Abstract

Abstract. Peatlands represent a vast carbon reserve that has accumulated under conditions of low nitrogen availability. Given the strong coupling between the carbon and nitrogen cycles, we need to establish the consequences of the increase in reactive nitrogen deposition for the sustainability of peatlands, and whether the form in which the nitrogen is deposited makes a difference. We have addressed these questions using a globally unique field simulation of reactive N deposition as dry deposited ammonia and wet deposited reduced N, ammonium and oxidised N, nitrate, added as ammonium chloride or sodium nitrate, to an ombrotrophic peatland, Whim bog in SE Scotland. Here we report the fate of 56 kg N ha−1 yr−1 additions over 10 yr and the consequences. The effects of 10 yr of reactive N additions depended on the form in which the N was applied. Ammonia-N deposition caused the keystone Sphagnum species, together with the main shrub Calluna and the pleurocarpous mosses, to disappear, exposing up to 30% of the peat surface. This led to a significant increase in soil water nitrate and nitrous oxide emissions. By contrast wet deposited N, despite significantly reducing the cover of Sphagnum and Pleurozium moss, did not have a detrimental effect on Calluna cover nor did it significantly change soil water N concentrations or nitrous oxide emissions. Importantly 10 yr of wet deposited N did not bare the peat surface nor significantly disrupt the vegetation enabling the N to be retained within the carbon rich peatland ecosystems. However, given the significant role of Sphagnum in maintaining conditions that retard decomposition, this study suggests that all nitrogen forms will eventually compromise carbon sequestration by peatlands through loss of some keystone Sphagnum species.

Highlights

  • Peatlands and bogs are valuable carbon (C) stores and potential C sinks (Belyea and Malmer, 2004)

  • Cover of the common non-vascular plants (S. capillifolium, H. jutlandicum and P. schreberi) was eliminated by the NH3 treatment, while H. jutlandicum and P. schreberi were significantly affected (p = 0.015 and p < 0.001 respectively) by the high wet N treatments. Both Nox and Nred significantly reduced the cover of Pleurozium, whereas Nox increased the cover of Hypnum while www.biogeosciences.net/10/149/2013/

  • In summary we have shown that a substantial increase (∼ 8∗ ambient, over 9 yr ∼ 600 kg N ha−1) in N deposition to an acidic peatland can substantially increase the greenhouse gas (GHG) N2O emissions by > 100 fold, but this only occurs when the vegetative sink is compromised

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Summary

Introduction

Peatlands and bogs are valuable carbon (C) stores and potential C sinks (Belyea and Malmer, 2004). Peat soils are the product of C sequestration, a consequence of C assimilation exceeding rates of decomposition. Anthropogenic activities can challenge the manifestation of these properties and undermine the ability of peat bog ecosystems to fulfil their role as C sinks (Gunnarsson and Rydin, 2000), especially where change influences the drivers that control C and nitrogen (N) cycling. Increases in anthropogenic N deposition can increase productivity and C assimilation and release C if decomposition rates are accelerated through changes in N availability or species composition (van Breeman, 1995a). The overall consequences of enhanced N deposition for vegetation, function and sustainability and its fate in peat bogs are not fully understood

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