Abstract

Abstract. Forest ecosystems play a crucial role in the global carbon cycle by sequestering a considerable fraction of anthropogenic CO2, thereby contributing to climate change mitigation. However, there is a gap in our understanding about the carbon dynamics of eucalypt (broadleaf evergreen) forests in temperate climates, which might differ from temperate evergreen coniferous or deciduous broadleaved forests given their fundamental differences in physiology, phenology and growth dynamics. To address this gap we undertook a 3-year study (2010–2012) of eddy covariance measurements in a dry temperate eucalypt forest in southeastern Australia. We determined the annual net carbon balance and investigated the temporal (seasonal and inter-annual) variability in and environmental controls of net ecosystem carbon exchange (NEE), gross primary productivity (GPP) and ecosystem respiration (ER). The forest was a large and constant carbon sink throughout the study period, even in winter, with an overall mean NEE of −1234 ± 109 (SE) g C m−2 yr−1. Estimated annual ER was similar for 2010 and 2011 but decreased in 2012 ranging from 1603 to 1346 g C m−2 yr−1, whereas GPP showed no significant inter-annual variability, with a mean annual estimate of 2728 ± 39 g C m−2 yr−1. All ecosystem carbon fluxes had a pronounced seasonality, with GPP being greatest during spring and summer and ER being highest during summer, whereas peaks in NEE occurred in early spring and again in summer. High NEE in spring was likely caused by a delayed increase in ER due to low temperatures. A strong seasonal pattern in environmental controls of daytime and night-time NEE was revealed. Daytime NEE was equally explained by incoming solar radiation and air temperature, whereas air temperature was the main environmental driver of night-time NEE. The forest experienced unusual above-average annual rainfall during the first 2 years of this 3-year period so that soil water content remained relatively high and the forest was not water limited. Our results show the potential of temperate eucalypt forests to sequester large amounts of carbon when not water limited. However, further studies using bottom-up approaches are needed to validate measurements from the eddy covariance flux tower and to account for a possible underestimation in ER due to advection fluxes.

Highlights

  • Terrestrial ecosystems, together with the ocean, take up more than half of the yearly anthropogenic CO2 emissions and their combined sink strength has increased over the past 5 decades in step with increased emissions (Ballantyne et al, 2012; Le Quéré et al, 2013, 2015)

  • A clear distinct seasonal pattern was shown in the dependence of midday net ecosystem carbon exchange (NEE) on Fsd, Ta and vapour pressure deficit (VPD) when coefficients of determinations were plotted for each month (Fig. 6a)

  • Parameters, standard errors and/or the coefficient of determination (R2) of (a) the rectangular hyperbolic light-response curve (LRC) between daily means of midday NEE and incoming radiation (Fsd), (b) linear fits between residuals of LRC and air temperature (Ta) or vapour pressure deficit (VPD), and (c) linear fits between second residuals (b) with Ta and soil water content (SWC) for subsets of data. α: initial slope of LRC and canopy light-utilization efficiency; β: maximum NEE at light saturation

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Summary

Introduction

Terrestrial ecosystems, together with the ocean, take up more than half of the yearly anthropogenic CO2 emissions and their combined sink strength has increased over the past 5 decades in step with increased emissions (Ballantyne et al, 2012; Le Quéré et al, 2013, 2015). Uncertainty remains regarding the future trend in and strength of this terrestrial carbon sink (Ciais et al, 2013; Mystakidis et al, 2016; Reichstein et al, 2013; Sitch et al, 2015). This is mainly related to the high interannual variability in the carbon uptake of ecosystems because of regional and even global variations in climate from year to year (Ahlström et al, 2015; Reichstein et al, 2013). While some studies primarily attribute inter-annual variability in NEE to changes in respiration (Cox et al, 2000; Valentini et al, 2000), others point to a primary dependence on the variability in ecosystem GPP (Ahlström et al, 2015; Jung et al, 2011; Sitch et al, 2015)

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