Project Details
Projekt Print View

Soil nitrogen turnover and nitrous oxide emissions in continuous permafrost landscapes of Northern China in a changing climate (NIFROCLIM)

Subject Area Soil Sciences
Biochemistry
Microbial Ecology and Applied Microbiology
Metabolism, Biochemistry and Genetics of Microorganisms
Term from 2019 to 2024
Project identifier Deutsche Forschungsgemeinschaft (DFG) - Project number 410850447
 
Final Report Year 2023

Final Report Abstract

In this project, soil nitrogen (N) turnover and nitrous oxide (N2O) emissions in permafrost landscapes in a changing climate were investigated. Due to an assumption of strong temperature limitation and low ecosystem inputs and availability of N according to the traditional permafrost N cycle paradigm, organic N cycling has been thought to dominate over only marginal mineral N cycling (ammonification, nitrification, denitrification). Thus, also hardly any climate change feedbacks via emissions of N2O had been expected, since these require an active mineral N cycle. However, this traditional permafrost N cycle paradigm builds on relatively little experimental evidence such as net rates of N turnover but not on measurement of gross N turnover processes. In addition, climate change, being particularly rapid in the Arctic, could amplify mineral N cycling in permafrost-affected soils. Thus, the overall goal of this project was to improve the understanding of soil biogeochemical N turnover processes in permafrost ecosystems. Field studies in the Eurasian permafrost of Northeast China and in Greenland were conducted to quantify gross N turnover across landscapes, the role of alder invasion, as well as of different fire intensities for N turnover in permafrost-affected soils. Finally, within a comprehensive synthetic meta-analysis and review we modified the traditional N cycle paradigm. This was necessary because both meta-analyses and field studies revealed the main assumptions of the traditional permafrost N cycle paradigm to be erroneous: Gross N mineralization and N2O emissions occur despite low temperatures, supported by, e.g., large N inputs via biological N2 fixation. In fact, organic N is ammonified and nitrified in active layers at large rates comparable to those in temperate and tropical systems. Permafrost-affected soils even show a very similar dependency on soil organic carbon content as a universal driver of gross N mineralization. Vigorous permafrost N cycling is confirmed by a well-adapted functional microbial community found both in active and permafrost layers. We therefore suggested a revised paradigm of permafrost N cycling with a high importance of mineral N at least in active layers and no general difference to N cycling in other soils. Also in the field study in boreal permafrost in Northeast China, significant gross mineral N turnover rates determined with in situ 15N pool dilution were detected both in mineral upland and organic lowland soils. Importantly, expansion of alders leads to a massive acceleration of the N cycle. Symbiotic input of N via Alnus-Frankia associations doubled topsoil N concentrations, thereby boosting gross ammonification and gross nitrification as well as soil N2O emissions by an order of magnitude in the sampled alder forest. As alders spread on permafrost-affected soils in the course of climate change, the described effect could trigger significant permafrost N-climate feedbacks. In addition, increasing thawing depths promote N release from formerly protected permafrost which can further increase mineral N turnover. N turnover in frozen soils and the origin of unexpected ammonium peaks close to the permafrost table are remaining research gaps. Another climate change factor are Arctic fires. Our molecular ecological studies within a fire experiment in Greenland underlined the potential role of tundra fires of low intensity but not high intensity for promoting microbes involved in N mineralization in the short term, while long-term fire effects on the microbiome need further investigation. Overall, the results of this project quantitatively reveal the unexpectedly large importance of mineral N transformations in permafrost-affected soils which will further increase through climatechange impacts. This has severe implications for Arctic ecosystem functioning in a warming climate, as more mineral N turnover might strongly increase N2O source strength, but also provide mineral nutrients for a potentially faster development of vegetation.

Publications

 
 

Additional Information

Textvergrößerung und Kontrastanpassung