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Idling – when the engine is running but not generating tractive power – occurs when a diesel train is coasting or braking, and also when stationary in stations, stabling locations or depots. Diesel trains have one or more idle modes where the engine operates at a relatively low engine speed (revolutions per minute, rpm). A substantial part of a diesel train’s drive cycle can be spent in idle.
Although emissions of the air quality pollutants nitrogen oxides (NOx) and particulate matter (PM) in idle are lower per unit time (g/h) than in other engine notches, they are highest on a power basis (g/kWh). Consequently, idling emissions can have a disproportionately higher impact on air quality compared to other parts of the drive cycle.
Emissions during idling may only be a small part of the total mass of emissions generated throughout the overall drive cycle of a train. However, they may be particularly important at key locations with existing air quality issues where concentrations of air quality pollutants are close to breaching an existing ambient air quality objective or potential rail air quality target.
Reducing idling has numerous benefits:
However, at many locations idling may be necessary to produce power for hotel loads (such as heating or cooling), brake compressors and other auxiliaries, including when the driver prepares the train for departure. Unavoidable idling also occurs while waiting at a stop signal: engines need to be kept running to ensure the train can move off as soon as it is allowed to proceed. In addition, there is little benefit in shutting down engines for stops that are less than 10 minutes. It was therefore necessary to distinguish between unavoidable and avoidable idling in this project.
The need to address idling emissions is recognised in the rail industry Air Quality Strategic Framework and Sustainable Rail Blueprint. It is also included in the 2022 Chief Medical Officer’s annual report. To meet this challenge RSSB contracted Aether to quantify when and where idling takes place, to investigate why idling occurs, and to develop guidance on how it can be reduced.
To quantify potential avoidable idling and identify where it occurs, on-train monitoring data was obtained from a number of train operating companies (TOCs) operating diesel trains and the owning rolling stock leasing companies (ROSCOs). The data varied considerably in the parameters measured and data formats used, so significant pre-processing was required. All of the data included time of day and vehicle speed. Some of the data included GPS location data that could be used to identify the stop location, while some of the data included engine speed. Where engine speed was missing, other indicators were used to determine whether the engines were running, such as the battery voltage or the data logging frequency.
Vehicle speed and location data (where available) was used to identify where the train had stopped, and the locations were categorised by station (terminating or through), depot (including stabling locations) or network (stops at signals etc.). Longer stops over 10 minutes were identified as a threshold for identifying potential avoidable idling. Stopping rates were then determined at stations and at depots. Using the time distributions of these prolonged stops, typical potential avoidable idling rates (in minutes per 1000 vehicle-km) were derived.
The analysis of the data from the different train classes and operators showed a large variation in the amount of idling occurring. Some trains were left idling while stationary for about half of the day, whereas others were left idling for about a quarter of the day. Some idling events exceeded 12 hours.
The figure below shows an illustrative example of data collected from two diesel multiple units (DMUs) in routine operation for about a month. This included running scheduled timetables, overnight stabling, and time in depots. The data has been analysed to determine the amount of time in four different modes:

By extrapolating average potential avoidable idling rates for different fleets using annual vehicle-km figures, the total annual avoidable idling nationally was estimated to be over 2 million hours, split almost equally between terminating stations and depots. The associated societal carbon and air pollution damage annual costs were calculated to be about £24 million for CO2 emissions, and over £10 million each for NOx and PM emissions. The cost of the fuel used during potentially avoidable idling is over £20 million per year, which represents about 8.5% of the national diesel train fuel usage.
Due to high variability across rolling stock, routes, and operations, it is impossible to prescribe a single solution to reduce avoidable idling. TOCs must understand their own situation to determine where and why idling happens and how much is avoidable. With this information, TOCs will be able to assess the most practical, effective solutions that will address the biggest issues.
TOCs are therefore encouraged to develop idling reduction strategies and to include them in air quality improvement plans. The findings from the research were used to draft guidance for the industry, which sets out the following recommended approach:
The detailed guidance is set out in the RSSB publication Good Practice Guide: Reducing Emissions From Idling Diesel Trains.
Further information is available on the RSSB website.
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