9 research outputs found

    Uncertainties in global aerosols and climate effects due to biofuel emissions

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    Aerosol emissions from biofuel combustion impact both health and climate; however, while reducing emissions through improvements to combustion technologies will improve health, the net effect on climate is largely unconstrained. In this study, we examine sensitivities in global aerosol concentration, direct radiative climate effect, and cloud-albedo aerosol indirect climate effect to uncertainties in biofuel emission factors, optical mixing state, and model nucleation and background secondary organic aerosol (SOA). We use the Goddard Earth Observing System global chemical-transport model (GEOS-Chem) with TwO Moment Aerosol Sectional (TOMAS) microphysics. The emission factors include amount, composition, size, and hygroscopicity, as well as optical mixing-state properties. We also evaluate emissions from domestic coal use, which is not biofuel but is also frequently emitted from homes. We estimate the direct radiative effect assuming different mixing states (homogeneous, core-shell, and external) with and without absorptive organic aerosol (brown carbon). We find the global-mean direct radiative effect of biofuel emissions ranges from −0.02 to +0.06 W m−2 across all simulation/mixing-state combinations with regional effects in source regions ranging from −0.2 to +0.8 W m−2. The global-mean cloud-albedo aerosol indirect effect (AIE) ranges from +0.01 to −0.02 W m−2 with regional effects in source regions ranging from −1.0 to −0.05 W m−2. The direct radiative effect is strongly dependent on uncertainties in emissions mass, composition, emissions aerosol size distributions, and assumed optical mixing state, while the indirect effect is dependent on the emissions mass, emissions aerosol size distribution, and the choice of model nucleation and secondary organic aerosol schemes. The sign and magnitude of these effects have a strong regional dependence. We conclude that the climate effects of biofuel aerosols are largely unconstrained, and the overall sign of the aerosol effects is unclear due to uncertainties in model inputs. This uncertainty limits our ability to introduce mitigation strategies aimed at reducing biofuel black carbon emissions in order to counter warming effects from greenhouse gases. To better understand the climate impact of particle emissions from biofuel combustion, we recommend field/laboratory measurements to narrow constraints on (1) emissions mass, (2) emission size distribution, (3) mixing state, and (4) ratio of black carbon to organic aerosol

    Aerosol Optical Depth Over India

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    Tropospheric aerosol optical depth (AOD) over India was simulated by Goddard Earth Observing System (GEOS)-Chem, a global 3-D chemical-transport model, using SMOG (Speciated Multi-pOllutant Generator from Indian Institute of Technology Bombay) and GEOS-Chem (GC) (current inventories used in the GEOS-Chem model) inventories for 2012. The simulated AODs were similar to 80% (SMOG) and 60% (GC) of those measured by the satellites (Moderate Resolution Imaging Spectroradiometer and Multi-angle Imaging SpectroRadiometer). There is no strong seasonal variation in AOD over India. The peak AOD values are observed/simulated during summer. The simulated AOD using SMOG inventory has particulate black and organic carbon AOD higher by a factor similar to 5 and 3, respectively, compared to GC inventory. The model underpredicted coarse-mode AOD but agreed for fine-mode AOD with Aerosol Robotic Network data. It captured dust only over Western India, which is a desert, and not elsewhere, probably due to inaccurate dust transport and/or noninclusion of other dust sources. The calculated AOD, after dust correction, showed the general features in its observed spatial variation. Highest AOD values were observed over the Indo-Gangetic Plain followed by Central and Southern India with lowest values in Northern India. Transport of aerosols from Indo-Gangetic Plain and Central India into Eastern India, where emissions are low, is significant. The major contributors to total AOD over India are inorganic aerosol (41-64%), organic carbon (14-26%), and dust (7-32%). AOD over most regions of India is a factor of 5 or higher than over the United States. Plain Language Summary Overhead amounts of particulate matter, their chemical make up, and their variations over India, a highly polluted and fast developing country, were calculated using a global model. It shows that the particulate pollution levels over the Indo-Gangetic Plain is more than 5 times higher than over the United States. The use of the most recent available emission inventory shows that there is more black carbon, from incomplete combustion, than estimated using the existing regional inventory. The calculations also show that the cleanest part is the very Northern India and that pollution over Eastern India is significantly influenced by what happens over the Indo-Gangetic Plain

    Characterization and night-time oxidation of pellet stove emissions

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    A growing energy demand has shifted interest towards alternative energy sources such as biomass combustion. Wood has become an important fuel even in the developed world, frequently used in households for heating purposes mostly as logs but also as pellets. During winter biomass burning is one of the most important air pollution sources emitting both primary organic aerosol (POA) and organic vapours that can be oxidized producing secondary organic aerosol (SOA). Pellet stoves are considered as low-emitting combustion sources, but a growing influence of their emissions on air quality is expected. For example, during 2018 global wood pellet consumption increased by 130% compared to its 2013 levels, reaching 53 million tons (EPC, 2019). Half of this consumption took place in Europe (27 million tons; 60% increase in 5 years). Recently, there has been increasing interest in exploring the extent of night-time chemical processing of biomass burning emissions. Hartikainen et al. (2018) reported substantial SOA production in laboratory experiments under dark conditions. Kodros et al. (2020) suggested that dark oxidation of biomass burning plumes by NO3 radicals may be an additional formation pathway of oxygenated OA and may lead to secondary inorganic and organic aerosol nitrate formation. Environmental simulation chamber experiments were performed in the Foundation of Research and Technology-Hellas atmospheric simulation chamber (FORTH-ASC), to characterize fresh and aged pellet stove emissions. The fresh PM1 (particulate matter with diameter less than 1 μm) emissions consisted mainly of organics (93 ± 4 %), followed by black carbon (5 ± 3 %), nitrates and sulfate (1 %). The emission rates of fresh OA were in the range of 2.6 to 12 g kg-1 of pellets depending on burning conditions, while the POA oxygen-to-carbon ratio (O:C) was 0.58 ± 0.04. The pH for the fresh emissions estimated to be 3.2 ± 0.3. The oxidation of the pellet emissions was investigated under dark conditions by injecting nitrogen dioxide (NO2) and ozone (O3), at different relative humidity (RH) levels. In all experiments SOA was formed (1-32 μg m-3), increasing the OA levels by 2-28 % after a few hours of exposure to NO3 radicals in the chamber (3 - 5 hours of equivalent atmospheric dark oxidation) (Figure 1). An increase in the O:C ratio of the OA by 7-21 % was also observed. Figure 1. SOA (red bars) and organic nitrate (black bars) mass concentrations for the dark ageing experiments. These results suggest that dark oxidation of pellet emissions is an additional biomass burning SOA source that should be considered in atmospheric models. This work was supported by the European Research Council PyroTRACH project (grant 726165) and the EU Horizon-2020 project REMEDIA (grant 874753)
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