Abstract

Abstract. Elevated levels of tropospheric ozone, O3, cause damage to terrestrial vegetation, affecting leaf stomatal functioning and reducing photosynthesis. Climatic impacts under future raised atmospheric greenhouse gas (GHG) concentrations will also impact on the net primary productivity (NPP) of vegetation, which might for instance alter viability of some crops. Together, ozone damage and climate change may adjust the current ability of terrestrial vegetation to offset a significant fraction of carbon dioxide (CO2) emissions. Climate impacts on the land surface are well studied, but arguably large-scale modelling of raised surface level O3 effects is less advanced. To date most models representing ozone damage use either O3 concentration or, more recently, flux-uptake-related reduction of stomatal opening, estimating suppressed land–atmosphere water and CO2 fluxes. However there is evidence that, for some species, O3 damage can also cause an inertial “sluggishness” of stomatal response to changing surface meteorological conditions. In some circumstances (e.g. droughts), this loss of stomata control can cause them to be more open than without ozone interference. To both aid model development and provide empiricists with a system on to which measurements can be mapped, we present a parameter-sparse framework specifically designed to capture sluggishness. This contains a single time-delay parameter τO3, characterizing the timescale for stomata to catch up with the level of opening they would have without damage. The larger the value of this parameter, the more sluggish the modelled stomatal response. Through variation of τO3, we find it is possible to have qualitatively similar responses to factorial experiments with and without raised O3, when comparing to reported measurement time series presented in the literature. This low-parameter approach lends itself to the inclusion of ozone-induced inertial effects being incorporated in the terrestrial vegetation component of Earth system models (ESMs).

Highlights

  • Anthropogenic emissions from industrial processes, transport and biomass burning are increasing background levels of surface ozone, O3 (Vingarzan, 2004)

  • There is much evidence this adjusts the stomatal opening of terrestrial vegetation, and so influencing land–atmosphere exchanges of water and carbon both globally and locally (Ainsworth et al, 2012; Wittig et al, 2007, 2009; Mills et al, 2016)

  • Extensive projections of ozone impacts on the land surface response need understanding within the context of other large-scale changes affecting terrestrial ecosystems. These include the direct physiological effect of raised CO2 through fossil fuel burning, the impact of climate change due to raised CO2 and other greenhouse gases (GHGs), and aerosols adjusting the composition of downward shortwave radiation (Huntingford et al, 2011)

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Summary

Introduction

Anthropogenic emissions from industrial processes, transport and biomass burning are increasing background levels of surface ozone, O3 (mol mol−1) (Vingarzan, 2004). Extensive projections of ozone impacts on the land surface response need understanding within the context of other large-scale changes affecting terrestrial ecosystems. These include the direct physiological effect of raised CO2 through fossil fuel burning, the impact of climate change due to raised CO2 and other greenhouse gases (GHGs), and aerosols adjusting the composition of downward shortwave radiation (Huntingford et al, 2011). If a substantial fraction of vegetation responses to elevated tropospheric ozone contain stomata sluggishness, this requires implementation in large-scale terrestrial vegetation models and ESMs to assess global implications.

Sluggishness parameter τO3 and modelled stomatal opening
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