1. Introduction
Arctic biological soil crusts (biocrusts) play crucial roles in harsh environments, with fungi contributing significantly to nutrient cycling and soil stabilization [
1]. Fungi in biocrusts decompose organic matter, mineralize nutrients, and form symbiotic relationships with phototrophic organisms, impacting both biocrust productivity and soil structure. Arctic fungi exhibit remarkable adaptations, possessing cold-active enzymes, melanized cell walls for UV resistance, and specialized water retention strategies [
2,
3]. These traits enhance their survival under environmental stress and shape community composition along altitude and environmental gradients.
While studies have documented the altitudinal responses of phototrophic biocrust members, the patterns and drivers of fungal diversity and function across elevation gradients in the Arctic remain poorly understood. We hypothesize that increasing elevation, and the associated changes in temperature, moisture, and radiation, will select for fungal taxa with traits conferring greater stress tolerance (e.g., melanization, psychrotolerance, production of extracellular polysaccharides), leading to shifts in both taxonomic composition and functional profiles. By integrating community profiling with functional trait analysis, our aim is to provide new insights into how Arctic fungi contribute to biocrust resilience and ecosystem functioning under varying environmental conditions.
2. Materials and Methods
Site descriptions, sampling procedures, chemical parameters, and phototrophic community composition were previously described in [
4]. In summary, biocrust samples were collected during the summers of 2022 and 2023 from three localities in Kongsfjorden (Svalbard), selected to represent a spatial gradient from the open sea toward the inner parts of the fjord: Outer Fjord (OF; Geop, Knau, Kn), Mid Fjord (MF; Knud, Bl), and Inner Fjord (IF; Gr, Os), each comprising low and high elevation sites (marked as L and H, respectively). The most common vascular plants included
Dryas octopetala,
Salix polaris,
Saxifraga oppositifolia,
Carex sp.,
Silene acaulis, and
Bistorta vivipara. The collected biocrusts were well-developed and comprised lichens and bryophytes, with their abundance varying by elevation. Five replicates were collected from each site and the total DNA was extracted and subsequently sequenced using the Illumina NovaSeq6000 platform (PE150). The raw reads were submitted to the Sequence Read Archive (SRA) under the project PRJNA1124630.
Bioinformatic analysis was performed using the OmicsBox software (Biobam, Spain), and the reads were quality-filtered using Trimmomatic [
5]. The taxonomic classification of the fungi was executed using the UNITE database (v10.0). Fungi were further divided into the functional guilds based on their primary lifestyle using the FungalTraits database [
6]. Genes were predicted with MetaEuk on the Galaxy platform and functionally annotated using EggNOG (v5.0.2; Huerta-Cepas et al., 2017). Differential abundance of KEGG metabolic pathways between low- and high-elevation samples was assessed with a false discovery rate (FDR) cut-off of 0.05 and a log fold change threshold of –2 to +2.
Statistical analyses were carried out in R (version 4.2.1). To test for differences among the sampling sites, one and two-way analyses of variance (ANOVA) were conducted, followed by Tukey's HSD post hoc test (p-value < 0.05). Normality of variance was assessed using Shapiro–Wilk's test. If necessary, data were Log or SQRT transformed. Furthermore, to illustrate the distribution of fungal reads, non-metric multidimensional scaling (NMDS) was performed using the package vegan [
8] and statistical difference was tested with the ANOSIM test. Soil parameters were fitted into the ordination space using the function envfit and significance of the associations was determined by 999 random permutations.
3. Results and Discussion
The majority of the fungal reads in all samples were assigned to the Ascomycota across the samples (40-81% of fungal reads;
Supplementary Figure S1). Basidiomycota (3-29% of fungal reads) and Rozellomycota (3-18% of fungal reads) were also the dominant fungal phyla, as found in previous studies of Arctic biocrusts [
9]. The relative abundance of the majority of fungal phyla demonstrated no significant variation across elevation and location in the fjord. However, two phyla, namely Mucoromycota and Zoopagomycota, exhibited a marked increase in abundance at lower elevations. It has been demonstrated that certain Mucoromycota fungi facilitate plant growth and benefit from plant-derived organic matter [
10], which is supported by the higher angiosperm coverage observed at the lower sites. The presence of dense vegetation has also been linked to a more diverse soil food web, resulting in increased populations of microarthropods, nematodes, and protozoa. These organisms, in turn, might serve as prey for numerous species of Zoopagomycota [
11].
A recent study showed that the diversity of saprotrophs in forest soils from Europe and Iceland declines with elevation [
12]. In contrast, in the present study no significant differences in fungal genus richness or read abundance were observed for any fungal guild between low- and high-elevation sites (
Figure 1). However, the location within the fjord significantly affected the composition of the fungi, with the number of fungal genera and read abundance being lower in MF sites and higher in IF sites (
Figure 1 and
Figure 2).
The NMDS plot based on fungal read counts, followed by a PERMANOVA test, showed that the location within the fjord significantly explained variation in community composition (R² = 13.9%, p = 0.001), whereas elevation had a non-significant effect (R² = 2.1%, p > 0.05;
Figure 2). Fungal community dissimilarities were explained by pH, C:N ratio and chlorophyll a, TP contents. Sites in MF had higher pH and chlorophyll a, but lower TP and C:N, which could relate to lower fungal abundance and richness observed there. C:N ratio appears to be a critical factor influencing fungal distribution and competitive success, potentially shaping community composition even across small-scale elevational gradients [
13]. Sites in OF and IF, with higher C:N ratios and TP content, might favour fungal taxa capable of efficiently degrading complex carbon compounds, given that the elevated P availability supports the metabolic and enzymatic processes required for their growth and function [
14].
Despite no significant differences between fungal phyla and guilds, 27 genera were identified as indicators of sites at high elevation, while 4 genera were designated as indicators of sites at low elevation (
Supplementary Table S1). For example, lichenized fungi (e.g.
Staurothele,
Acarospora,
Placopsis,
Calogaya,
Pannoparmelia) were significantly associated with higher-elevation sites, which was also consistent with vegetation analyses showing increased lichen coverage in these areas [
4]. Harsh environmental conditions at higher elevations limit vascular plant growth, reducing competition for space and nutrients and allowing lichens to proliferate [
15]. Increased lichen diversity at higher elevation could provide more hosts for endolichenic (
Sclerococcum) or lichenicolous (
Endococcus and
Cercidospora) fungi, which were also indicator taxa of high elevations biocrusts.
Functional annotation indicated that the core metabolic pathway, such as oxidative phosphorylation (map00190), was consistently observed in fungal communities across the sites (15-38% of annotated fungal contigs). However, fungi from high-elevation sites exhibited significant enrichment in DNA repair, stress signaling, cell structure, gene expression machinery, and specialized metabolism pathways, reflecting adaptations to additional stressors [
16,
17] associated with higher elevations, such as increased UV exposure, lower temperatures, and more extreme microclimatic variability compared to lower-elevation sites (
Table 1). As some pathways were exclusively detected in high-elevation communities and absent in low-elevation ones, these appeared as extreme fold-change values, which should be interpreted as presence/absence signals rather than precise quantitative differences.
Overall, these findings emphasize that Arctic fungal diversity and function are governed not solely by elevation but by a combination of local biotic and abiotic factors, highlighting their integral role in sustaining biocrust stability, nutrient cycling, and ecosystem resilience in polar environments.
Supplementary Materials
The following supporting information can be downloaded at the website of this paper posted on Preprints.org.
Funding
This project was supported by Deutsche Forschungsgemeinschaft (DFG) within the project PU867/1-1, Be1779/.
Data Availability Statement
The original contributions presented in this study are included in the article/supplementary material. Further inquiries can be directed to the corresponding author.
Acknowledgments
We would like to thank members of AWIPEW station in Ny-Ålesund for technical and logistic support during sampling. Furthermore, we are grateful to Isabel Mas Martinez and Leonie Keilholz for the laboratory assistance.
Conflicts of Interest
The authors declare no conflict of interest.
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