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Challenges in the use of local data for regional scale mapping of C and N stocks in the continuous permafrost zone at the Yukon Coastal Plain

  • Julia Wagner*
  • , Juliane Wolter
  • , Justine Ramage
  • , Victoria Martin
  • , Andreas Richter
  • , Niek Jesse Speetjens
  • , Jorien E. Vonk
  • , Rachele Lodi
  • , Annett Bartsch
  • , Michael Fritz
  • , Hugues Lantuit
  • , Gustaf Hugelius
  • *Corresponding author for this work

Research output: Contribution to Journal › Article › Academic › peer-review

Abstract

Permafrost soils are particularly vulnerable to climate change. To assess and improve estimations of carbon (C) and nitrogen (N) budgets it is necessary to accurately map soil carbon and nitrogen in the permafrost region. In particular, soil organic carbon (SOC) stocks have been predicted and mapped by many studies from local to pan-Arctic scales. Several studies have been carried out at the Canadian Beaufort Sea coast, though no regional maps of terrestrial carbon stocks based on spatial modelling has been conducted yet. This study combines available field data from the Canadian Yukon coastal plain and uses it to map regional SOC and N stocks using the machine learning algorithm random forest and environmental variables based on remote sensing data. We developed models using the data for the entire region and separate models for the coastal mainland area and Qikiqtaruk Herschel Islandand. Each model was used to map SOC and N stocks for its respective area. We assessed the performance of the different random forest models by using crossvalidation. We further assessed model results using the Area of Applicability (AOA) method and the quantile regression forest approach, comparing the results and discussing their implications within the context of both methods. We explore local differences in soil properties and how soil data distribution across the region affects the accuracy of the predictions of SOC and N stocks. The estimated SOC stock for the upper metre is 48.7 ± 6.6 kg m-2 and the N stock 3.03 ± 0.30 kg m-2. The average SOC stocks vary significantly when creating separate models for subsets of the data. Qikiqtaruk Herschel Island is geologically different from the coastal mainland and has on average lower SOC stocks. Including Qikiqtaruk Herschel Island soil data to predict SOC stocks at the mainland has large impact on the results. Differences in N stocks were not as dependent on the location as SOC stocks and rather differences between individual studies occurred. The results of the separate models show 38.0 ± 5.6 kg C m-2 and 2.87 ± 0.34 kg N m-2 for Qikiqtaruk Herschel Island and 52.5 ± 6.3 kg C m-2 and 3.15 ± 0.32 kg N m-2 for the mainland. These estimates refer to the entire study area, without masking out regions outside the Area of Applicability (AOA). Our results indicate that the spatial perspective, whether regional or local (whole area vs. mainland and Qikiqtaruk Herschel Island separately), can affect the patterns and values represented in the resulting maps, highlighting the importance of scale when interpreting SOC and N stock distributions. Using a more densely sampled, region-specific dataset, our study captures finer regional-scale patterns than previous lower-resolution or pan-Arctic analyses.

Original languageEnglish
Pages (from-to)113-132
Number of pages20
JournalSoil
Volume12
Issue number1
Early online date10 Feb 2026
DOIs
Publication statusPublished - 2026

Bibliographical note

Publisher Copyright:
© 2026 Julia Wagner et al.

Funding

The authors would like to thank GeorgeTanski for help with coring during the Yukon Coast 2019 springfield campaign and Justin Lindemann for assistance in AWI laboratories. We thank the Yukon Territorial Government, the Yukon Parksoffice (Herschel Island Qikiqtaruk Territorial Park), Parks Canadaoffice (Ivvavik National Park) and the Aurora Research Institute andAurora College (ARI) in Inuvik, NT, for administrative and logistical support for our fieldwork.This study is part of the Nunataryuk project,which received funding under the European Union’s Horizon2020 Research and Innovation Programme under grant agreementno. 773421. JWo was funded by German Research Foundation(DFG) (grant no. DFG WO 2420/2-1). JR received additionalfunding from the Swedish Academy of Science (Formas) (grant no. FR-2021/0004). GH received support from the EuropeanUnion’s Horizon Europe Research and Innovation Programme tothe ILLUQ project (grant no. 773421) and the Swedish ResearchCouncil VR (grant no. 2022-04839). This study is part of the Nunataryuk project, which received funding under the European Union's Horizon 2020 Research and Innovation Programme under grant agreement no. 773421. JWo was funded by German Research Foundation (DFG) (grant no. DFG WO 2420/2-1). JR received additional funding from the Swedish Academy of Science (Formas) (grant no. FR‐2021/0004). GH received support from the European Union's Horizon Europe Research and Innovation Programme to the ILLUQ project (grant no. 773421) and the Swedish Research Council VR (grant no. 2022-04839).The publication of this article was funded by the Swedish Research Council, Forte, Formas, and Vinnova.

FundersFunder number
Swedish ResearchCouncil VR
European Union’s Horizon2020 research and innovation programme
Yukon Parksoffice
Aurora Research Institute
European Union's Horizon Europe research and innovation programme
Yukon Territorial Government
Herschel Island Qikiqtaruk Territorial Park
EuropeanUnion’s Horizon Europe Research and Innovation Programme
Horizon 2020 Framework Programme773421
Deutsche ForschungsgemeinschaftDFG WO 2420/2-1
Swedish Academy of Science (Formas)FR‐2021/0004
Vetenskapsrådet2022-04839

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