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AIR5715
Procedure for the Calculation of Aircraft Emissions
Procedure for the Calculation of Aircraft Emissions
有效
【范围】 This AIR describes procedures for calculating emissions resulting from the main engines of commercial jet and turboprop aircraft through all modes of operation for all segments of a flight. Piston engine aircraft emissions are not included in this AIR. Some information about piston engine aircraft emissions can be found in FOCA 2007. The principal purpose of the procedures is to assist model developers in calculating aircraft emissions in a consistent and accurate manner that can be used to address various environmental assessments including those related to policy decisions and regulatory requirements. The pollutants considered in this document are: Nitrogen Oxides (NOx) Carbon Monoxide (CO) Total unburned Hydrocarbons (THC) Carbon Dioxide (CO 2 ) Water (H 2 O) Sulfur Oxides (SOx) Volatile Organic Compounds (VOC) Methane (CH 4 ) Non-Methane Hydrocarbons (NMHC) Non-Methane Volatile Organic Compounds (NMVOC) Nitrous Oxide (N 2 O) Particulate Matter (PM 2.5 and PM 10 ) As indicated above, hazardous air pollutants (HAPs) are not individually accounted for; many of these are simply included as part of THC. Also, trace metals are not included other than those that may already be accounted for as part of PM emissions. Since the scope is limited to aircraft engine emissions only, emissions from Ground Service Equipment (GSE), roadway vehicles, power plants, training fires, etc., are not included within this document. Athough Auxilliary Power Units (APU), brakes, and tires are also part of the aircraft, their emissions (e.g., tire wear) are not within the scope of this document. The methods are based on aircraft performance and emissions modeling. This means that only the pollutants exiting the exhaust of an engine are considered. Any atmospheric effects including those that occur in the near-field (e.g., exhaust plume) and the subsequent atmospheric dispersion are not modeled. The exception to this is in the computation of PM emissions. In meeting the needs of modelers who may have varying fidelity requirements for both emissions and aircraft performance modeling, this document does not try to promote a single database and methodology. Therefore, several methods have been included in this document as indicated below with the emissions methods categorized by pollutants: Emissions Modeling Methods o NOx, CO, and THC P3T3 Boeing Fuel Flow Method 2 (BFFM2) Deutsche Forschungsanstalt fur Luft- and Raumfahrt (DLR) Method International Civil Aviation Organization (ICAO) Reference Method o CO 2 , H 2 O, and SOx Fuel Composition Method (FCM) o VOC, NMVOC, CH 4 and NMTHC Derivative Factor Method (DFM) o N 2 O Approximate Factor Method (AFM) o PM 2.5 and PM 10 First Order Approximation (FOA) Aircraft Performance Methods o Aircraft performance data from flight data recorders o Manufacturer aircraft performance models o SAE AIR 1845 combined with Eurocontrol’s Base of Aircraft Data (BADA) o Eurocontrol’s BADA o Other aircraft performance models such as the Project Interactive Analysis and Optimisation (PIANO) tool Both of these sets of emissions and aircraft performance methods are listed in the order in which they are presented in this document. And as previously indicated, the order generally denotes the level of accuracy where the first method in each section represents the most accurate method based on current understanding. The exceptions to this are: Emissions Methods BFFM2 DLR Aircraft Performance SAE 1845 + BADA BADA The ordering of these methods are arbitrary since they are considered comparable (e.g., BFFM2 is comparable to DLR). One other possible exception is the last listing under aircraft performance methods (“Other aircraft performance models”). The data from these other sources may be more accurate, comparable, or less accurate than the previously mentioned methods. This last category was added to include all other methods that were not based on manufacturer, SAE 1845, and BADA models. In order to provide a better understanding of the relative condition of these methods, they have been defined into development status (i.e., “mature” or “developing”) and fidelity (i.e., “simple,” “intermediate,” or “advanced”) categories as presented in Table 1. {6b471cdc315997b0498e6b8f33dde7a3.jpg} The “other” aircraft model category was not included in Table 1 since it is understood that it can be listed in any of the categories depending on which method/model is employed. The definitions for each of the categories are as follows: Simple: This category represents the lowest complexity in terms of data requirements and computational procedures. The results generated from methods within this category are also considered to be the least accurate. Intermediate: This category represents a middle-tier complexity in terms of data requirements and computational procedures. The results generated from methods within this category are also considered to be of middle-tier. Advanced: This category represents the highest complexity in terms of data requirements and procedures. The results generated from methods within this category are also considered to be the most accurate. Mature: Methods within this category are considered to be well-established. They have been used extensively in past studies and may have been validated to a certain extent. Developing: Methods within this category are not considered to be well-established. The methods are still being assessed and are considered to be evolving. In modeling aircraft performance and emissions, the main focus is on a single flight. This includes the complete operation and movement of the aircraft from gate-to-gate: Main engine start-up Ground taxi-out and delay activities Takeoff: Runway roll Takeoff: Initial ascent Climbout En route/cruise Airborne delay activities Approach Landing roll Thrust reverser Ground taxi-in and delay activities Engine shut-down For modeling purposes, these modes can generally be simplified so that they are equated to one of the four LTO modes. Depending on the method, the actual modeling of the gate-to-gate movement may involve a segment-by-segment approach where results can be integrated to obtain totals by mode and flight. Currently, the AIR does not address emissions during engine start-up and shut-down activities. Also, thrust reverse operations are not directly covered in this AIR.strRefField
【与前一版的变化】

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包含图表

TABLE 1 - CATEGORIZA
P3T3 METHODOLOGY OF
FORMULA 1
HUMIDITY CORRECTION
ICAO DATA FOR TRENT
ASSUMED THERMODYNAMI
FORMULA w1
FORMULA w2
FORMULA w3
NOX, CO, AND THC EMI
ADJUSTMENT FACTORS F
EXAMPLE LOG-LOG PLOT
NON-STANDARD DATA BE
ADDITIONAL METHODS T
FORMULA 2
FORMULA 3
FORMULA 4
FORMULA 5
FORMULA 6
FORMULA 7
FORMULA 8
FORMULA 9
FORMULA 10
ICAO DATA FOR TRENT
FUEL FLOW ADJUSTMENT
LOG OF REFERENCE EIN
LOG REFERENCE EICO V
LOG OF REFERENCE EIT
FORMULA w4
FORMULA w5
FORMULA w6
NOX EMISSIONS COMPUT
CO AND THC EMISSIONS
FORMULA 11
FORMULA 12
FORMULA 13
FORMULA 14
FORMULA 15
FORMULA 16
FORMULA 16
EXAMPLE NOX EI VERSU
FORMULA 17
FORMULA 18
EXAMPLE PLOT OF EI V
FORMULA 19
SECOND ORDER POLYNOM
ASSUMED COMBUSTOR IN
FORMULA w7
FORMULA w8
REFERENCE EICO VERSU
REFERENCE EITHC VERS
FORMULA w9
FORMULA w10
FORMULA w11
NOX, CO, AND THC EMI
DEFINITION OF LTO MO
LTO CYCLE
FORMULA 20
ICAO DEFAULT TIM DAT
FORMULA 21
ICAO DATA FOR TRENT
CO2, H2O, AND SOX EM
FORMULA 22
FORMULA 23-28
EXAMPLE EI DATA FOR
FORMULA 29
FORMULA w12
FORMULA w13
VOC, NMVOC, CH4AND N
FORMULA 30
DERIVATIVE FACTORS
FORMULA 31-32
FORMULA 31-32
FORMULA 33
FORMULA 34
N2O EMISSIONS COMPUT
FORMULA 35
PM EMISSIONS COMPUTA
FORMULA 36-38
FORMULA 39
FORMULA 40
PM EI DUE TO VOLATIL
SURROGATE THC EI DAT
FORMULA 41
FORMULA 42
FORMULA 43
FORMULA 44
FORMULA 45
AVERAGE AIR-TO-FUEL
FORMULA 46
FORMULA 47
FORMULA 48
SUGGESTED SF VALUES
ICAO DATA FOR JT8D-2
FORMULA w14
FORMULA w15
FORMULA c1
FORMULA c2
FORMULA c3
FORMULA c4

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