Abstract

Abstract. We have tested the ability of a high-resolution chemical transport model (CTM) to reproduce biomass burning (BB) plume strikes and ozone (O3) enhancements observed at Cape Grim in Tasmania, Australia, from the Robbins Island fire. The CTM has also been used to explore the contribution of near-field BB emissions and background sources to O3 observations under conditions of complex meteorology. Using atmospheric observations, we have tested model sensitivity to meteorology, BB emission factors (EFs) corresponding to low, medium, and high modified combustion efficiency (MCE), and spatial variability. The use of two different meteorological models (TAPM–CTM and CCAM–CTM) varied the first (BB1) plume strike time by up to 15 h and the duration of impact between 12 and 36 h, and it varied the second (BB2) plume duration between 50 and 57 h. Meteorology also had a large impact on simulated O3, with one model (TAPM–CTM) simulating four periods of O3 enhancement, while the other model (CCAM) simulating only one period. Varying the BB EFs, which in turn varied the non-methane organic compound (NMOC) ∕ oxides of nitrogen (NOx) ratio, had a strongly non-linear impact on simulated O3 concentration, with either destruction or production of O3 predicted in different simulations. As shown in previous work (Lawson et al., 2015), minor rainfall events have the potential to significantly alter EF due to changes in combustion processes. Models that assume fixed EF for O3 precursor species in an environment with temporally or spatially variable EF may be unable to simulate the behaviour of important species such as O3. TAPM–CTM is used to further explore the contribution of the Robbins Island fire to the observed O3 enhancements during BB1 and BB2. Overall, TAPM–CTM suggests that the dominant source of O3 observed at Cape Grim was aged urban air (age = 2 days), with a contribution of O3 formed from local BB emissions. This work shows the importance of assessing model sensitivity to meteorology and EF and the large impact these variables can have in particular on simulated destruction or production of O3 in regional atmospheric chemistry simulations. This work also shows the importance of using models to elucidate the contribution from different sources to atmospheric composition, where this is difficult using observations alone.

Highlights

  • Biomass burning (BB) makes a major global contribution to atmospheric trace gases and particles, with ramifications for human health, air quality and climate

  • We investigated how much model spatial gradients vary by sampling The Air Pollution Model (TAPM)–chemical transport model (CTM) output with modified combustion efficiency (MCE) = 0.89 at four grid points located 1 km to the north, east, south and west of Cape Grim

  • In this work we have used a unique set of opportunistic BB observations at Cape Grim Baseline Air Pollution Station to test the ability of Commonwealth Scientific and Industrial Research Organisation (CSIRO)’s high-resolution (400 m grid cell) CTM to reproduce primary (CO, black carbon (BC)) and secondary (O3) BB species in challenging non-stationary, inhomogeneous and near-field conditions

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Summary

Introduction

Biomass burning (BB) makes a major global contribution to atmospheric trace gases and particles, with ramifications for human health, air quality and climate. Emitted species include carbon monoxide (CO), carbon dioxide (CO2), oxides of nitrogen (NOx), primary organic aerosol, non-methane organic compounds (NMOCs) and black carbon (BC), while chemical transformations occurring in the plume over time lead to formation of secondary species such as O3, oxygenated NMOC and secondary aerosol. Depending on a number of factors, including magnitude and duration of fire, plume rise, and meteorology, the impact of BB plumes on human health, air quality and climate may be local, regional or global. Lawson et al.: Modelling biomass burning at Cape Grim

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