Abstract

Increasing atmospheric nitrogen (N) deposition has profound effects on carbon (C) cycling in forest ecosystems. As an important part of belowground C dynamics, soil respiration is potentially affected by changing N availability. However, the responses of total soil respiration (RST) and its three components, soil respiration derived from plant roots (RSR), root-free soil (RSS) and the litter layer (RSL), to such N enrichment remains poorly understood. To assess the effects of N enrichment on soil respiration components, three levels of N addition, namely low (LN, 50 kg N ha−1 year−1), medium (MN, 100 kg N ha−1 year−1) and high (HN, 150 kg N ha−1 year−1), were conducted over five growing seasons from 2011 to 2015 in a temperate Chinese pine (Pinus tabulaeformis) forest in northern China. A control plot without N addition (CK) was also established. The five-year mean annual rate of RST was 2.18 ± 0.43 μmol m−2 s−1, and the contributions of RSR, RSS and RSL were 8.8 ± 3.1%, 82.2 ± 4.5% and 9.0 ± 5.5%, respectively. Compared with CK, RST was significantly increased by 16.5% in the HN plots, but not in the LN or MN treatments. RSS was significantly decreased by 18.1%, 26.6% and 18.4% in the LN, MN and HN plots, respectively, due to the reduction of both microbial biomass carbon (MBC) and enzyme activity. In contrast, RSR was increased by more than twice under the MN treatment, which promoted root growth and activity (higher fine root biomass and N concentration). A significant elevation in RSL was only detected in the HN plots, where the increased litter input enhanced litter decomposition and hence RSL. Our findings clearly demonstrated that N addition of different intensities had different effects on soil components. In particular, the above- and belowground components of heterotrophic respiration, RSL and RSR, showed contrasting responses to high level addition of N. Thus, we highlight that the response of soil respiration components to N addition should be examined individually. Our results may contribute to a better understanding of soil respiration dynamics under future N scenarios, and have important implications in forest management.

Highlights

  • Anthropogenic activities, including fossil fuel combustion and nitrogen (N)-based fertilizer application, have caused a three- to five-fold increase in the deposition of atmospheric N over the last century [1,2,3]

  • We have highlighted the different responses of soil respiration and its components to N addition of different intensities

  • Total soil respiration in response to N addition was largely dependent on its components, autotrophic respiration and heterotrophic respiration

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Summary

Introduction

Anthropogenic activities, including fossil fuel combustion and nitrogen (N)-based fertilizer application, have caused a three- to five-fold increase in the deposition of atmospheric N over the last century [1,2,3]. Nitrogen deposition is predicted to continue to increase 2.5-fold by the end of the century [2]. Forests 2018, 9, 544 the rapid increase in N deposition may have profound effects on ecosystem processes and functioning, such as plant growth and productivity [4,5], soil properties [6,7] and the biogeochemical cycling of carbon (C) [8]. As the second largest C flux in terrestrial ecosystems, soil respiration (RS) plays an important role in global and regional C cycling [9,10]. Total soil respiration (RST ) consists of autotrophic and heterotrophic components [11,12]. Autotrophic respiration derives from plant roots and its symbionts (RSR ), whereas heterotrophic respiration originates from the decomposition of root-free soil organic

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