PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT
<p><strong><em>Purpose</em></strong><em>: </em><em>The effects of aircraft engine emissions within the planetary boundary layer under the landing/ take-off operations contribute sufficiently to deterioration of air pollution in the vicinity of the airp...
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2016-12-01
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doaj-4949eb6cc93c4142918302931e1b98302020-11-25T03:20:44ZengNational Aviation UniversityVìsnik Nacìonalʹnogo Avìacìjnogo Unìversitetu1813-11662306-14722016-12-01694778810.18372/2306-1472.69.1105910707PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORTOleksandr Zaporozhets0Kateryna Synylo1National Aviation UniversityNational Aviation University<p><strong><em>Purpose</em></strong><em>: </em><em>The effects of aircraft engine emissions within the planetary boundary layer under the landing/ take-off operations contribute sufficiently to deterioration of air pollution in the vicinity of the airports and nearby residential areas. Currently the primary object of airport air quality are the nitrogen oxides and particle matter (PM<sub>10</sub>, PM<sub>2.5</sub> and ultrafine PM) emissions from aircraft engine exhausts as initiators of photochemical smog and regional haze, which may further impact on human health. Analysis of PM emission inventory results at major European airports highlighted on sufficiently high contribution of aircraft engines and APU. The paper aims to summarize the knowledge on particle size distributions, particle effective density, morphology and internal structure of aircraft PM, these properties are critical for understanding of the fate and potential health impact of PM. It also aims to describe the basic methods for calculation of emission and dispersion of PM, produced by aircrafts under the LTO operations. </em><strong><em>Methods</em></strong><em>:</em><em> analytical solution of the atmospheric diffusion equation is used to calculate the maximum PM concentration from point emission source. The PM concentration varies inversely proportional to the wind velocity u<sub>1</sub> and directly proportional to the vertical component of the turbulent exchange coefficient k<sub>1</sub>/u<sub>1</sub>. The evaluation of non-volatile PM concentration includes the size and shape of PM. PolEmiCa calculates the distributions of PM fractions for aircraft and APU exhausts (height of installation was given H=4,5m like for Tupolev-154).</em><em> </em><strong><em>Results:</em></strong><em> The maximum concentration of PM in exhaust from APU is higher and appropriate distance is less than in case for gas. PM<strong> </strong>polydispersity<strong> </strong></em><em>leads to the separation of maximums concentration in space for individual fractions on the wind direction and therefore it contributes to the reduction of maximum total concentration.</em><em> <strong>Discussion</strong>:</em><em>But although the APU has contributed significantly to the emission of aircraft at airports, APU emissions are not certificated by ICAO or any other responsible for that authority.</em><em>It is quite actual task for local air quality to development model and find measurement techniques to identify aircraft engine and APU contribution to total airport PM pollution. </em><em></em></p>http://jrnl.nau.edu.ua/index.php/visnik/article/view/11059air pollutionaircraft engine emissionauxiliary power unitconcentrationemission indexemission inventoryparticle matternon-volatile particlevolatile particleparticle size distribution |
collection |
DOAJ |
language |
English |
format |
Article |
sources |
DOAJ |
author |
Oleksandr Zaporozhets Kateryna Synylo |
spellingShingle |
Oleksandr Zaporozhets Kateryna Synylo PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT Vìsnik Nacìonalʹnogo Avìacìjnogo Unìversitetu air pollution aircraft engine emission auxiliary power unit concentration emission index emission inventory particle matter non-volatile particle volatile particle particle size distribution |
author_facet |
Oleksandr Zaporozhets Kateryna Synylo |
author_sort |
Oleksandr Zaporozhets |
title |
PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT |
title_short |
PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT |
title_full |
PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT |
title_fullStr |
PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT |
title_full_unstemmed |
PM EMISSIONS PRODUCED BY AIRCRAFT UNDER THE OPERATIONS AT THE AIRPORT |
title_sort |
pm emissions produced by aircraft under the operations at the airport |
publisher |
National Aviation University |
series |
Vìsnik Nacìonalʹnogo Avìacìjnogo Unìversitetu |
issn |
1813-1166 2306-1472 |
publishDate |
2016-12-01 |
description |
<p><strong><em>Purpose</em></strong><em>: </em><em>The effects of aircraft engine emissions within the planetary boundary layer under the landing/ take-off operations contribute sufficiently to deterioration of air pollution in the vicinity of the airports and nearby residential areas. Currently the primary object of airport air quality are the nitrogen oxides and particle matter (PM<sub>10</sub>, PM<sub>2.5</sub> and ultrafine PM) emissions from aircraft engine exhausts as initiators of photochemical smog and regional haze, which may further impact on human health. Analysis of PM emission inventory results at major European airports highlighted on sufficiently high contribution of aircraft engines and APU. The paper aims to summarize the knowledge on particle size distributions, particle effective density, morphology and internal structure of aircraft PM, these properties are critical for understanding of the fate and potential health impact of PM. It also aims to describe the basic methods for calculation of emission and dispersion of PM, produced by aircrafts under the LTO operations. </em><strong><em>Methods</em></strong><em>:</em><em> analytical solution of the atmospheric diffusion equation is used to calculate the maximum PM concentration from point emission source. The PM concentration varies inversely proportional to the wind velocity u<sub>1</sub> and directly proportional to the vertical component of the turbulent exchange coefficient k<sub>1</sub>/u<sub>1</sub>. The evaluation of non-volatile PM concentration includes the size and shape of PM. PolEmiCa calculates the distributions of PM fractions for aircraft and APU exhausts (height of installation was given H=4,5m like for Tupolev-154).</em><em> </em><strong><em>Results:</em></strong><em> The maximum concentration of PM in exhaust from APU is higher and appropriate distance is less than in case for gas. PM<strong> </strong>polydispersity<strong> </strong></em><em>leads to the separation of maximums concentration in space for individual fractions on the wind direction and therefore it contributes to the reduction of maximum total concentration.</em><em> <strong>Discussion</strong>:</em><em>But although the APU has contributed significantly to the emission of aircraft at airports, APU emissions are not certificated by ICAO or any other responsible for that authority.</em><em>It is quite actual task for local air quality to development model and find measurement techniques to identify aircraft engine and APU contribution to total airport PM pollution. </em><em></em></p> |
topic |
air pollution aircraft engine emission auxiliary power unit concentration emission index emission inventory particle matter non-volatile particle volatile particle particle size distribution |
url |
http://jrnl.nau.edu.ua/index.php/visnik/article/view/11059 |
work_keys_str_mv |
AT oleksandrzaporozhets pmemissionsproducedbyaircraftundertheoperationsattheairport AT katerynasynylo pmemissionsproducedbyaircraftundertheoperationsattheairport |
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