Nitrogen (N) fixation is the main source of 'new' N for N-limited ecosystems like subarctic and arctic tundra. This crucial ecosystem function is performed by a wide range of N-2 fixer (diazotroph) associations that could differ fundamentally in their timing and amount of N release to the soil. To assess the importance of different associative N-2 fixers for ecosystem N cycling, we tracked N-15-N-2 into four N-2-fixer associations (with a legume, lichen, free-living, moss) and into soil, microbial biomass and non-diazotroph-associated plants 3 days and 5 weeks after in situ labelling. In addition, we tracked C-13 from (CO2)-C-13 labelling to assess if N and C fixation are linked. Three days after labelling, half of the fixed N-15 was recovered in the legume soils, indicating a fast release of fixed N-2. Within 5 weeks, the free-living N-2 fixers released two-thirds of the fixed N-15 into the soil, whereas the lichen and moss retained the fixed N-15. Carbon and N-2 fixation were linked in the lichen shortly after labelling, in free-living N-2 fixers 5 weeks after labelling, and in the moss at both sampling times. The four investigated N-2-fixer associations released fixed N-2 at different rates into the soil, and non-diazotroph-associated plants have no access to 'new' N within several weeks after N-2 fixation. Although legumes and free-living N-2 fixers are immediate sources of 'new' N for N-limited tundra ecosystems, lichens and especially mosses, do not contribute to increase the N pool via N-2 fixation in the short term.