Emissions of PCDD and PCDF from combustion of forest fuels and sugarcane: A comparison between field measurements and simulations in a laboratory burn facility

被引:24
作者
Black, R. R. [1 ]
Meyer, C. P. [2 ]
Touati, A. [3 ]
Gullett, B. K. [4 ]
Fiedler, H. [5 ]
Mueller, J. F. [1 ]
机构
[1] Univ Queensland, Natl Res Ctr Environm Toxicol, Coopersplains, Qld 4108, Australia
[2] CSIRO Marine & Atmospher Res, Aspendale, Vic, Australia
[3] ARCADIS Geraghty & Miller Inc, Res Triangle Pk, NC 27709 USA
[4] US EPA, Off Res & Dev, Res Triangle Pk, NC 27711 USA
[5] UNEP DTIE Chem Branch, CH-1219 Chatelaine, GE, Switzerland
关键词
Polychlorinated dibenzo-p-clioxins; Polychlorinated dibenzofurans; Persistent organic pollutants; Bushfires; Forest fires; Sugarcane burning; FIRE;
D O I
10.1016/j.chemosphere.2011.03.062
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Release of PCDD and PCDF from biomass combustion such as forest and agricultural crop fires has been nominated as an important source for these chemicals despite minimal characterisation. Available emission factors that have been experimentally determined in laboratory and field experiments vary by several orders of magnitude from <0.51 mu g TEQ(t fuel consumed)(-1) to >1001 mu g TEQ(t fuel consumed)(-1). The aim of this study was to evaluate the effect of experimental methods on the emission factor. A portable field sampler was used to measure PCDD/PCDF emissions from forest fires and the same fuel when burnt over a brick hearth to eliminate potential soil effects. A laboratory burn facility was used to sample emissions from the same fuels. There was very good agreement in emission factors to air (EFAir) for forest fuel (Duke Forest, NC) of 0.52 (range: 0.40-0.79), 0.59 (range: 0.18-1.2) and 0.75 (range: 0.27-1.2) mu g TEQ(WHO2005) (t fuel consumed)(-1) for the in-field, over a brick hearth, and burn facility experiments, respectively. Similarly, experiments with sugarcane showed very good agreement with EFAir of 1.1 (range: 0.40-2.2), 1.5 (range: 0.84-2.2) and 1.7 (range: 0.34-4.4) mu g TEQ (t fuel consumed)(-1) for in-field, over a brick hearth, open field and burn facility experiments respectively. Field sampling and laboratory simulations were in good agreement, and no significant changes in emissions of PCDD/PCDF could be attributed to fuel storage and transport to laboratory test facilities. (C) 2011 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1331 / 1338
页数:8
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