Abstract

Abstract. Using the 1-D atmospheric chemistry transport model SOSAA, we have investigated the atmospheric reactivity of a boreal forest ecosystem during the HUMPPA-COPEC-10 campaign (summer 2010, at SMEAR~II in southern Finland). For the very first time, we present vertically resolved model simulations of the NO3 and O3 reactivity (R) together with the modelled and measured reactivity of OH. We find that OH is the most reactive oxidant (R ∼ 3 s-1) followed by NO3 (R ∼ 0.07 s-1) and O3 (R ∼ 2 × 10-5s-1). The missing OH reactivity was found to be large in accordance with measurements (∼ 65%) as would be expected from the chemical subset described in the model. The accounted OH radical sinks were inorganic compounds (∼ 41%, mainly due to reaction with CO), emitted monoterpenes (∼ 14%) and oxidised biogenic volatile organic compounds (∼ 44%). The missing reactivity is expected to be due to unknown biogenic volatile organic compounds and their photoproducts, indicating that the true main sink of OH is not expected to be inorganic compounds. The NO3 radical was found to react mainly with primary emitted monoterpenes (∼ 60%) and inorganic compounds (∼ 37%, including NO2). NO2 is, however, only a temporary sink of NO3 under the conditions of the campaign (with typical temperatures of 20–25 °C) and does not affect the NO3 concentration. We discuss the difference between instantaneous and steady-state reactivity and present the first boreal forest steady-state lifetime of NO3 (113 s). O3 almost exclusively reacts with inorganic compounds (∼ 91%, mainly NO, but also NO2 during night) and less with primary emitted sesquiterpenes (∼ 6%) and monoterpenes (∼ 3%). When considering the concentration of the oxidants investigated, we find that OH is the oxidant that is capable of removing organic compounds at a faster rate during daytime, whereas NO3 can remove organic molecules at a faster rate during night-time. O3 competes with OH and NO3 during a short period of time in the early morning (around 5 a.m. local time) and in the evening (around 7–8 p.m.). As part of this study, we developed a simple empirical parameterisation for conversion of measured spectral irradiance into actinic flux. Further, the meteorological conditions were evaluated using radiosonde observations and ground-based measurements. The overall vertical structure of the boundary layer is discussed, together with validation of the surface energy balance and turbulent fluxes. The sensible heat and momentum fluxes above the canopy were on average overestimated, while the latent heat flux was underestimated.

Highlights

  • As most biogenically and anthropogenically emitted trace gases are oxidised within the Earth’s boundary layer, the oxidising capacity of this layer may be considered to be approximately that of the atmosphere

  • Using the 1-D atmospheric chemistry transport model SOSAA, we have investigated the atmospheric reactivity of a boreal forest ecosystem during the HUMPPACOPEC-10 campaign

  • Since one of the main aims of this paper is to investigate the reactivity of NO3, and since the concentrations of NO and NO2 are crucial in order to obtain this, we chose to use the Max Planck Institute (MPI)-measured NOx concentrations for our simulations due to the high sensitivity of the MPI instrument, unless otherwise specified

Read more

Summary

Introduction

As most biogenically and anthropogenically emitted trace gases are oxidised within the Earth’s boundary layer, the oxidising capacity of this layer may be considered to be approximately that of the atmosphere. Anthropogenic activity, resulting in increased sources of air pollution and more intense forest management (e.g. deforestation), results in changes in the composition of the atmosphere and potentially in its oxidation capacity. Especially those in forested areas, is the large missing fraction of the OH reactivity. This means that OH is lost due to unaccounted processes that is most often attributed to unmeasured and unidentified compounds either originating from direct emission or formed via oxidation processes Mount and Eisele, 1992; Di Carlo et al, 2004; Sinha et al, 2010) This means that OH is lost due to unaccounted processes that is most often attributed to unmeasured and unidentified compounds either originating from direct emission or formed via oxidation processes (e.g. Mount and Eisele, 1992; Di Carlo et al, 2004; Sinha et al, 2010)

Objectives
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call