Emission factor estimates of cereal waste burning in Spain

Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire with intense flames are similar to those of the African dry savanna heading fires. This paper surveys the atmospheric emission caused by this...

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Published inAtmospheric environment (1994) Vol. 34; no. 19; pp. 3183 - 3193
Main Authors Ortiz de Zárate, I., Ezcurra, A., Lacaux, J.P., Van Dinh, Pham
Format Journal Article
LanguageEnglish
Published Elsevier Ltd 2000
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Abstract Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire with intense flames are similar to those of the African dry savanna heading fires. This paper surveys the atmospheric emission caused by this process by combining results of field and combustion chamber experiments. Combustion chamber experiments show that during the flaming phase 88% of the fire exposed carbon is converted into CO 2 and during the smoldering phase this percentage changes to 74%. These combustion chamber experiments also show that the soluble part of the aerosols emitted during the course of fires only represent 3% of the total particulate matter (TPM) produced, being the ions K + and CI − the predominant ones. The cereal waste fire process can be represented by an arithmetic combination that takes into account the amounts of mass burned during the two phases of the fire: 0.90 flaming +0.10 smoldering. Emission factor estimates from field burning experiment are 13±7 g TPM kg −1(dm) and 2.8±0.2 g NO x kg −1 (dm). Finally, we obtain average emissions of 80–130 Gg TPM, 17–28 Gg NO x , 210–350 Gg CO and 8–14 Tg CO 2 in Spain. These emissions represent nearly 25% of the total NO x and 50% of the total CO 2 emissions by other pollution sources during the burning period in Spain.
AbstractList Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire with intense flames are similar to those of the African dry savanna heading fires. This paper surveys the atmospheric emission caused by this process by combining results of field and combustion chamber experiments. Combustion chamber experiments show that during the flaming phase 88% of the fire exposed carbon is converted into CO sub(2) and during the smoldering phase this percentage changes to 74%. These combustion chamber experiments also show that the soluble part of the aerosols emitted during the course of fires only represent 3% of the total particulate matter (TPM) produced, being the ions K super(+) and Cl super(-) the predominant ones. The cereal waste fire process can be represented by an arithmetic combination that takes into account the amounts of mass burned during the two phases of the fire: 0.90 flaming + 0.10 smoldering. Emission factor estimates from field burning experiment are 13 plus or minus 7 g TPM kg super(-) super(1) (dm) and 2.8 plus or minus 0.2 g NO sub(x) kg super(-) super(1) (dm). Finally, we obtain average emissions of 80-130 Gg TPM, 17-28 Gg NO sub(x) , 210-350 Gg CO and 8-14 Tg CO sub(2) in Spain. These emissions represent nearly 25% of the total NO sub(x) and 50% of the total CO sub(2) emissions by other pollution sources during the burning period in Spain.
Farmers in Spain prefer to burn the straw and stubble that remain in agricultural fields following harvest. Results are presented from an experimental evaluation of the cereal-waste-burning emission factors, which combined field and chamber experiments. The composition of fuels was determined by an elemental analyzer, and two distinctly different fire regimes were considered: flaming and smoldering. Combustion efficiency was deduced from carbon monoxide emission ratios. Results indicate that, during the flaming phase, 88% of the C was converted to carbon dioxide and only 3% was converted to CO. Under smoldering conditions, CO sub(2) production was reduced to 77%, while CO production increased to 17%. The burning of 1 kg of cereal waste was determined to release 1400, 35, 3, and 13 g of CO sub(2), CO, nitrogen oxides, and total particulate matter, respectively, and to release 220, 800, and 320 mg of formic acid, acetic acid, and propionic acid, respectively. For all of Spain, annual cereal-burning emissions were calculated to range 80 130 Gg, 17 28 Gg, 210 350 Gg, and 8 14 Tg of total particulate matter, NO sub(x), CO, and CO sub(2), respectively.
Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire with intense flames are similar to those of the African dry savanna heading fires. This paper surveys the atmospheric emission caused by this process by combining results of field and combustion chamber experiments. Combustion chamber experiments show that during the flaming phase 88% of the fire exposed carbon is converted into CO sub(2) and during the smoldering phase this percentage changes to 74%. These combustion chamber experiments also show that the soluble part of the aerosols emitted during the course of fires only represent 3% of the total particulate matter (TPM) produced, being the ions K super(+) and CI super(-) the predominant ones. The cereal waste fire process can be represented by an arithmetic combination that takes into account the amounts of mass burned during the two phases of the fire: 0.90 flaming +0.10 smoldering. Emission factor estimates from field burning experiment are 13 plus or minus 7 g TPM kg super(-1)(dm) and 2.8 plus or minus 0.2 g NO sub(x) kg super(-1) (dm). Finally, we obtain average emissions of 80-130 Gg TPM, 17-28 Gg NO sub(x), 210-350 Gg CO and 8-14 Tg CO sub(2) in Spain. These emissions represent nearly 25% of the total NO sub(x) and 50% of the total CO sub(2) emissions by other pollution sources during the burning period in Spain.
Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire with intense flames are similar to those of the African dry savanna heading fires. This paper surveys the atmospheric emission caused by this process by combining results of field and combustion chamber experiments. Combustion chamber experiments show that during the flaming phase 88% of the fire exposed carbon is converted into CO 2 and during the smoldering phase this percentage changes to 74%. These combustion chamber experiments also show that the soluble part of the aerosols emitted during the course of fires only represent 3% of the total particulate matter (TPM) produced, being the ions K + and CI − the predominant ones. The cereal waste fire process can be represented by an arithmetic combination that takes into account the amounts of mass burned during the two phases of the fire: 0.90 flaming +0.10 smoldering. Emission factor estimates from field burning experiment are 13±7 g TPM kg −1(dm) and 2.8±0.2 g NO x kg −1 (dm). Finally, we obtain average emissions of 80–130 Gg TPM, 17–28 Gg NO x , 210–350 Gg CO and 8–14 Tg CO 2 in Spain. These emissions represent nearly 25% of the total NO x and 50% of the total CO 2 emissions by other pollution sources during the burning period in Spain.
Author Van Dinh, Pham
Ezcurra, A.
Lacaux, J.P.
Ortiz de Zárate, I.
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Keywords Combustion chamber experiment
Gases and particle emissions
Cereal waste in Spain
Biomass burning
Field burning
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Snippet Every year more than 5 million ha of cereal fields are affected by fires in order to eliminate cereal waste in Spain. The characteristics of this type of fire...
Farmers in Spain prefer to burn the straw and stubble that remain in agricultural fields following harvest. Results are presented from an experimental...
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StartPage 3183
SubjectTerms Biomass burning
Cereal waste in Spain
Combustion chamber experiment
Field burning
Gases and particle emissions
Spain
Title Emission factor estimates of cereal waste burning in Spain
URI https://dx.doi.org/10.1016/S1352-2310(99)00254-X
https://search.proquest.com/docview/14546704
https://search.proquest.com/docview/17684787
https://search.proquest.com/docview/18084567
Volume 34
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