Abstract

Abstract. In October–November 2011 we measured trace gas emission factors from seven prescribed fires in South Carolina (SC), US, using two Fourier transform infrared spectrometer (FTIR) systems and whole air sampling (WAS) into canisters followed by gas-chromatographic analysis. A total of 97 trace gas species were quantified from both airborne and ground-based sampling platforms, making this one of the most detailed field studies of fire emissions to date. The measurements include the first emission factors for a suite of monoterpenes produced by heating vegetative fuels during field fires. The first quantitative FTIR observations of limonene in smoke are reported along with an expanded suite of monoterpenes measured by WAS including α-pinene, β-pinene, limonene, camphene, 4-carene, and myrcene. The known chemistry of the monoterpenes and their measured abundance of 0.4–27.9% of non-methane organic compounds (NMOCs) and ~ 21% of organic aerosol (mass basis) suggests that they impacted secondary formation of ozone (O3), aerosols, and small organic trace gases such as methanol and formaldehyde in the sampled plumes in the first few hours after emission. The variability in the initial terpene emissions in the SC fire plumes was high and, in general, the speciation of the initially emitted gas-phase NMOCs was 13–195% different from that observed in a similar study in nominally similar pine forests in North Carolina ~ 20 months earlier. It is likely that differences in stand structure and environmental conditions contributed to the high variability observed within and between these studies. Similar factors may explain much of the variability in initial emissions in the literature. The ΔHCN/ΔCO emission ratio, however, was found to be fairly consistent with previous airborne fire measurements in other coniferous-dominated ecosystems, with the mean for these studies being 0.90 ± 0.06%, further confirming the value of HCN as a biomass burning tracer. The SC results also support an earlier finding that C3-C4 alkynes may be of use as biomass burning indicators on the time-scale of hours to a day. It was possible to measure the downwind chemical evolution of the plume on four of the fires and significant O3 formation (ΔO3/ΔCO from 10–90%) occurred in all of these plumes within two hours. The slowest O3 production was observed on a cloudy day with low co-emission of NOx. The fastest O3 production was observed on a sunny day when the downwind plume almost certainly incorporated significant additional NOx by passing over the Columbia, SC metropolitan area. Due to rapid plume dilution, it was only possible to acquire high-quality downwind data for two other trace gas species (formaldehyde and methanol) during two of the fires. In all four of these cases, significant increases in formaldehyde and methanol were observed in <2 h. This is likely the first direct observation of post-emission methanol production in biomass burning plumes. Post-emission production of methanol does not always happen in young biomass burning plumes, and its occurrence in this study could have involved terpene precursors to a significant extent.

Highlights

  • On a global scale, biomass burning is thought to be the largest source of primary fine carbonaceous particles in the atmosphere and the second largest source of total trace gases (Crutzen and Andreae, 1990; Bond et al, 2004; Akagi et al, 2011)

  • Detection limits for the compounds we report other than CO2 ranged from hundreds of ppt to 10 ppb for nitric oxide (NO) and NO2, where the gain in SNR was partially canceled by the decreased resolution

  • Fourier transform infrared spectrometer (FTIR) and whole air sampling (WAS) samples were combined in the calculation of fire-average emission ratios for species measured by both techniques from airborne and ground-based platforms

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Summary

Introduction

Biomass burning is thought to be the largest source of primary fine carbonaceous particles in the atmosphere and the second largest source of total trace gases (Crutzen and Andreae, 1990; Bond et al, 2004; Akagi et al, 2011). Despite land managers’ best efforts, prescribed fires, along with wildfires, do impact local-to-regional air quality (ozone, O3; particulate matter, PM), health, and visibility in the southeastern US and elsewhere (McMeeking et al, 2006; Pfister et al, 2006; Park et al, 2007; Liu et al, 2009). The major features of this study were to expand the scope of measurements to include: (1) emissions data for fires that burned in forest stands with a broader range of management histories, as well as in additional important fuel types, (2) post-emission plume evolution data on days with different solar insolation and on a day with significant mixing of urban and fire emissions, and (3) addressing all these topics with a significantly expanded suite of instrumentation. Initial emissions are discussed first followed by observations in the aging plumes

Experimental details
Other airborne measurements
Nov 10 Nov
Site descriptions
Airborne and ground-based sampling approach
Initial emissions
Brief comparison to similar work
Nov 2011
Background levels and production in smoke plumes
High levels of terpenes in fresh smoke
C3-C4 alkynes
Formaldehyde
Conclusions
Full Text
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