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      Aerosol optical properties and trace gas emissions by PAX and OP-FTIR for laboratory-simulated western US wildfires during FIREX

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          Abstract

          <p><strong>Abstract.</strong> Western wildfires have a major impact on air quality in the US. In the fall of 2016, 107 test fires were burned in the large-scale combustion facility at the US Forest Service Missoula Fire Sciences Laboratory as part of the Fire Influence on Regional and Global Environments Experiment (FIREX). Canopy, litter, duff, dead wood, and other fuel components were burned in combinations that represented realistic fuel complexes for several important western US coniferous and chaparral ecosystems including ponderosa pine, Douglas fir, Engelmann spruce, lodgepole pine, subalpine fir, chamise, and manzanita. In addition, dung, Indonesian peat, and individual coniferous ecosystem fuel components were burned alone to investigate the effects of individual components (e.g., “duff”) and fuel chemistry on emissions. The smoke emissions were characterized by a large suite of state-of-the-art instruments. In this study we report emission factor (EF, grams of compound emitted per kilogram of fuel burned) measurements in fresh smoke of a diverse suite of critically important trace gases measured using open-path Fourier transform infrared spectroscopy (OP-FTIR). We also report aerosol optical properties (absorption EF; single-scattering albedo, SSA; and Ångström absorption exponent, AAE) as well as black carbon (BC) EF measured by photoacoustic extinctiometers (PAXs) at 870 and 401<span class="thinspace"></span>nm. The average trace gas emissions were similar across the coniferous ecosystems tested and most of the variability observed in emissions could be attributed to differences in the consumption of components such as duff and litter, rather than the dominant tree species. Chaparral fuels produced lower EFs than mixed coniferous fuels for most trace gases except for NO<span class="inline-formula"><sub><i>x</i></sub></span> and acetylene. A careful comparison with available field measurements of wildfires confirms that several methods can be used to extract data representative of real wildfires from the FIREX laboratory fire data. This is especially valuable for species rarely or not yet measured in the field. For instance, the OP-FTIR data alone show that ammonia (1.62<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup>)</span>, acetic acid (2.41<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup>)</span>, nitrous acid (HONO, 0.61<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup>)</span>, and other trace gases such as glycolaldehyde (0.90<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup>)</span> and formic acid (0.36<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup>)</span> are significant emissions that were poorly characterized or not characterized for US wildfires in previous work. The PAX measurements show that the ratio of brown carbon (BrC) absorption to BC absorption is strongly dependent on modified combustion efficiency (MCE) and that BrC absorption is most dominant for combustion of duff (AAE 7.13) and rotten wood (AAE 4.60): fuels that are consumed in greater amounts during wildfires than prescribed fires. Coupling our laboratory data with field data suggests that fresh wildfire smoke typically has an EF for BC near 0.2<span class="thinspace"></span>g<span class="thinspace"></span>kg<span class="inline-formula"><sup>−1</sup></span>, an SSA of <span class="inline-formula">∼</span><span class="thinspace"></span>0.91, and an AAE of <span class="inline-formula">∼</span><span class="thinspace"></span>3.50, with the latter implying that about 86<span class="thinspace"></span>% of the aerosol absorption at 401<span class="thinspace"></span>nm is due to BrC.</p>

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          Biomass burning in the tropics: impact on atmospheric chemistry and biogeochemical cycles.

          Biomass burning is widespread, especially in the tropics. It serves to clear land for shifting cultivation, to convert forests to agricultural and pastoral lands, and to remove dry vegetation in order to promote agricultural productivity and the growth of higher yield grasses. Furthermore, much agricultural waste and fuel wood is being combusted, particularly in developing countries. Biomass containing 2 to 5 petagrams of carbon is burned annually (1 petagram = 10(15) grams), producing large amounts of trace gases and aerosol particles that play important roles in atmospheric chemistry and climate. Emissions of carbon monoxide and methane by biomass burning affect the oxidation efficiency of the atmosphere by reacting with hydroxyl radicals, and emissions of nitric oxide and hydrocarbons lead to high ozone concentrations in the tropics during the dry season. Large quantities of smoke particles are produced as well, and these can serve as cloud condensation nuclei. These particles may thus substantially influence cloud microphysical and optical properties, an effect that could have repercussions for the radiation budget and the hydrological cycle in the tropics. Widespread burning may also disturb biogeochemical cycles, especially that of nitrogen. About 50 percent of the nitrogen in the biomass fuel can be released as molecular nitrogen. This pyrdenitrification process causes a sizable loss of fixed nitrogen in tropical ecosystems, in the range of 10 to 20 teragrams per year (1 teragram = 10(12) grams).
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            A technology-based global inventory of black and organic carbon emissions from combustion

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                Author and article information

                Journal
                Atmospheric Chemistry and Physics
                Atmos. Chem. Phys.
                Copernicus GmbH
                1680-7324
                2018
                March 01 2018
                : 18
                : 4
                : 2929-2948
                Article
                10.5194/acp-18-2929-2018
                c729a1da-ddb1-4806-b856-b201faed0d5d
                © 2018

                https://creativecommons.org/licenses/by/4.0/

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