Abstract

Nitrogen (N2) fixation is a major source of available N in ecosystems that receive low amounts of atmospheric N deposition. In boreal forest and subarctic tundra, the feather moss Hylocomium splendens is colonized by N2 fixing cyanobacteria that could contribute fundamentally to increase the N pool in these ecosystems. However, N2 fixation in mosses is inhibited by N input. Although this has been shown previously, the ability of N2 fixation to grow less sensitive towards repeated, increased N inputs remains unknown. Here, we tested if N2 fixation in H. splendens can recover from increased N input depending on the N load (0, 5, 20, 80, 320 kg N ha-1 yr-1) after a period of N deprivation, and if sensitivity towards increased N input can decrease after repeated N additions. Nitrogen fixation in the moss was inhibited by the highest N addition, but was promoted by adding 5 kg N ha-1 yr-1, and increased in all treatments during a short period of N deprivation. The sensitivity of N2 fixation towards repeated N additions seem to decrease in the 20 and 80 kg N additions, but increased in the highest N addition (320 kg N ha-1 yr-1). Recovery of N in leachate samples increased with increasing N loads, suggesting low retention capabilities of mosses if N input is above 5 kg N ha-1 yr-1. Our results demonstrate that the sensitivity towards repeated N additions is likely to decrease if N input does not exceed a certain threshold.

Highlights

  • Nitrogen fixation is a main input of new N for N limited habitats like subarctic tundra [1]

  • In a laboratory set-up [13], the authors found no inhibition of N2 fixation in P. schreberi at additions of 10 kg N, contrasting the results reported by [8], and [10] showing moss associated N2 fixation to be inhibited by road-derived N deposition of 4 kg N ha-1 yr-1 in boreal forests

  • Moss-associated N2 fixation in boreal forests has been shown to be inhibited by N input [8, 9, 10]

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Summary

Introduction

Nitrogen fixation is a main input of new N for N limited habitats like subarctic tundra [1]. While deposition of reactive N (Nr) in these areas is low (0–2 kg N ha-1 yr-1) [2], the predicted increase in Nr input to N-limited ecosystems seems inevitable e.g [3], and the effects on major ecosystem functions, like N2 fixation, have yet to be comprehensively assessed. Feather mosses like Hylocomium splendens are ubiquitous in subarctic tundra, covering large fractions of the ground [4] and can contribute significantly to ecosystem productivity [5]. H. splendens is colonized by several genera of N2-fixing cyanobacteria [6], contributing fundamentally to the N pool in pristine habitats [7].

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