Abstract

In order to estimate emission factors (EFs) of air pollutants, three types of biomass (rice straw, maize residue and leaf litter) were collected and burnt in a self-designed stainless steel chamber. The EFs of PM_(10) from biomass burning were leaf litter (1.22 ± 0.29 g kg_(dry)^(-1)) > rice straw (0.89 ± 0.25 g kg_(dry)^(-1)) > maize residue (0.59 ± 0.13 g kg_(dry)^(-1)), while those of PM_(10)-bound polycyclic aromatic hydrocarbons (PAHs) were leaf litter (0.91 ± 0.28 mg kg_(dry)^(-1)) > maize residue (0.47 ± 0.11 mg kg_(dry)^(-1)) ~ rice straw (0.46 ± 0.21 mg kg_(dry)^(-1)). The results revealed that burning of forest leaf litter emitted higher amounts of particulate pollutants than the agricultural residue burning. New values of diagnostic ratios of some PAHs, including FLA/(FLA + PYR, BaA/(BaA + CHR) and IND/(IND + BPER), were proposed to identify biomass burning sources. Emission rates (ERs) of PM_(10) and PAHs from biomass burning in Chiang Mai, Thailand were estimated based on the EFs and burning areas recorded in the dry season of 2010 and 2011. The ERs of pollutants from forest burning were found to be much higher than those from agricultural field burning, mainly due to larger burnt areas in the forest. In 2010, PM_(10) was mainly emitted from the forest fire (2,250 tons), followed by crop burning (133 tons) and paddy field burning (66.9 tons). The same trend was found in 2011 but with much lower emission rates. The ERs of PAHs from biomass burning were 1,815 kg in 2010 and 416 kg in 2011. The ERs of PM_(10) and PAHs in 2011 were 77% decreased from those in 2010 due to unusually high precipitation in the dry season, causing relatively smaller burnt areas and lower pollutant emissions from open burning. It is expected that the results from this study will be significant information for regulatory actions of air quality management in the northern part of Thailand.

Highlights

  • Biomass burning is the burning of living or dead vegetation such as forest, savannas and agricultural lands (Koppmann et al, 2005)

  • Emission rates (ERs) of PM10 and polycyclic aromatic hydrocarbons (PAHs) from biomass burning in Chiang Mai, Thailand were estimated based on the Emission Factors (EFs) and burning areas recorded in the dry season of 2010 and 2011

  • Leaf litter was collected in a shaded area under tree canopies, while rice straw and maize residues were collected in an open area

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Summary

Introduction

Biomass burning is the burning of living or dead vegetation such as forest, savannas and agricultural lands (Koppmann et al, 2005). Biomass burning has generated global concerns because it emits particles and vapor pollutants into the air, affecting visibility, human health and the global climate (Fang et al, 1999; Yang et al, 2007). Biomass burning is a common method for agricultural residue disposal. This method represents a considerable source of atmospheric pollutants (Korenaga et al, 2001; Chang et al, 2015; Lyu et al, 2015). The PAHs recognized as carcinogenic are mostly associated with particulate matter. Atmospheric PAH concentrations are strongly dependent upon the size of airborne particulate matter (PM)

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