centuries.

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Scientific uncertainty remains significant, and it cuts in both directions. Models may be underestimating resilience in some peatland systems. They may also be underestimating the speed of abrupt thaw events like thermokarst expansion and retrogressive thaw slumps, which can release decades worth of gradual thaw in a single summer.

The 2025 Nature Communications study on permafrost tipping points triggered by loss of old carbon adds further evidence that abrupt transitions are more likely than gradual models suggest.

What is not uncertain is the direction of travel. Every year of high emissions narrows the window for preserving permafrost peatland stability and increases the probability of crossing irreversible thresholds. Immediate action โ€” on emissions, conservation, and monitoring โ€” is not precautionary. It is the rational response to the best available evidence.

Why Permafrost Peatlands Demand Our Immediate Attention

Permafrost peatlands approaching their tipping point represent one of the most consequential and least publicly understood climate risks of our time. These frozen systems have stored carbon accumulated over thousands of years, regulated Arctic hydrology, and supported unique ecosystems and human communities. Their destabilization is not a distant future event โ€” it is documented, measurable, and already underway.

For crop farmers and agronomists, the relevance is direct: accelerated permafrost thaw feeds back into the global temperature trajectory that determines growing season length, precipitation patterns, and extreme weather frequency in every agricultural region on Earth.

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For agricultural researchers and agri-tech consultants, understanding carbon feedback from permafrost peatlands is essential context for any serious work on climate-smart agriculture and carbon markets. For policymakers, the gap between current permafrost accounting in national emissions inventories and the actual carbon risk locked in these systems demands urgent correction.

The science is clear that strong and immediate emissions reductions โ€” combined with active peatland conservation and restoration โ€” can still preserve the largest and most carbon-rich permafrost peatlands from crossing their tipping points. The window for that action is narrowing, but it has not yet closed. What happens in the next decade to the permafrost peatlands of Siberia, Canada, and Alaska will shape the climate of the next century for everyone on Earth.

References:

1. Nitzbon, J., Schneider von Deimling, T., Aliyeva, M., Chadburn, S. E., Grosse, G., Laboor, S., โ€ฆ & Langer, M. (2024). No respite from permafrost-thaw impacts in the absence of a global tipping point. Nature Climate Change, 14(6), 573-585.

2. Brovkin, V., Bartsch, A., Hugelius, G., Calamita, E., Lever, J. J., Goo, E., โ€ฆ & de Vrese, P. (2025). Permafrost and freshwater systems in the Arctic as tipping elements of the climate system. Surveys in geophysics, 46(2), 303-326.

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3. Devoie, ร‰. G., Craig, J. R., Connon, R. F., & Quinton, W. L. (2019). Taliks: A tipping point in discontinuous permafrost degradation in peatlands. Water Resources Research, 55(11), 9838-9857.

4. Hessen, D. O., Andersen, T., Armstrong McKay, D., Kosten, S., Meerhoff, M., Pickard, A., & Spears, B. (2023). Lake ecosystem tipping points and climate feedbacks. Earth System Dynamics Discussions, 2023, 1-34.

5. van der Velde, Y., Temme, A. J., Nijp, J. J., Braakhekke, M. C., van Voorn, G. A., Dekker, S. C., โ€ฆ & Teuling, A. J. (2021). Emerging forestโ€“peatland bistability and resilience of European peatland carbon stores. Proceedings of the National Academy of Sciences, 118(38), e2101742118.

6. Wang, Y., & Way, R. G. (2025). Future trajectories of peatland permafrost under climate and ecosystem change in northeastern Canada. Journal of Geophysical Research: Earth Surface, 130(2), e2024JF007930.

7. Page, S. E., & Baird, A. J. (2016). Peatlands and global change: response and resilience. Annual review of environment and resources, 41(1), 35-57.

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8. Gibson, C., Cottenie, K., Gingras-Hill, T., Kokelj, S. V., Baltzer, J. L., Chasmer, L., & Turetsky, M. R. (2021). Mapping and understanding the vulnerability of northern peatlands to permafrost thaw at scales relevant to community adaptation planning. Environmental Research Letters, 16(5), 055022.

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