Abstract. Permafrost ecosystems are limited in nutrients for
vegetation development and constrain the biological activity to the active
layer. Upon Arctic warming, permafrost thaw exposes large amounts of soil
organic carbon (SOC) to decomposition and minerals to weathering but also
releases organic and mineral soil material that may directly influence the
soil exchange properties (cation exchange capacity, CEC, and base saturation,
BS). The soil exchange properties are key for nutrient base cation supply
(Ca2+, K+, Mg2+, and Na+) for vegetation growth and
development. In this study, we investigate the distributions of soil exchange
properties within Arctic tundra permafrost soils at Eight Mile Lake
(Interior Alaska, USA) because they will dictate the potential reservoir of
newly thawed nutrients and thereby influence soil biological activity and
vegetation nutrient sources. Our results highlight much lower CEC density in
surface horizons (∼9400 cmolc m−3) than in the mineral
horizons of the active layer (∼16 000 cmolc m−3)
or in permafrost soil horizons (∼12 000 cmolc m−3). Together, with the overall increase in CEC density with depth and
the overall increase in BS (percentage of CEC occupied by exchangeable base
cations Ca2+, K+, Mg2+, and Na+) with depth (from
∼19 % in organic surface horizons to 62 % in permafrost soil
horizons), the total exchangeable base cation density (Ca2+, K+,
Mg2+, and Na+ in g m−3) is up to 5 times higher in the
permafrost than in the active layer. More specifically, the exchangeable
base cation density in the 20 cm upper part of permafrost about to thaw is
∼850 g m−3 for Caexch, 45 g m−3 for
Kexch, 200 g m−3 for Mgexch, and 150 g m−3 for
Naexch. This estimate is needed for future ecosystem prediction models
to provide constraints on the size of the reservoir in exchangeable
nutrients (Ca, K, Mg, and Na) about to thaw. All data described in this paper are stored in Dataverse, the online repository of Université catholique de Louvain, and are accessible through the following DOI: https://doi.org/10.14428/DVN/FQVMEP (Mauclet et al., 2022b).