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 15 N-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 13 C from 13 CO 2 labelling to assess if N and C fixation are linked. Three days after labelling, half of the fixed 15 N was recovered in the legume soils, indicating a fast release of fixed N 2 . Within 5 weeks, the free-living N 2 fixers released twothirds of the fixed 15 N into the soil, whereas the lichen and moss retained the fixed 15 N. 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 nondiazotroph-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.