Abstract

Steady-state and dynamic gas exchange responses to ozone visible injury were investigated in an ozone-sensitive poplar clone under field conditions. The results were translated into whole tree water loss and carbon assimilation by comparing trees exposed to ambient ozone and trees treated with the ozone-protectant ethylenediurea (EDU). Steady-state stomatal conductance and photosynthesis linearly decreased with increasing ozone visible injury. Dynamic responses simulated by severing of a leaf revealed that stomatal sluggishness increased until a threshold of 5% injury and was then fairly constant. Sluggishness resulted from longer time to respond to the closing signal and slower rate of closing. Changes in photosynthesis were driven by the dynamics of stomata. Whole-tree carbon assimilation and water loss were lower in trees exposed to ambient O3 than in trees protected by EDU, both under steady-state and dynamic conditions. Although stomatal sluggishness is expected to increase water loss, lower stomatal conductance and premature leaf shedding of injured leaves aggravated O3 effects on whole tree carbon gain, while compensating for water loss. On average, WUE of trees exposed to ambient ozone was 2–4% lower than that of EDU-protected control trees in September and 6–8% lower in October.

Highlights

  • Tropospheric ozone (O3) is an important phytotoxic air pollutant and is recognized as a significant greenhouse gas [1]

  • Sluggishness has been reported during dynamic stomatal responses to fluctuating photosynthetic photon flux density (PPFD) [22,24,25,26,27], vapor pressure deficit (VPD) [27], and severe water stress imposed by severing a leaf [26,28,29,30]

  • Whole-tree leaf water loss and carbon assimilation under the severe water stress simulated by severing a leaf (Wloss_st: mol H2O tree21 s21, and Atree_st: mmol CO2 tree21 s21) were estimated by the following equations: Wloss

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Summary

Introduction

Tropospheric ozone (O3) is an important phytotoxic air pollutant and is recognized as a significant greenhouse gas [1]. Effects of O3 on stomatal responses are not straightforward, as both reductions and sluggish responses have been reported [21,22]. Sluggishness has been reported during dynamic stomatal responses to fluctuating photosynthetic photon flux density (PPFD) [22,24,25,26,27], vapor pressure deficit (VPD) [27], and severe water stress imposed by severing a leaf [26,28,29,30]. Forest ability of water control and carbon sequestration under O3 pollution is of rising importance [14]

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