Abstract

Soil respiration (R S) represents a large terrestrial source of CO2 to the atmosphere. Global change drivers such as climate warming and nitrogen deposition are expected to alter the terrestrial carbon cycle with likely consequences for R S and its components, autotrophic (R A) and heterotrophic respiration (R H). Here we investigate the impacts of a 3°C soil warming treatment and a 50 kg ha−1 y−1 nitrogen addition treatment on R S, R H and their respective seasonal temperature responses in an experimental tussock grassland. Average respiration in untreated soils was 0.96±0.09 μmol m−2 s−1 over the course of the experiment. Soil warming and nitrogen addition increased R S by 41% and 12% respectively. These treatment effects were additive under combined warming and nitrogen addition. Warming increased R H by 37% while nitrogen addition had no effect. Warming and nitrogen addition affected the seasonal temperature response of R S by increasing the basal rate of respiration (R 10) by 14% and 20% respectively. There was no significant interaction between treatments for R 10. The treatments had no impact on activation energy (E 0). The seasonal temperature response of R H was not affected by either warming or nitrogen addition. These results suggest that the additional CO2 emissions from New Zealand tussock grassland soils as a result of warming-enhanced R S constitute a potential positive feedback to rising atmospheric CO2 concentration.

Highlights

  • Soils contain a pool of carbon approximately double that stored in terrestrial biomass [1]

  • Both RS and RH were sensitive to soil water content, with a reduction in respiration rate observed below 0.2 m3 m23 soil water content

  • The average (6 SE) soil respiration rate measured in the control plots over the course of this study was 0.9660.09 mmol m22 s21

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Summary

Introduction

Soils contain a pool of carbon approximately double that stored in terrestrial biomass [1]. Soil respiration (RS), the primary pathway for return of soil carbon to the atmosphere, is increasing globally by 0.1 Pg C y21 at present [2]. Several notable examples have shown the effect of warming on RS to be only transient [7,8] Mechanisms for this acclimation of RS to prolonged warming include depletion of labile carbon substrates [8,9,10], changes to the microbial community structure [7,11], physiological acclimation of soil microbes [12], reduction in root biomass [13] and reduction in the specific root respiration rate [14]. Acclimation of soil respiration may limit potential soil carbon loss as a result of climate warming

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