Abstract

Abstract. The Arctic is a water-rich region, with freshwater systems covering about 16 % of the northern permafrost landscape. Permafrost thaw creates new freshwater ecosystems, while at the same time modifying the existing lakes, streams, and rivers that are impacted by thaw. Here, we describe the current state of knowledge regarding how permafrost thaw affects lentic (still) and lotic (moving) systems, exploring the effects of both thermokarst (thawing and collapse of ice-rich permafrost) and deepening of the active layer (the surface soil layer that thaws and refreezes each year). Within thermokarst, we further differentiate between the effects of thermokarst in lowland areas vs. that on hillslopes. For almost all of the processes that we explore, the effects of thaw vary regionally, and between lake and stream systems. Much of this regional variation is caused by differences in ground ice content, topography, soil type, and permafrost coverage. Together, these modifying factors determine (i) the degree to which permafrost thaw manifests as thermokarst, (ii) whether thermokarst leads to slumping or the formation of thermokarst lakes, and (iii) the manner in which constituent delivery to freshwater systems is altered by thaw. Differences in thaw-enabled constituent delivery can be considerable, with these modifying factors determining, for example, the balance between delivery of particulate vs. dissolved constituents, and inorganic vs. organic materials. Changes in the composition of thaw-impacted waters, coupled with changes in lake morphology, can strongly affect the physical and optical properties of thermokarst lakes. The ecology of thaw-impacted lakes and streams is also likely to change; these systems have unique microbiological communities, and show differences in respiration, primary production, and food web structure that are largely driven by differences in sediment, dissolved organic matter, and nutrient delivery. The degree to which thaw enables the delivery of dissolved vs. particulate organic matter, coupled with the composition of that organic matter and the morphology and stratification characteristics of recipient systems will play an important role in determining the balance between the release of organic matter as greenhouse gases (CO2 and CH4), its burial in sediments, and its loss downstream. The magnitude of thaw impacts on northern aquatic ecosystems is increasing, as is the prevalence of thaw-impacted lakes and streams. There is therefore an urgent need to quantify how permafrost thaw is affecting aquatic ecosystems across diverse Arctic landscapes, and the implications of this change for further climate warming.

Highlights

  • Permafrost is perennially frozen ground that underlies about a quarter of the landmass of the Northern Hemisphere (Brown et al, 1998)

  • Ground-ice content, topography, and soil type are the main drivers for both types of permafrost thaw and associated release of constituents into aquatic systems. (i) When thaw is manifested as a pulse disturbance, this leads to thermokarst lakes or slumping

  • The soil type of the thawed material generally determines the release and effect of constituents; thaw of organic carbon (OC)-rich soils will lead to higher OC export whereas thaw of mineral-rich soils will lead to lower OC export

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Summary

Introduction

Permafrost is perennially frozen ground that underlies about a quarter of the landmass of the Northern Hemisphere (Brown et al, 1998). Hillslope processes result in dramatic features such as retrogressive thaw slumps (Fig. 2b), active layer detachment slides, and thermal erosional gullies (Fig. 2c), which together we refer to as thermoerosional features (TEFs) The scale of these features is local and depends on landscape features, but the transport of sediment, nutrients, and organic matter into aquatic ecosystems can be large, and these features may form in a matter of hours and slowly grow for several years. While ground ice content and topography are important modifying factors that determine how permafrost thaw manifests itself within landscapes, factors such as the local composition of soils and regional extent of permafrost will play an important role in determining the effect of permafrost thaw on aquatic ecosystems (Fig. 3).

Physical and optical limnology
Chemical limnology and the transfer of materials from land to water
Sediment delivery to aquatic ecosystems
Organic matter delivery to aquatic ecosystems
Nutrient delivery to aquatic ecosystems
Delivery of major ions
Mobilization of contaminants
Overarching considerations
Pathways of degradation
Biodegradation of organic carbon
Photodegradation of organic carbon
Photochemical and microbial transformation of contaminants
Microbiology of thaw waters
Emission of CO2 and CH4 from permafrost-thaw-impacted systems
Scale and distribution of GHG measurements
Lake morphology and evolution
Release of old permafrost OC into aquatic systems
Release of old permafrost OC as greenhouse gases
Carbon burial in Arctic aquatic ecosystems
Carbon burial in yedoma thermokarst lakes
Ecosystem structure and function
Streams
Export to ocean
Broad-scale climatic effects
Summary
General future research directions
Research directions specific to streams and rivers
Research directions specific to thermokarst lakes
Findings
The use of specific techniques in future research
Full Text
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