The calculation method of aviation emissions based on time spent in various modes in LTO cycles was improved. The effective emission height was calculated based on AMDAR data, instead of using the height (915m) proposed by ICAO. Then, the total amount of atmospheric pollutant emissions from aviation was estimated accurately. The total emissions of NOx, CO, HC, SO2 and PM2.5 from aviation in Beijing Capital International Airport (BCIA) were about 7042.1, 3189.9, 295.3, 429.4 and 150.4t, respectively. As compared with the traditional method based on LTO cycles, the result estimated with the improved method revealed that emissions of NOx, CO, HC and SO2 had increased by 23.5%, 2.3%, 2.1% and 18.1%, severally. Monthly emissions of CO, HC, SO2 and PM2.5 from aircraft in BCIA presented a relatively steady trend, but NOx was fluctuated on a large scale. Emissions from aviation were lower in January to February; and monthly emission was peaked in August. Moreover, as for different operation modes, the climbing and taxiing course were found with the largest emission. Approximately 37.7% and 36.8% of the total aircraft emissions were produced in climbing and taxiing, respectively.
Zang H S, Ki H K, Sang K S. Long-term trend in NO2 and NOx levels and their emission ratio in relation to road traffic activities in East Asia[J]. Atmospheric Environment, 2011,45(18):3120-3131.
Isaksen I S A, Stordal F, Berntsen T. Model Studies of Effects of Highflying Supersonic Commercial Transport on Stratospheric and Tropospheric Ozone[R]. Report no. 76, Institute of Geophysics, University of Oslo, Norway, 1989.
[5]
Lee D S, Fahey D W, Forster P M, et al. Aviation and global climate change in the 21st century[J]. Atmospheric Environment, 2009,43(22/23):3520-3537.
[6]
Fan W Y, Sun Y F, Zhu T L, et al. Emissions of HC, CO, NOx, CO2, and SO2 from civil aviation in China in 2010[J]. Atmospheric Environment, 2012(3),56:52-57.
The Environment Branch of the International Civil Aviation Organization (ICAO). ICAO Environmental Report 2013[R]. International Civil Aviation Organization, 2014.
Stettler M E J, Eastham S, Barrett S R H. Air quality and public health impacts of UK airports. Part I: Emissions[J]. Atmospheric Environment, 2011,45(31):5415-5424.
[14]
Song S K, Shon Z H. Emissions of greenhouse gases and air pollutants from commercial aircraft at international airports in Korea[J]. Atmospheric Environment, 2012,61(7):148-158.
[15]
Morten W, Uffe K, Thomas E, et al. Emissions of NOx, particle mass and particle numbers from aircraft main engines, APU's and handing equipment at Copenhagen Airport[J]. Atmospheric Environment, 2015,100:148-158.
[16]
Schürmann G, Schäfer K, Jahn C, et al. The impact of NOx, CO and VOC emissions on the air quality of Zurich airport[J]. Atmospheric Environment, 2007,41(1):103-118.
[17]
Kesgin U. Aircraft emissions at Turkish airports[J]. Energy, 2006,31(2/3):372-384.
Davies F, Middleton D R, Bozier K E. Urban air pollution modeling and measurements of boundary layer height[J]. Atmospheric Environment, 2007,41(19):4040-4049.
Kalivoda M T, Kudrna M. Methodologies for estimating emissions from air traffic: future emissions[R]. MEET Project ST-96-SC, 1997,204,Vienna, Austria: Perchtoldsdorf-Vienna, 46-53.
Unal A, Hu Y T, Chang M E, et al. Airport related emissions and impacts on air quality: Application to the Atlanta International Airport[J]. Atmospheric Environment, 2005,39(32):5787-5798.