DavidGreen, Image : King's College London

Dr David Green: There have been a few studies in the past, notably [London] Paddington, but that was some time ago when there were still lots of diesel trains running there. There has been a more recent study at Birmingham New Street as well, which has problems due to the subterranean nature of some of the platforms.

So the work that my team and I undertook for RSSB was one of the most comprehensive assessments. We’re really trying to understand both the concentrations and the sources as well.

When we were trying to get an idea of the spatial representation of air quality around the station, we had to look for smaller devices. For nitrogen dioxide, we were using small diffusion tubes, which are quite accurate but they have a poor time resolution because you have to deploy them for four weeks. It’s very difficult to get an accurate, small sensor for nitrogen dioxide.

For particulate matter, there are smaller sensors available, and we used some of those, which are based on the optical properties of particles. These are small enough that we could put them up in four or five locations around the station. That can tell us a bit about the variability of concentrations.

We also had these measurements outside the stations, so we could understand how much more pollution there was inside the station relative to outside. We like to view this as an increment approach – the difference between what you measure outside and inside is what is coming from inside the station.

What we found at Edinburgh, if you compare it to King’s Cross – Edinburgh is a smaller city [than London], so the background concentrations were lower than they were at King’s Cross. However, there are more diesel trains and generally more train movements at Edinburgh station, so the station increment was higher. So we found fairly similar concentrations at Edinburgh and King’s Cross, but for slightly different reasons.

I think it’s really important to understand that complexity. If you don’t understand the sources that are contributing to the concentrations at the station, you can’t develop management or policy tools to reduce the concentrations. At Edinburgh, we found that food outlets contributed to some of the measurements we made.

Most of the measurements we made at other locations were related to the movements of diesel trains, so that was very clear. But some of it also seemed to be influenced by the local geometry of the station itself. The concourse at Edinburgh, in particular, was quite enclosed, and relatively close to a couple of the departure points for the trains. Whereas the concourse at King’s Cross was very separate from the departure point. There was a little bit of insight around if you were designing a new station layout, how you might want to do that to minimise the exposure of waiting passengers.

You could draw a parallel between standing on a platform edge to standing by a busy road. What you’re being exposed to is the background air plus the emissions from the diesel engine as a local source. So the risks are similar to standing by a road in the middle of a city. I’m loath to say there’s a health concern above and beyond what you’d exposed to in a normal city environment.

The emissions of small particles and nitrogen dioxide are primarily associated with diesel trains, although there are some other contributing factors such as food halls, the urban background, and if there’s any construction work or other vehicles. Edinburgh has changed a bit but they used to have a taxi rank actually within the station itself, and I think Euston still has some taxi access to one of the areas.

There’s the effect of train idling as well. It wasn’t something within the report that we had a great deal of detail on, but obviously the longer the engine is running within the station, the more it’s going to emit.

In general, when we talk about reducing concentrations, we always like to focus on reducing emissions, because it’s much easier to reduce emissions at source than it is to reduce concentrations once they’re in the air. The same is true of many of the solutions that are talked about, like photocatalytic paint or green walls.

In enclosed locations, ventilation can help, but you often run into problems with building design. For instance, King’s Cross is certainly a grade I or II listed building, so major changes to the outside of that to put fans in would be very difficult. The same, I think, is true of Edinburgh, and you may run into problems with the surrounding hotels, some of which sit virtually on top of the station.

At Birmingham New Street there is quite an advanced ventilation system, which kicks in based on the CO₂ or NO₂ concentrations on the platform. So there are options, but they have to be dealt with in the remit of planning and regulation. So it’s not always straightforward.

I think that’s a decision for the rail industry because there are accepted problems with electrifying large areas of the network. The relationship between [diesel trains and emissions] is clear, and diesel trains are being replaced at many stations. I don’t think, apart from the odd sleeper train, there are any diesel trains leaving from Paddington anymore. So there is certainly progress being made, but if you remove diesel trains from stations, then you would remove the dominant NO₂ and PM sources. Looking at bi-mode systems that may run on the wires as they come into stations would be a solution to that.

Yeah, I think taking steps to reduce your personal exposure is a very easy, quick win. Outside of railway stations, we recommend people walk along back streets between locations rather than on the roadside. As you move away from the source, the concentration drops exponentially, certainly in the open air. So putting a distance between yourself and the source is generally a good idea to reduce exposure.