Emissions of organic air toxics from open burning: a comprehensive review

Emissions from open burning, on a mass pollutant per mass fuel (emission factor) basis, are greater than those from well-controlled combustion sources. Some types of open burning (e.g. biomass) are large sources on a global scale in comparison to other broad classes of sources (e.g. mobile and industrial sources). A detailed literature search was performed to collect and collate available data reporting emissions of organic air toxics from open burning sources. The sources that were included in this paper are: Accidental Fires, Agricultural Burning of Crop Residue, Agricultural Plastic Film, Animal Carcasses, Automobile Shredder Fluff Fires, Camp Fires, Car – Boat– Train (the vehicle not cargo) Fires, Construction Debris Fires, Copper Wire Reclamation, Crude Oil and Oil Spill Fires, Electronics Waste, Fiberglass, Fireworks, Grain Silo Fires, Household Waste, Land Clearing Debris (biomass), Landfills/Dumps, Prescribed Burning and Savanna/Forest Fires, Structural Fires, Tire Fires, and Yard Waste Fires. Availability of data varied according to the source and the class of air toxics of interest. Volatile organic compound (VOC) and polycyclic aromatic hydrocarbon (PAH) data were available for many of the sources. Non-PAH semi-volatile organic compound (SVOC) data were available for several sources. Carbonyl and polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofuran (PCDD/F) data were available for only a few sources. There were several known sources for which no emissions data were available at all. It is desirable that emissions from those sources be tested so that the relative degree of hazard they pose can be assessed. Several observations were made including: Biomass open burning sources typically emitted less VOCs than open burning sources with anthropogenic fuels on a mass emitted per mass burned basis, particularly those where polymers were concerned. Biomass open burning sources typically emitted less SVOCs and PAHs than anthropogenic sources on a mass emitted per mass burned basis. Burning pools of crude oil and diesel fuel produced significant amounts of PAHs relative to other types of open burning. PAH emissions were highest when combustion of polymers was taking place. Based on very limited data, biomass open burning sources typically produced higher levels of carbonyls than anthropogenic sources on a mass emitted per mass burned basis, probably due to oxygenated structures resulting from thermal decomposition of cellulose. It must be noted that local burn conditions could significantly change these relative levels. Based on very limited data, PCDD/F and other persistent bioaccumulative toxic (PBT) emissions varied greatly from source to source and exhibited significant variations within source categories. This high degree of variation is likely due to a combination of factors, including fuel composition, fuel heating value, bulk density, oxygen transport, and combustion conditions. This highlights the importance of having acceptable test data for PCDD/F and PBT emissions from open burning so that contributions of sources to the overall PCDD/F and PBT emissions inventory can be better quantified. q 2003 Elsevier Ltd. All rights reserved.

[1]  Charlotte Clark,et al.  Burning tires for fuel and tire pyrolysis: air implications , 1991 .

[2]  Bette Hileman.  Little Progress Made In New Delhi , 2002 .

[3]  Joaquim Casal,et al.  Flame temperature distribution in a pool-fire , 1998 .

[4]  Paul M. Lemieux,et al.  Evaluation of Emissions from the Open Burning of Household Waste in Barrels , 1998 .

[5]  R. Gerstle,et al.  Atmospheric emissions from open burning. , 1967, Journal of the Air Pollution Control Association.

[6]  D. F. Natschke,et al.  Field evaluation of a method for estimating gaseous fluxes from area sources using open-path Fourier transform infrared. , 2001, Environmental science & technology.

[7]  C. Lutes,et al.  Aquatic ecological risks due to cyanide releases from biomass burning. , 2003, Chemosphere.

[8]  Joseph P. Pinto,et al.  Chemical and Physical Properties of Emissions from Kuwaiti Oil Fires , 1993 .

[9]  K. F. Higgins,et al.  Prescribed Burning Guidelines in the Northern Great Plains , 1989 .

[10]  C. C. Lutes,et al.  Characterization of emissions from the simulated open-burning of non-metallic automobile shredder residue. Final report, February 1989-October 1992 , 1993 .

[11]  Paulo Artaxo,et al.  Chemical composition of aerosol particles from direct emissions of vegetation fires in the Amazon Basin: water-soluble species and trace elements , 2000 .

[12]  William T Winberry,et al.  Compendium of methods for the determination of toxic organic compounds in ambient air, June 1988 , 1988 .

[13]  Paul M. Lemieux,et al.  Characterization of air pollutants emitted from a simulated scrap tire fire , 1993 .

[14]  L. Goldman,et al.  Polychlorinated Dibenzo-p-dioxin and Dibenzofuran Contamination at Metal Recovery Facilities, Open Burn Sites, and a Railroad Car Incineration Facility. , 1995, Environmental science & technology.

[15]  B. Fisher,et al.  Modelling plume rise and dispersion from pool fires , 2001 .

[16]  Tahir Husain,et al.  Kuwaiti oil fires : source estimates and plume characterization , 1994 .

[17]  J. Levine,et al.  Biomass Burning: A Driver for Global Change! , 1995 .

[18]  Ram A. Hashmonay,et al.  Computed tomography of air pollutants using radial scanning path-integrated optical remote sensing , 1999 .

[19]  W B Grant,et al.  Optical remote measurement of toxic gases. , 1992, Journal of the Air & Waste Management Association.

[20]  R. B. Williamson,et al.  Smoke Emission Factors from Medium-Scale Fires: Part 2 , 1989 .

[21]  J. Reisman.  Air Emissions from Scrap Tire Combustion , 1997 .

[22]  B. Simoneit,et al.  Molecular characterization of smoke from campfire burning of pine wood (Pinus elliottii) , 2000 .

[23]  Abderrahmane Touati,et al.  PCDD/F emissions from forest fire simulations. , 2003 .

[24]  W. Lorenz,et al.  Release of polychlorinated dibenzo-p-dioxins and dibenzofurans by setting off fireworks. , 1999, Chemosphere.

[25]  Effects of open-air burning of metal scrap on ambient polycyclic aromatic hydrocarbon concentrations , 1995 .

[26]  H. Lee,et al.  Mutagenicity of airborne particulates from combustion of electric cables in a waste metal retrieval area. , 1994, Mutation research.

[27]  Ryan.  Characterization of emissions from the simulated open burning of scrap tires. Final report, August 1988-June 1989 , 1989 .

[28]  P. Coleman,et al.  Dioxins in ambient air, bonfire night 1994 , 1997 .

[29]  B. Gullett,et al.  Variables Affecting Emissions of PCDD/Fs from Uncontrolled Combustion of Household Waste in Barrels , 2003, Journal of the Air & Waste Management Association.

[30]  Joseph V. Mullin,et al.  Studies of Emissions from Oil Fires , 1999 .

[31]  B. Simoneit,et al.  Identification and emission factors of molecular tracers in organic aerosols from biomass burning Part 2. Deciduous trees , 2001 .

[32]  B. Simoneit,et al.  Identification and emission factors of molecular tracers in organic aerosols from biomass burning Part 1. Temperate climate conifers , 2001 .

[33]  Edward J. Tennyson,et al.  Emissions from mesoscale in situ oil fires: the mobile 1991 experiments , 1996 .

[34]  S. Masunaga,et al.  Congener-specific characterization of PCDDs/PCDFs in atmospheric deposition: comparison of profiles among deposition, source, and environmental sink. , 2001, Chemosphere.

[35]  Kevin B. McGrattan,et al.  Numerical simulation of smoke plumes from large oil fires , 1996 .

[36]  G. Petersson,et al.  Methoxyphenols from burning of Scandinavian forest plant materials. , 2000, Chemosphere.

[37]  Ram A. Hashmonay,et al.  On the application of Open-Path Fourier transform Infra-Red spectroscopy to measure aerosols : Observations of water droplets , 1999 .

[38]  Bryan M. Jenkins,et al.  Development of test procedures to determine emissions from open burning of agricultural and forestry wastes. , 1990 .

[39]  J. Hobbs.  Particle and Gas Emissions from an In Situ Burn of Crude Oil on the Ocean. , 1996, Journal of the Air & Waste Management Association.

[40]  B. Jenkins,et al.  Particle concentrations, gas-particle partitioning, and species intercorrelations for polycyclic aromatic hydrocarbons (PAH) emitted during biomass burning , 1996 .

[41]  K. Perry.  Effects of Outdoor Pyrotechnic Displays on the Regional Air Quality of Western Washington State. , 1999, Journal of the Air & Waste Management Association.

[42]  M. Andreae,et al.  Emission of trace gases and aerosols from biomass burning , 2001 .

[43]  Christopher C Lutes,et al.  EVALUATION OF EMISSIONS FROM PAVING ASPHALTS. , 1994 .

[44]  B. Gullett,et al.  Emissions of PCDD/F from uncontrolled, domestic waste burning. , 2001, Chemosphere.

[45]  Juhani Ruuskanen,et al.  Formation of polyaromatic hydrocarbons and polychlorinated organic compounds in municipal waste landfill fires , 1995 .

[46]  D. DeMarini,et al.  Chemical and biological characterization of products of incomplete combustion from the simulated field burning of agricultural plastic. , 1989, JAPCA.

[47]  V. S. Engleman,et al.  Characterization of Emissions Formed from Open Burning of Pesticide Bags , 1992 .

[48]  J. Abbott,et al.  Emissions of polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans from the open burning of household waste in barrels , 2000 .

[49]  J. Lacaux,et al.  Determination of biomass burning emission factors: Methods and results , 1995, Environmental monitoring and assessment.

[50]  R. B. Williamson,et al.  Smoke Emission Factors from Medium-Scale Fires: Part 1 , 1989 .

[51]  Olavi Keski-Rahkonen,et al.  Landfill Fires in Finland , 1996 .

[52]  C. Liousse,et al.  Emissions of Polycyclic aromatic hydrocarbons by savanna fires , 1995 .

[53]  Lindsay E. Booher,et al.  Air Emissions from Petroleum Hydrocarbon Fires During Controlled Burning , 1997 .

[54]  Bryan M. Jenkins,et al.  Emission factors for polycyclic aromatic hydrocarbons from biomass burning , 1996 .