Facts sheet 5(b) - Carbon emissions: high speed rail and air compared
Originally February 2007 updated June 2008
Wp ref. factssheet05bB
Data sources and results
Appendix 1 of Facts Sheet 5, sourced from the BERR, provides (A) circa 150 Tonnes of carbon per GWh (550 tonnes of carbon dioxide) if we assume average emissions or (B) circa 300 Tonnes per GWh (1,100 tonnes of carbon dioxide) if emissions are related to coal fired generation. In this note we present emission on both bases. However, the coal fired emission rates may be the more appropriate because, as pointed out by the RSSB in its report on Traction Energy Metrics, July 2007, any large scale increase in electricity supply would prolong the life of coal fired generation.
The emissions per passenger-km depend on occupancy assumptions. The RSSB report Traction Energy Metrics, in section 6, assigns a 40% occupancy to intercity rail. We have used that here although it is said to lead to overcrowding on some trains. For comparison the average other trains is 30%. If for service level reasons that should be the target for intercity services then the emissions per passenger-km in Table 1 should be increased by one third.
The emissions per passenger-km for the aircraft assume an occupancy of 80%. That is above the industry average but below the 84% claimed by Ryanair. Further, emissions by air cited in table 2 are 10% above those in the source table 3 to allow for refinery energy use and the transport of the fuel to the users.
The fuel consumptions for rail in the following table are from Professor Roger Kemp. They have been converted to carbon emissions using the emission data cited above.
TABLE 1
High speed train emissions |
KW-h
per 100 seat-km |
Carbon dioxide Gms (A) |
Carbon dioxide Gms (B) |
per 100 Seat-km |
per 100 Passenger-km |
per 100 Seat-km |
per 100 passenger-km |
| Pendolino West Coast at 200 kph: range |
3.5 |
1,925 |
4,810 |
3,850 |
9,720 |
| 4 |
2,200 |
5,500 |
4,400 |
11,000 |
| Class 91 East Coast at 200 kph |
3.2 |
1,660 |
4,150 |
3,320 |
8,300 |
| Eurostar at 300 kph |
5 |
2,750 |
6875 |
5,500 |
13,750 |
(Note, Eurostar achieves a higher occupancy than used here and claims electricity from France where 80% is from nuclear. Hence in Eurostar publicity emission rates are much lower than in this table).
Professor Kemp also cited a diesel HST requiring 0.8 litres per 100 seat-km at 200 kph. The specific gravity of diesel is 0.84 and the CO2 per Kg is 3,150 gms. Hence the carbon dioxide per 100 seat km is 0.8 x 0.84 x 3,150 = 2,117 gms or 5,290 gms per 100 passenger-km at 40% load factor.
Data for air is summarised in table 2. As noted above the emissions have been increased by 10% above those in the source table 3 to allow for the energy used in refineries and in transporting the fuel to the users. The data (with the exception of Ryanair) overstates the emissions for comparison with rail because of the relatively large amounts of luggage and freight carried by passenger aircraft but not (presumably) by high speed rail.
Table 2 |
Gms of CO2 |
| Per 100 seat-km |
per 100 passenger-km |
| Ryanair |
6,780 |
8,475 |
| 757-300 |
7,750 |
9,690 |
| Fokker F28 |
19,540 |
24,420 |
Comment
The data in tables 1 and 2 could be used to claim that, if it is emission (B), coal fired generation, that is relevant and if Ryanair is taken as the model aircraft, then air produces the lower emissions. On the other hand if it is emission (A), the generating industry average, that is relevant, then high speed rail may claim the lower emission.
Against that background we conclude that no strong case can be made for claiming an advantage for rail compared with air or indeed the reverse.
However, if we accept that emissions due to coal fired generation are the relevant ones and if the rail industry aspires to 300 kph Eurostar style trans for intercity routes then Ryanair would emit 40% less carbon than the trains with a 40% load factor.
Radiative forcing
The emissions from aircraft are often weighted by a factor in the range 1.5 to 3 to allow for the greater radiative forcing arising from high altitude emissions. However, short haul aircraft spend little time at the altitude where the higher radiative forcing factors apply. Further ground level emissions are said to carry a radiative forcing factor that is usually omitted. Hence when comparing the warming effects of rail compared with air the differences in radiative forcing can probably be ignored.
Sources and notes reference aircraft
The Institute of Energy (0207 467 7100) and others provided the following for aviation fuel:
Calorific value: gross = 46.2 giga-joules per Tonne, Net 46.2 x 0.935 = 43.2
Carbon dioxide: 3.15 Kg of CO2 per Kg of ATF (Jet 1)
Specific gravity range 0.775 to 0.84 providing an average here set to 0.8.
That together with the source data in Table 3 below enables the emission data therein to be calculated. E.g. Ref. the CRJ-700 first item: CO2 per 100 seat-km = (545 x 3.785 x 0.8 x 3,150 x 100)/(334 x 1.6 x 70) = 13,896 gms.
The Aircraft Monitor data in table 3 was recommended to us by Dr Peter Morrell of the Cranfield Institute of Technology. Dr Morrell has also been kind enough to confirm that the parameters and calculations used in this table are in close agreement with his estimate for the B747-200 (the last aircraft cited in table 3).
Fuel consumptions in this table should be increased by 10% to allow for refinery energy use and fuel used in transporting the fuel to the users
TABLE 3 |
Source: The Airline Monitor, August 2002 * |
Carbon dioxide gms |
Short/medium haul: |
US gals per
block hour |
Av. Seats
per flight |
Av miles
per flight |
Av mph |
per 100
seat-km |
per 100 pass-km:
80% load |
| Ryanair |
776 |
189 |
611 |
397 |
6,165 |
7,707 |
| CRJ-700 |
545 |
70 |
428 |
334 |
13,896 |
17,370 |
| CRJ-100/200 |
365 |
50 |
442 |
297 |
14,653 |
18,316 |
| ERJ-135 |
312 |
37 |
390 |
261 |
19,260 |
24,075 |
| ERJ-140 |
359 |
44 |
387 |
284 |
17,127 |
21,408 |
| ERJ-145 |
358 |
50 |
431 |
270 |
15,809 |
19,761 |
| Avro 85 |
569 |
69 |
297 |
247 |
19,903 |
24,878 |
| Bae 146 |
623 |
91 |
316 |
258 |
15,819 |
19,773 |
| Fokker F28 |
664 |
69 |
430 |
323 |
17,761 |
22,201 |
| DC-9-30 |
808 |
101 |
512 |
306 |
15,585 |
19,482 |
| F-100 |
658 |
88 |
473 |
293 |
15,213 |
19,017 |
| 717-200 |
635 |
111 |
415 |
292 |
11,679 |
14,599 |
| MD 90 |
927 |
150 |
811 |
359 |
10,262 |
12,828 |
| 737-200 |
910 |
115 |
522 |
329 |
14,338 |
17,923 |
| 737-500 |
704 |
109 |
600 |
334 |
11,528 |
14,410 |
| A319 |
758 |
123 |
933 |
374 |
9,823 |
12,279 |
| 737-300 |
730 |
131 |
610 |
333 |
9,976 |
12,470 |
| 737-400 |
786 |
141 |
663 |
333 |
9,979 |
12,474 |
| A320-200 |
822 |
146 |
1,091 |
388 |
8,650 |
10,813 |
| MD80 |
956 |
135 |
779 |
351 |
12,027 |
15,034 |
| 727-200 |
1281 |
149 |
766 |
354 |
14,478 |
18,097 |
| 737-800 |
836 |
149 |
1,055 |
382 |
8,756 |
10,945 |
| 737-900 |
801 |
172 |
1,075 |
390 |
7,118 |
8,898 |
| A321-200 |
927 |
169 |
1,406 |
410 |
7,975 |
9,969 |
| 757-200 |
1091 |
182 |
1,258 |
402 |
8,889 |
11,112 |
| 757-300 |
1191 |
247 |
1,084 |
408 |
7,045 |
8,807 |
| A300-600R |
1743 |
228 |
1,513 |
413 |
11,035 |
13,793 |
| B767-400 |
1661 |
272 |
1,547 |
429 |
8,486 |
10,607 |
| Medium/long-haul |
| L1011-500 |
2365 |
288 |
2,340 |
449 |
10,903 |
13,629 |
| DC10-10/30/40 |
2606 |
284 |
2,575 |
461 |
11,866 |
14,832 |
| A330 |
2169 |
261 |
3,647 |
468 |
10,586 |
13,232 |
| MD-11 |
2160 |
272 |
3,651 |
488 |
9,701 |
12,126 |
| B767-300 |
1476 |
207 |
2,274 |
450 |
9,446 |
11,808 |
| B767-200 |
1459 |
176 |
2,083 |
436 |
11,335 |
14,168 |
| B777-200 |
2134 |
266 |
3,557 |
487 |
9,820 |
12,276 |
| B747-400 |
3429 |
369 |
4,445 |
505 |
10,970 |
13,712 |
| B747-200 |
3536 |
357 |
3,386 |
480 |
12,301 |
15,377 |
Further a report in the Times of 8th February cites for the A380 (certified to carry 853 passengers) as emitting 8,000 gms of CO2 per 100 passenger-km when carrying 550 passengers on an 8,000 km trip.
Transport-watch
Updated June 2008
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