99 Emissions from aircraft and handling equipment in Copenhagen

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DEPARTMENT OF ENVIRONMENTAL SCIENCE

AARHUS UNIVERSITY

Emissions from Aircraft and Handling

Equipment in Copenhagen Airport

19th International Transport and Air Pollution conference

November 26-27, 2012

Thessaloniki, Greece

M. Winther, U. Kousgaard, T. Ellermann, M.

Ketzel, P. Løfstrøm, A. Massling, J.K. Nøjgaard

Department of Environmental Science, Aarhus University

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Introduction

Morten Winther Senior adviser 27. november 2012

› Arising from the concern of airport workers health, a detailed investigation of the air pollution in Copenhagen Airport has been conducted in 2009-2011.

› Main focus was the airport apron area where handling occurs.

› The airport study as such comprises a detailed baseline emission inventory as well as subsequent dispersion modeling of the air quality (Ellermann et al., 2011).

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Introduction

Morten Winther Senior adviser 27. november 2012

› This presentation explains the detailed baseline emission inventory for aircraft main engines, auxiliary power units (APU) and handling equipment.

› Total emission results of CO, HC, NO x and PM will shown for the apron area in focus and the airport as a whole.

› PM results for the apron (5m x 5m) will also be shown suited for the further dispersion modelling work.

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Disposition

Morten Winther Senior adviser

› Activity data - and digitization

› Aircraft movements

› APU (Auxiliary Power Unit)

› Main engine start-up

› Handling equipment

› Road transport vehicles

› Emission factors

› Calculation method

› Results

› Conclusions

27. november 2012

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Digitization – aircraft movements

AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

Aircraft movements digitized from airport data: Flight operation (Start/landing) and time, lane (04L+04R, 22L+22R, 12, 30), taxi way, gate no., on/off-block time

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AARHUS UNIVERSITY Morten Winther Senior adviser

Digitization – APU, push-back and main engine start-up

27. november 2012

• APU (arrival, start-up, boarding):

Gate no., On/Off-block time.

• APU and push-back along the green/red lines (5 km/h).

• APU and main engine start-up by the start-up mark (red dot; e.g. P).

APU condition →

APU load →

2 engine aircraft

Arrival APU Start Boarding

Normal Start-up Normal

300 s 180 s 216 s

4 engine aircraft 300 s 180 s 318 s

Source: ICAO Airport Air Quality Guidance Manual (doc. 9889)

During push-back

Normal

Calculated

Calculated

Main engine start

High

35 s

140 s

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

Aircraft category →

Handling period (min) →

Equipment type

Arrival

B C D E B

15 20 30 40 15

Working time (min)

Baggage truck

Conveyor belt

Push-back at gate

Push-back moving

Container loader

Container transporter

Fuel (dispenser truck)

Fuel (refuelling truck)

Cleaning highloader

Cargo/Post tractor

Toilet truck

Catering B/C/D/E

9

10

0

0

0

0

10

10

0

0

0

1

10 15 25 9

20 20 20 10

0

0

0

0

0 10

0 0

15 27.5 35 0

15 27.5 35 0

15 30 50 a

0

15 30 50 a

0

0

5

10 15 0

5 5 0

0

3

0

5

0

5

Water truck 0 0 0 0

• Aircraft are grouped into four size categories (B-E).

0

0

0

• Arrival: Handling starts immediately after on-block at the gate.

Departure

C D

20 30

Working time (min)

E

40

10 15

20 20

10 10

0 0

15 27.5

15 27.5

0

0

0

5

0

0

10

5

10 20

0 0

7,5 15

0

0

15

5

20

0

15

25

20

10

0

35

35

Load factor

0.15

0.15

0.15

0.75

0.45

0.35

0.1

0.1

0.45

0.15

0.25

0.1/0.2/0.22/0.22

0,25

• Departure: Handling ends immediately before off-block at the gate.

• Handling equipment list from the handling companies: Fuel type, engine size, emission stage/year.

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Digitization - handling

Morten Winther Senior adviser 27. november 2012

› Handling occur on the right side of the aircraft. Area: Aircraft x wing length

› The working time is increased to cover the full handling period (handling table); emission rates are decreased correspondingly

› An exception for push-back; 10 mins before off-block, and movement towards the engine start up mark

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

Emission factors – aircraft main engines

› Main engines: flyID (airport) → engineID (global database)

› NO x

, CO, HC (g/kg fuel), smoke no., fuel (kg/s): Idle, take off

› Jet engines: ICAO engine exhaust emission database

› Turbo props (TP): FOI Sweden emission database

› Particulate matter (PM): ICAO’s FOA3.0 method (jets), and from a Swiss survey (TP)

› PM mass depends on smoke number, fuel sulphur and HC

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AARHUS UNIVERSITY Morten Winther Senior adviser

Emission factors – aircraft APU

27. november 2012

› APU

› NO x

, CO, HC and PM (kg/h): ICAO (air quality manual, doc. 9889)

› Fuel (kg/h): Lasport (German air quality model for airports)

› New/older aircraft types and seating capacity

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

Emission factors – handling equipment

• Non road diesel: Split into emission levels and kW sizes according to EU emission directives.

• Non road emission data: EMEP/EEA guidebook.

• Road diesel: EU emission limits for Euro 0-V are used directly (Test cycle, ESC).

• Gasoline (baggage truck): Old ones ~ gasoline cars from 1970 ’s. New ones ~ Euro 1 cars.

Fuel type Legislation Emission level

Diesel Non road <1981

Diesel

Diesel

Diesel

Diesel

Non road

Non road

Non road

Non road

1981-1990

1991-Stage I

Stage I

Stage II

Diesel

Diesel

Diesel

Diesel

Non road

Non road

Non road

Road

Stage IIIA

Stage IIIB

Stage IV

Euro 0

Diesel

Diesel

Diesel

Diesel

Diesel

Road

Road

Road

Road

Road

Euro I

Euro II

Euro III

Euro IV

Euro V

Gasoline

Gasoline

Road

Road

ECE 15/00-01 (> 2l.)

Euro 1 (> 2l.)

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Calculation method

Morten Winther Senior adviser 27. november 2012

› The emissions are calculated as the product of the emission rate

(g/s) and time duration spend in cell i, for the activity:

E ( t , i )

ER

  t ( t , i )

∆E = Emission/fuel consumption (g) for cell = i and time = t

ER = Emission/fuel consumption rate (g/s) for ME, APU, ME start up and handling gear

∆t = Time duration for the activity in cell = i t = Time of the day (sec.)

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PM – handling activities

Morten Winther Senior adviser 27. november 2012

• The emission contributions from handling are clearly visible on the right side of the aircraft.

• The emission trails from push-back tractors are visible by the most inner part of the gates, and during the movement towards the main engine start-up marks.

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PM – APU activities

Morten Winther Senior adviser 27. november 2012

• APU emissions are visible at the gates, during push-back to ME start-up marks, and during ME start-up.

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PM – Main engines

Morten Winther Senior adviser 27. november 2012

• The map clearly depicts the ME emissions from the start-up marks, on the taxi ways towards the runways, and close to the gates moving into aircraft parking position.

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PM – all sources

Morten Winther Senior adviser 27. november 2012

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Inner apron: NO x and PM emission shares are significantly high for handling and APU.

Handling: High fuel related emission factors for the diesel fueled handling equipment.

APU: Somewhat lower emission factors, but large fuel consumption.

• ME: NO x and PM emissions are small due to the very small emission factors during taxiing.

• ME: Large amounts of HC and CO while taxiing and during engine start-up due to poor combustion.

• Total airport: ME HC and CO emissions are high.

During take off the emissions of NO x are high due to the high engine combustion temperature.

Apron emission distribution - Copenhagen Airport

100%

90%

80%

70%

60%

50%

40%

30%

20%

10%

0%

HC CO NOx PM Fuel

Main engines

Handling

APU

Morten Winther Senior adviser 27. november 2012

100%

90%

80%

70%

60%

50%

40%

30%

20%

10%

0%

HC

Total emission distribution - Copenhagen Airport

CO NOx PM Fuel

Main engines

Handling

APU

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AARHUS UNIVERSITY Morten Winther Senior adviser

Total PM emissions/day - Copenhagen Airport

18

16

14

12

10

8

2

0

6

4

Road transport APU Handling Main engines

S: 942 ppm

Main engines

S: 0 ppm

27. november 2012

• JP sulphur content = 942 ppm, according to information from airport refueling services.

• The calculated PM emissions from main engines decrease by more than 50 %, in the case of zero sulphur in the jet fuel.

• APU: Most likely the PM emissions will be significantly reduced in this case also.

• Emissions from road transport vehicles (traffic counts, five zones) are rather insignificant.

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

NO x emissions/day

Predominantly use of lane 22

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Conclusions

Morten Winther Senior adviser 27. november 2012

› A detailed 5x5 m airport emission inventory has been made, and emission results are explained by the size of emf. and fuel consumption (activity data).

› On the airport apron, handling is the largest emission source of NO x

(63 %) and PM

(51 %). APU emissions (NO x

: 25 %, PM: 45 %) are also considerable. ME emissions of

NO x

(11 %) and especially PM (4 %) are small.

› Conversely, on the apron, ME is the largest source of HC (63 %) and CO (44 %). For the whole airport, ME becomes the largest emission source for all pollutants.

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Conclusions

Morten Winther Senior adviser 27. november 2012

The calculated PM emissions from main engines decrease by more than 50 %, in the case of zero sulphur in the jet fuel.

APU: Most likely the PM emissions will be significantly reduced in this case also.

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

References

› Ellermann, T., Massling, A., Løfstrøm, P, Winther, M., Nøjgaard, J. K. & Ketzel. M.. 2011: Investigation of air pollution at the apron at Copenhagen airport in relation to working environment (Danish with English summary) DCE - Danish Centre for Environment and Energy, Aarhus University. 148 p.

– DCE report no. 5. http://www.dmu.dk/Pub/TR5.pdf

› Løfstrøm, P., Ketzel, M., Winther, M., Kousgaard, U., Christensen, J., Geels, C., Massling, A., Nøjgaard, J.K., Ellerman, T.

2012: AIR POLLUTION LEVELS AT COPENHAGEN AIRPORT ESTIMATED BY MEASUREMENTS AND NESTED REGIONAL

EULERIAN, LOCAL GAUSSIAN PLUME AND CFD MODELS, 5 p., 14th Conference on Harmonisation within Atmospheric

Dispersion Modelling for Regulatory Purposes

– 2-6 October 2011, Kos, Greece.

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AARHUS UNIVERSITY Morten Winther Senior adviser 27. november 2012

Thank you for your attention!

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AARHUS UNIVERSITY Morten Winther Senior adviser

Aktivitetsdata – kørende trafik

27. november 2012

› Trafiktællinger/15 min intervaller fra CPH (kamera):

› Hilton

› Busterminal v. T2

› Drop off v. T3

› Finger B-C

› Check Øst

› Køretøjskategorier

› Personbiler, varebiler/minibus, busser (rute/turist), bagagevogne

› Strækninger opmålt på kort

› Antagelser vedr. tomgang og kørehastighed

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