EMISSION CHARACTERISTICS OF GASEOUS POLLUTANTS AND PARTICULATE MATTER FROM A SMALL TURBOFAN ENGINE UNDER MULTIPLE OPERATING CONDITIONS
-
摘要: DGEN380发动机作为专为喷气式公务机设计的小型涡扇发动机,其气态污染物和颗粒物的排放特性值得探究。于2023年12月23日测试了该发动机在多种工况条件(包括10%、30%和45%推力)下的运行情况。结果显示:1)随着推力的增加,NO和NOx的排放因子显著增加,而NO2和CO的排放因子则呈降低趋势。10%推力下颗粒物的粒径整体呈双峰分布,在20,100 nm处达到峰值,且其总数量浓度为30%和45%推力下的3.4~3.9倍。不同粒径段颗粒物组分中,Na、Mg、Fe、S和Cu元素的排放因子较高,其总和在不同推力下占比均超过80%。碳质组分中有机碳3(OC3)占比最高(25.67%~56.56%),其含量随发动机推力变化而变化;而元素碳(EC)含量在各推力下均较为稳定。3)离子组分以SO2-4、NO-3和Cl-为主,在各推力下的平均排放因子为0.24~1.60 mg/kg。4)通过对污染物排放浓度与发动机参数进行逐步回归分析发现,CO排放的主要影响因素是燃烧室进口平均温度,NO和NOx排放浓度与滑油流量呈正相关,而颗粒物排放与燃烧室进口平均温度及进口压强均呈负相关。研究结果为喷气式公务机污染物排放特征评估提供数据基础,为通航机场大气污染防治提供参考。Abstract: The DGEN380 engine was chosen as a representative turbofan engine for jet business aircrafts, and the emission characteristics of gaseous pollutants and particulate matter from this engine were tested on December 23, 2023, at multiple operating conditions (including three operating conditions at a thrust level of 10%, 30%, and 45%). The results indicated that 1) NO and NOx emission factors increased significantly with increasing thrust level, while the emission factors of NO2 and CO showed a decreasing trend. Under the 10% thrust condition, the particle size distribution of particulate matter exhibited a bimodal pattern, with two peaks at 20 nm and 100 nm. The total number concentration of particles was found to be 3.4 to 3.9 times higher than that under 30% and 45% thrust conditions. 2) Further analysis of the composition of particulate matter fractions in different size ranges revealed high emission factors for Na, Mg, Fe, S, and Cu elements in the particulate matter. These elements accounted for more than 80% of the total composition at various thrust levels. The organic carbon component had the highest proportion as OC3 (25.67% to 56.56%), which varied significantly with engine thrust level; meanwhile, elemental carbon (EC) content remained relatively stable across all thrust levels. 3) Ionic components were predominantly composed of SO2-4, NO-3, and Cl-, with average emission factors ranging from 0.24 mg/kg to 1.60 mg/kg across all three thrust levels. 4) A stepwise regression analysis linking pollutant emissions concentrations to engine parameters revealed that average combustion chamber inlet temperature was a key factor influencing CO emissions; NO and NOx emission concentrations were positively correlated with lube oil flow rate; while particulate matter emissions showed a negative correlation with both average combustion chamber inlet temperature and inlet pressure. These findings can provide effective data for assessing pollutant emission characteristics in jet business aircraft, and offer scientific insights for preventing and controlling air pollution at airports serving such aircrafts.
-
[1] 袁远, 吴琳, 邹超, 等. 天津机场飞机污染排放及其特征研究[J]. 环境工程, 2018, 36(9): 81-86,58. [2] YU J L, SHAO C F, XUE C Y, et al. China’s aircraft-related CO2 emissions: decomposition analysis, decoupling status, and future trends[J]. Energy Policy, 2020, 138: 111215. [3] 韩博, 石依琳, 纪翔, 等. 典型通航飞机PM与TVOC排放特征及排放因子[J]. 中国环境科学, 2023, 43 (4): 1550-1557. [4] DURDINA L, BREM B T, SCHÖNENBERGER D, et al. Nonvolatile particulate matter emissions of a business jet measured at ground level and estimated for cruising altitudes[J]. Environmental Science & Technology, 2019, 53(21): 12865-12872. [5] HU S, FRUIN S, KOZAWA K, et al. Aircraft emission impacts in a neighborhood adjacent to a general aviation airport in Southern California[J]. Environmental Science & Technology, 2009, 43(21): 8039-8045. [6] CHEN L F, LIANG Z R, LIU H Y, et al. Sensitivity analysis of fuel types and operational parameters on the particulate matter emissions from an aviation piston engine burning heavy fuels[J]. Fuel, 2017, 202: 520-528. [7] 盛久江, 王飞, 李霞,等. 涡桨飞机 VOCs 排放特征的质子迁移反应飞行时间质谱 (PTR-TOF-MS)分析[J]. 环境科学学报, 2021, 41(5): 1784-1791. [8] YU Z H, LISCINSKY D S, FORTNER E C, et al. Evaluation of PM emissions from two in-service gas turbine general aviation aircraft engines[J]. Atmospheric Environment, 2017, 160: 9-18. [9] TRAN S, BROWN A, OLFERT J S. Comparison of particle number emissions from in-flight aircraft Fueled with Jet A1, JP-5 and an alcohol-to-jet fuel blend[J]. Energy & Fuels, 2020, 34(6): 7218-7222. [10] BENAVIDES A, BENJUMEA P, CORTÉS F B, et al. Chemical composition and low-temperature fluidity properties of jet fuels[J]. Processes, 2021, 9(7): 1184. [11] International Civil Aviation Organization (ICAO). Annex 16-Environmental Protection-Volume Ⅱ-Aircraft Engine Emissions[J]. Montr é al:International Civil Aviation Organization,2017. [12] 张子祎, 刘保双, 孟赫, 等. 青岛市港口区域PM2.5污染特征及来源解析研究[J]. 环境科学学报, 2022, 42(11): 293-307. [13] BASHTANI J, SEDDIGHI S, BAHRABADI-Jovein I. Control of nitrogen oxide formation in power generation using modified reaction kinetics and mixing[J]. Energy, 2018, 145: 567-581. [14] TANBAY T, UCA M B, DURMAYAZ A. Assessment of NO<em>x emissions of the Scimitar engine at Mach 5 based on a thermodynamic cycle analysis[J]. International Journal of Hydrogen Energy, 2020, 45(5): 3632-3640. [15] CERINSKI D, VUJANOVIC M, PETRANOVIC Z, et al. Numerical analysis of fuel injection configuration on nitrogen oxides formation in a jet engine combustion chamber[J]. Energy Conversion and Management, 2020, 220: 112862. [16] International Civil Aviation Organization (ICAO). ICAO aircraft engine emissions databank[EB/OL].2021,https://www.easa.europa.eu/domains/environment/icao-aircraft-engine-emissions-databank. [17] IODICE P, SENATORE A, LANGELLA G, et al. Effect of ethanol-gasoline blends on CO and HC emissions in last generation SI engines within the cold-start transient: an experimental investigation[J]. Applied Energy, 2016, 179: 182-190. [18] KINSEY J S, DONG Y J, WILLIAMS DC, et al. Physical characterization of the fine particle emissions from commercial aircraft engines during the Aircraft Particle Emissions eXperiment (APEX) 1-3[J]. Atmospheric Environment, 2010, 44(17): 2147-2156. [19] DELHAYE D, OUF F X, FERRY D, et al. The MERMOSE project: characterization of particulate matter emissions of a commercial aircraft engine[J]. Journal of Aerosol Science, 2017, 105: 48-63. [20] LIANG Z R, YU Z H, ZHANG C, et al. IVOC/SVOC and size distribution characteristics of particulate matter emissions from a modern aero-engine combustor in different operational modes[J]. Fuel, 2022, 314: 122781. [21] KINSEY J S, TIMKO M T, HERNDON S C, et al. Determination of the emissions from an aircraft auxiliary power unit (APU) during the Alternative Aviation Fuel Experiment (AAFEX)[J]. Journal of the Air & Waste Management Association, 2012, 62(4): 420-430. [22] SCHRIPP T, ANDERSON B E, BAUDER U, et al. Aircraft engine particulate matter emissions from sustainable aviation fuels: results from ground-based measurements during the NASA/DLR campaign ECLIF2/ND-MAX[J]. Fuel, 2022, 325: 124764. [23] DURDINA L, BREM B T, SETYAN A, et al. Assessment of particle pollution from jetliners: from smoke visibility to nanoparticle counting[J]. Environmental Science & Technology, 2017, 51(6): 3534-3541. [24] CORBIN J C, MENSAH A A, PIEBER S M, et al. Trace metals in soot and PM2.5 from heavy-fuel-oil combustion in a marine engine[J]. Environmental Science & Technology, 2018, 52(11): 6714-6722. [25] TURGUT E T, AÇIKEL G, GAGA E O, et al. A comprehensive characterization of particulate matter, trace elements, and gaseous emissions of piston-engine aircraft[J]. Environmental Science & Technology, 2020, 54(13): 7818-7835. [26] PIERCE D, HAYNES A, HUGHES J, et al. High temperature materials for heavy duty diesel engines: historical and future trends[J]. Progress in Materials Science, 2019, 103: 109-179. [27] KINSEY J S, HAYS M D, DONG Y, et al. Chemical characterization of the fine particle emissions from commercial aircraft engines during the aircraft particle emissions experiment (APEX) 1 to 3[J]. Environmental Science & Technology, 2011, 45(8): 3415-3421. [28] DUAN J C, TAN J H, WANG S L, et al. Roadside, urban, and rural comparison of size distribution characteristics of PAHs and carbonaceous components of Beijing, China[J]. Journal of Atmospheric Chemistry, 2012, 69(4): 337-349. [29] 沈嵩, 刘蕾, 温维, 等. 北京及周边地区夏季PM2.5中含碳组分污染特征与来源解析[J]. 环境工程, 2022, 40(2): 71-80. [30] WATSON J G, CHOW J C, LOWENTHAL D H, et al. Differences in the carbon composition of source profiles for diesel-and gasoline-powered vehicles[J]. 1994, 28(15): 2493-2505. [31] 王成, 曹靖原, 段小琳, 等. 山西省四城市冬季PM2.5中碳质组分特征及来源分析[J]. 环境工程, 2021, 39(6): 114-121. [32] JI D S, ZHANG J K, HE J, et al. Characteristics of atmospheric organic and elemental carbon aerosols in urban Beijing, China[J]. Atmospheric Environment, 2016, 125: 293-306. [33] YAN C Q, ZHENG M, SHEN G F, et al. Characterization of carbon fractions in carbonaceous aerosols from typical fossil fuel combustion sources[J]. Fuel, 2019, 254: 115620. [34] HAN Y, CHEN Y J, AHMAD S, et al. High time- and size-resolved measurements of PM and chemical composition from coal combustion: implications for the EC formation process[J]. Environmental Science & Technology, 2018, 52(11): 6676-6685. [35] 韩博, 姚婷玮, 王立婕, 等. 天津机场区域大气NO2及O3影响因子研究[J]. 中国环境科学, 2020, 40(6): 2398-2408. [36] BIAN H S, CHIN M, HAUGLUSTAINE D A, et al. Investigation of global particulate nitrate from the AeroCom phase Ⅲ experiment[J]. Atmospheric Chemistry and Physics, 2017, 17(21): 12911-12940.
点击查看大图
计量
- 文章访问数: 12
- HTML全文浏览量: 3
- PDF下载量: 0
- 被引次数: 0