EGU24-16607, updated on 02 Apr 2024
https://doi.org/10.5194/egusphere-egu24-16607
EGU General Assembly 2024
© Author(s) 2024. This work is distributed under
the Creative Commons Attribution 4.0 License.

Long-term soil redox dynamics of intact and degraded permafrost in Interior Alaska

Patrick Liebmann1, Cordula Vogel2, Jiri Barta3,4, Tim Urich5, Alexander Kholodov6, Milan Varsadiya7, Muhammad Waqas3, Haitao Wang5, Oliver Donnerhack1, Olga Shibistova1, Stefan Wessel-Bothe8, Tim Mansfeldt9, and Georg Guggenberger1
Patrick Liebmann et al.
  • 1Institute of Earth System Sciences, Section Soil Sciences, Leibniz Universität Hannover, Hannover, Germany (liebmann@ifbk.uni-hannover.de)
  • 2Institute of Soil Science and Site Ecology, Chair of Soil Resources and Land Use, Technical University Dresden, Tharandt, Germany
  • 3Department of Ecosystems Biology, University of South Bohemia, České Budějovice, Czech Republic
  • 4Centre for Polar Ecology, Faculty of Science, University of South Bohemia, České Budějovice, Czech Republic
  • 5Institute of Microbiology, University of Greifswald, Greifswald, Germany
  • 6Geophysical Institute, University of Alaska Fairbanks, Fairbanks, USA
  • 7Ecological Microbiology, Bayreuth Center of Ecology and Environmental Research, University of Bayreuth, Bayreuth, Germany
  • 8ecoTech Umwelt-Meßsysteme GmbH, Bonn, Germany
  • 9Institute of Geography, University of Cologne, Cologne, Germany

Permafrost degradation, freezing and thawing processes, and poor drainage due to underlain frozen ground have far-reaching consequences on soil hydrology and biology and, thus, on the redox dynamic in soils of the Arctic. Assessing the redox status of these soils is essential for understanding soil organic matter decomposition processes and can be done by temporal measurements in the field, analyses of redox-sensitive elements, or identification of microbial species or enzymes in redox process chains. While such approaches provide snippets of the complex redox dynamic, publications reporting long-term in-situ redox potential (EH) measurements in arctic permafrost soils are scarce. Limited accessibility to study sites and technical limitations in measuring the redox potential in a frozen environment may be two reasons for this research gap.

But how does the redox potential develop in permafrost soils at different depths in the active layer during the summer? What happens during freezing and thawing? Finally, do thawing/degrading permafrost soils show different patterns compared to intact permafrost?

We approached these research questions by installation of a unique soil monitoring setup at 3 sites near Fairbanks, Alaska, in August 2021. An intact permafrost soil (active layer depth about 50 cm) was equipped with 3 redox electrodes (for EH) and 3 hydra probes (for water content and soil temperature) in the topsoil and subsoil, respectively, and connected to a logger unit allowing continuous measurement of these parameters in both depths every 15 minutes. In addition, two sites with advanced permafrost degradation (permafrost level below 100 cm) were equipped in the same way. One degraded site featured large water contents, representing a wet thaw scenario, while the other site was well-drained, representing a dry thaw scenario, thus representing different endmembers of the ongoing climate-change induced permafrost thaw.

Here, we present the first 2 years of soil monitoring in a discontinuous permafrost area in Interior Alaska from 09/2021 to 09/2023. Overall, pH values of all soils varied between 4.5-6.3. The dry thaw scenario showed oxic conditions (i.e., EH >600 mV) in top- and subsoil, while water contents were low. The wet thaw scenario exhibited high topsoil redox potentials (i.e., EH >500 mV), while subsoil redox potential was lower (i.e., EH <500 mV). High water contents in both intact permafrost and wet thaw scenario demonstrated a pronounced zero curtain effect over several months during the long winter season due to the release of latent heat during freezing. We further detected a strong 200-600 mV decrease in EH in the topsoil of the intact permafrost active layer during the summer season, reaching reducing conditions 1-3 months after seasonal thaw. Redox measurements in the subsoil of the intact permafrost active layer, which was about 25 cm below the topsoil measuring depth and about 5 cm above the frozen ground, revealed EH of >400 mV in the summer period (August to October), suggesting less oxygen consumption in this recently thawed permafrost subsoil.

How to cite: Liebmann, P., Vogel, C., Barta, J., Urich, T., Kholodov, A., Varsadiya, M., Waqas, M., Wang, H., Donnerhack, O., Shibistova, O., Wessel-Bothe, S., Mansfeldt, T., and Guggenberger, G.: Long-term soil redox dynamics of intact and degraded permafrost in Interior Alaska, EGU General Assembly 2024, Vienna, Austria, 14–19 Apr 2024, EGU24-16607, https://doi.org/10.5194/egusphere-egu24-16607, 2024.