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Leaf N Abundance of Subarctic Plants Provides Field Evidence That Ericoid, Ectomycorrhizal and Non-and Arbuscular Mycorrhizal Species Access Different Sources of Soil Nitrogen

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Journal Oecologia
Date 2017 Mar 18
PMID 28307122
Citations 29
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Abstract

The natural abundance of the nitrogen isotope 15, δN, was analysed in leaves of 23 subarctic vascular plant species and two lichens from a tree-line heath at 450 m altitude and a fellfield at 1150 m altitude close to Abisko in N. Sweden, as well as in soil, rain and snow. The aim was to reveal if plant species with different types of mycorrhizal fungi also differ in their use of the various soil N sources. The dwarf shrubs and the shrubs, which in combination formed more than 65% of the total above-ground biomass at both sites, were colonized by ericoid or ectomycorrhizal fungi. Their leaf δN was between-8.8 and-5.5‰ at the heath and between-6.1 and -3.3‰ at the fellfield. The leaf δN of non- or arbuscular mycorrhizal species was markedly different, ranging from -4.1 to -0.4‰ at the heath, and from -3.4 to+2.2‰ at the fellfield. We conclude that ericoid and ectomycorrhizal dwarf shrubs and shrubs utilize a distinct N source, most likely a fraction of the organic N in fresh litter, and not complexed N in recalcitrant organic matter. The latter is the largest component of soil total N, which had a δN of -0.7‰ at the heath and +0.5‰ at the fellfield. Our field-based data thus support earlier controlled-environment studies and studies on the N uptake of excised roots, which have demonstrated protease activity and amino acid uptake by ericoid and ectomycorrhizal tundra species. The leaves of ectomycorrhizal plants had slightly higher δN (fellfield) and N concentration than leaves of the ericoids, and Betula nana, Dryas octopetala and Salix spp. also showed NO reductase activity. These species may depend more on soil inorganic N than the ericoids. The δN of non- or arbuscular mycorrhizal species indicates that the δN of inorganic N available to these plants was higher than that of average fresh litter, probably due to high microbial immobilization of inorganic N. The δN of NH -N was +12.3‰ in winter snow and +1.9‰ in summer rain. Precipitation N might be a major contributer in species with poorly developed root systems, e.g. Lycopodium selago. Our results show that coexisting plant species under severe nutrient limitation may tap several different N sources: NH , NO and organic N from the soil, atmospheric N, and N in precipitation. Ericoid and ectomycorrhizal fungi are of major importance for plant N uptake in tundra ecosystems, and mycorrhizal fungi probably exert a major control on plant δN in organic soils.

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References
1.
Michelsen A, Schmidt I, Jonasson S, Dighton J, Jones H, Callaghan T . Inhibition of growth, and effects on nutrient uptake of arctic graminoids by leaf extracts - allelopathy or resource competition between plants and microbes?. Oecologia. 2017; 103(4):407-418. DOI: 10.1007/BF00328678. View

2.
Michelsen A, Jonasson S, Sleep D, Havstrom M, Callaghan T . Shoot biomass, δC, nitrogen and chlorophyll responses of two arctic dwarf shrubs to in situ shading, nutrient application and warming simulating climatic change. Oecologia. 2017; 105(1):1-12. DOI: 10.1007/BF00328785. View

3.
Atkin O, Villar R, Cummins W . The ability of several high arctic plant species to utilize nitrate nitrogen under field conditions. Oecologia. 2017; 96(2):239-245. DOI: 10.1007/BF00317737. View

4.
Jonasson S, Havstrom M, Jensen M, Callaghan T . In situ mineralization of nitorgen and phosphorus of arctic soils after perturbations simulating climate change. Oecologia. 2017; 95(2):179-186. DOI: 10.1007/BF00323488. View

5.
Virginia R, Delwiche C . Natural N abundance of presumed N-fixing and non-N-fixing plants from selected ecosystems. Oecologia. 2017; 54(3):317-325. DOI: 10.1007/BF00380000. View