When I raised this issue in the aviation forum I had hoped that the relatively simple case of airport access had allowed studies that might have illuminated the issues of mass transit vehicle capacity utilisation and the consequent impact of different transport modes on emissions.
I have always been uncomfortable with the quality of the argument that transferring demand between transport modes can reduce emissions. This partly due to vehicle physics, if constructed of similar materials a larger capacity terrestrial vehicle tends to be heavier per unit capacity than a smaller vehicle. This seems to be borne out by experience. Lightweight material are equally usable by all modes and rail vehicles require a minimum weight for traction so despite the low rolling resistance of steel on steel there are grounds for expecting a disadvantage that railway vehicles busses and coaches must overcome through higher capacity utilisation. Unfortunately, where peak trough ratios are high and service frequency is important it is not good logistics to expect higher capacity utilisation from larger vehicles. This is reflected in a great deal of data. Even the 18th report of the Royal Commission on the Environment published in table 12.2 data that showed all rail energy intensities as inferior to the coach and some, notably the electric suburban vehicle, as inferior to the car. This data was tentative but we now have in the public domain the Rail Safety and Standards Board paper Traction energy metrics. The data from this is usable to show the difficulties of assuming any benefit from road rail transfer.
The data gives energy intensity per seat kilometre and typical capacity utilisations. Unfortunately we only have the electrical power consumed at the vehicle for rail vehicles drawing on centrally generated power. The report addresses this by referring to the emissions of carbon dioxide from the different types of generating plant and the plans for their future use. Coal plant is the most polluting and is expected to provide 10% of electricity through 2022 because the may be a shortfall in gas generation the actual proportion generated by coal may be greater than 10%. The report discusses three approaches to estimating the emissions from power used by the railway.
Approach | Relevance |
If railway electricity use ceased the least efficient fossil fuel stations would reduce generation but lower emission generation would be unaffected. If railways increase electricity use and if this does not lead to the building of low emission plant that could not otherwise exist then the life and use of the least efficient fossil fuel stations must increase. | This approach seems to most effectively indicate the impact on emissions of policy initiatives to significantly increase railway electrical energy use by increasing electrification and transfers of demand from other modes. Consequently the table below attributes the emission of 910 grams of carbon dioxide for each kWh used by rail electric vehicles |
Reduction in generation is spread evenly over all plant. | The paper takes this approach in deriving the illustrative material on page 51. For this purpose it assumes that each kilowatt hour used by the railway causes the emission of 320 grams of carbon dioxide. This is the average figure expected to be achieved by 2022 although insecurity of gas supply might justify a less favourable forecast. The average figure in 2007 is 455 grams of carbon dioxide per kWh. In 2022 at least 10% of total generation will still be coal fired. The approach is relevant to inter-industry comparisons where no change in the mix of fuel for either industry is contemplated. |
Dedicated zero or low energy plant is created solely for rail use. (for example by vehicle installed fuel cells) | The white paper Delivering a Sustainable Railway appears to take this into account as a possibility along with other issues it considered in deciding to defer consideration of a rail network electrification. |
From the data, and using the emissions from coal burning we can calculate comparative CO2 emissions
| Type | Grams CO2/paxkm |
Aircraft | A320 | 187 |
Coach | Megabus | 28 |
Bus | Single deck | 72 |
Double Deck | 71 |
Future | Less than 70 |
Electric Rail | Class 373 | 147 |
Class 458 | 94 |
Class 357 | 94 |
Class 390 | 146 |
Class 91 | 112 |
Diesel Rail | Class 43 | 72 |
Class 170 | 69 |
Class 83 | 83 |
Future | 60-80 |
Cars | Current Average | 107 |
2022 Average | 81 |
Small car ten years old | 80 |
Future small car | >70 |
I have added figures from other sources for the small diesel car and there is considerable informed discussion of the availability of still lower energy intensities for this class of vehicle.
The data has an inherently high degree of uncertainty; for example, it is difficult to predict the trends of capacity utilisation for road and rail, if rail must increase frequency to match the utility of road vehicles then capacity utilisation could reduce as ridership increased while increasing fuel prices may increase car sharing and thus increase car capacity utilisation. The data also ignores the emission costs of consolidating loads except for stopping and starting and ignores the substantial emissions from building new facilities to expand rail capacity. The Author also suggests that, except for city centres, despite its high speed rail does not offer significant door to door advantages in travel time compared to the car or coach.
The author suggests that only differences in emission figures of 20% can indicate a high probability of a real difference. The author also suggests that because of their long life more efficient rail vehicles will not be available for decades. It can be seen that no rail vehicle is significantly better than a ten year old small car or even the average cars entering service in 2022. It can be seen therefore that increasing the proportion of small car use is the best option for reducing transport emissions overall and that increased use of the motor coach for longer distance journeys is a far better option than rail. On these data shifting demand from road to rail is not a good option for reducing passenger transport emissions.
Bus does not offer a significant advantage over the small car and may not always attract sufficient passengers to justify bus priority or offset the negative impact of so large a vehicle on congestion. On this evidence perhaps the determinant of bus policy in most locations should be how favourable its impact on social deprivation is.
The figures are of course very sensitive to capacity utilisation. The data in the report are variable. In the table above 20% is used for the proportion of places (ie including standing) used on the bus. 31% is used for all trains and this may be too high for commuter trains absorbing road traffic. It is tempting to assume the 20% figure for bus as more likely. Air uses 70% and coach 60%. These may be seem anomalously high although smaller vehicle size and high frequencies do lend themselves to pushing up capacity utilisation. It is often commented that aircraft increase capacity utilisation by the very aggressive marketing of discount fares but rail too uses this technique. Rail may achieve better than 31% on some lines but these lines may not sustain this if they must run extra trains to accommodate new peak traffic.
Aircraft are subject to one other issue, the energy intensity per pax km has multiplied by 2 to allow for radiative forcing but the aircraft spend very little time at the relevant altitude. Someone who knows more about this than me may be able to suggest a better factor.
Jim Russell.