Select Committee on Crossrail Bill Minutes of Evidence


Examination of Witnesses (Questions 2340 - 2359)

  2340. Now, if we move on to slide 14, we will start discussing the standards that are used. They are slightly different according to the circumstances and type of noise. It has become quite well-established in dealing with construction noise to use the index LAeq that I have described and to look at it in two lights. One is to see how it compares with what was there before the construction of the work started, known as the baseline noise level, to see how much the noise level is pushed up by the addition of the construction noise. Again, it is possible to arrange to visit a room right by a fairly meaty construction site and listen to what you get inside the room with the windows open and the windows closed and matters of that kind. It is also important to look at the LAeq level in its own right against what I call here trigger levels which have some significance in what we will come to in the next slide, slide 15.

  2341.  If the construction is taking place in an area where it is really very quiet to start with, where the baseline is very low, then we look at the left-hand side of this chart and we see first of all a black curve which has a flat bottom to it at 65 and if the noise level outside somebody's facade goes above 65, it is considered significant because if they had the windows open they would probably think, "I had better shut that window because of the construction noise and open one at the back of the house", and things like that. They will have to do things to make the noise level in their house tolerable, but it is not so bad that they cannot do that. Once we get up to 75, we have reached a point where shutting a window and ventilating from the other side of the house and things like that is not available because the sound insulation of closed windows is not really enough, and that is the point at which the Crossrail noise insulation scheme starts to kick in. The red line is if it is 10 dB noisier still, and you will remember that these 10 dB steps are a doubling of loudness, so the red line is four times as loud as the black line on the left-hand side. That is when using a fairly generous assumption one says that the noise insulation will not be enough to cause acceptable noise levels in the house and that is when the temporary re-housing part of the Crossrail policy kicks in. The reason why we have got a graph here is because if it is an area that is already noisy, and there are lots of areas like that, then clearly you have to look and see what the influence of the pre-existing ambient is—and ambient is just a term covering all the noise that is going on from all sources—and if the base line ambient is higher than 65, then there needs to be a secondary check which is whether the effect of the new construction noise worsens the noise environment by five dB, and that is one of the tests that determines eligibility for either noise insulation or temporary re-housing.

  2342. To move on to slide 16, this gives us the standards for construction vibration. I mentioned Vibration Dose Values, VDV, and it is rather curious units. They are there. It is very unusual for high vibration to occur except in particular circumstances close to construction activities. Those are the levels that have been used in environmental assessment.

  2343. And on slide 17 we see the threshold of significant impacts for vibration when one is only concerned with possible damage to buildings, causing cracks and things like that due to vibration. At this point I should say that whenever anyone has done research work to try to establish the relationship between vibration and building damage it has always been very hard to find cases where there is any damage at all caused by vibration.  What tends to happen is when there is something going on like construction work that may cause vibration that people can feel through their tactile sense, they start to worry and they start to look at all the plaster in their house, in every corner of very room, and I challenge anyone to go home and look at all the plaster in their house and not find hairline cracks due to ground heave, due to changes in the moisture content of the soil, and things like that. It is very rare for vibration to damage buildings.

  2344. Slide 18 takes us to the standards for airborne noise, airborne meaning noise that comes straight from something like the train wheels through the air to the person listening. The three dB that I mentioned when I was describing the effect of the decibel scale is important here. I said it was the smallest change that was normally noticeable and in considering whether noise from the surface railway is significant or not, the band between the increase of three to five is considered a slight increase but the formal label of significance is applied when the change is more than six. If it is more than 10 it is significant but it is described as a "substantial" increase.

  2345. Slide 19—there is and has been for a number of years a statutory scheme entitling people to noise insulation when some conditions are satisfied relating to airborne railway noise. The daytime LAeq trigger is 68 and night-time it is 63 and there has to be a one dB increase caused by the railway, and that applies to all new railway developments as part of the noise insulation regulations.

  2346. Slide 20, we were considering this morning the question of noise from underground railways and I think most people have experienced, even if they only visit London occasionally, the many places in London where you can hear the old Tube lines and trains passing underneath. Something between 50,000 and 60,000 people in London hear rumble from the old lines. By "old lines" I mean those constructed up to and including the first part of the Jubilee Line. And that kind of noise is measured in a slightly simpler way than the method used for both construction noise and airbourne noise from a surface railway.  We use a measure called LAmax, which is the maximum sound level. It is the easiest of all the indices to understand. If one had a meter in front of one—and if we go to this demonstration room I mentioned we will have a noise meter there and we can see the levels as they change -all that LAmax is is the highest level that the meter indicates as it rises and falls as the train goes by as you hear the distant rumble of the train. The capital S after LAmax relates effectively to the damping of the meter. Some old meters used to have needles, like barometers, and you could see the needle moving about.  When they were first designed there was both a slow and a fast characteristic, and when it was on fast the needle moved at that sort of speed, it moved rapidly, when it was on slow the needle was much more sluggish. There are uses for both weighting time constants. The advantage of LAmax S is that it is much more repeatable because of the damping of the excursions of the needle. I mentioned when I had finished introducing the decibel scale that all numbers, whether they be just dB or Laeq or LAmax only have meaning if they are linked to studies that have been carried out on the reaction of human beings to the noise, and all the information that we have about people's reaction to the rumble of a train passing underground is based on their reaction to noise levels in LAmax S.  We did have quite a debate about this in the Channel Tunnel Rail Link Committee, because one of the local authorities was very anxious that we should use the fast setting instead of the slow setting, but the outcome was we did all agree, experts from both sides, that for a modern railway good quality track, the difference between fast and slow is only about one dB and we do not really need to spend time debating which is the better. I would say that slow is better because it is more repeatable and more easily predictable.

  2347. Slide 21 shows us how we rate the noise from trains passing in tunnels underneath. The impact classification used in the Environmental Statement was labelled low if the LAmax S was in the range 35-39, and then we get significant impact should it be over 40. In fact there is no prediction over 40, because this is one of the areas where mitigation measures are well and truly available to reduce the level of noise of a passing train underground.

  2348.  Mr Elvin: Can I stop you there, because the issue about 40 in terms of ground-borne noise I raised this morning. Can I ask you to explain very briefly to the Committee because the issue, I know, is coming up with other Petitioners, in particular Camden, which I think is next, but can you just give a thumbnail sketch of the use of 40 and what it is used for?
  (Mr Thornely-Taylor) Yes, we began to take steps to deal with ground borne noise when the Jubilee line extension was planned, and clearly, that being part of the London Underground network, the most sensible thing to do was to talk to the then scientific adviser for London Underground and find out what they had found when investigating complaints about noise from the old tube lines, and all their complaints in the late 1960s early 1970s, which encompasses the period when the Victoria line was opened and the Victoria line, like all railways that have been built throughout the last century, has rail directly rigidly fastened to wooden blocks set into concrete—it has no vibration isolation, no resilience in its track support at all—and the results that were provided by the scientific adviser showed that in all cases where complaints have been investigated the sound level due to the passage of a train was over 40—many of them were quite a lot over 40—none of them were below 40, and so that was an important piece of guidance when the design aim for the Jubilee line extension was set. In fact, what happened there and what will happen with Crossrail, is that a type of track form is selected which, so far as one can, achieves the 40 from end to end even through the pinch-points, if I can call them that, where you come either close to the surface or closer to the foundations of the building, as a consequence of which the great majority of the alignment goes well below 40.  What should not happen, and does not usually happen, is that you have half a dozen different track forms and you keep changing them to keep bumping under the 40 as you go from end to end. The designer picks the most practicable, best vibration isolating platform for the whole system based on the difficult cases with the results we are going to see in a minute when I show some more slides.

  2349.  Mrs James: I have a question, and it relates to the Victoria line. This morning we saw some evidence in the Promoter's response about sound levels in theatres and the recommended level of 25 dB. I have recently been to see Billy Elliot at the Victoria Palace and every 15 minutes, without fail, it rumbled through, and to say I was uncomfortable was not true but you were constantly aware of the sound. About what level would that be? Would that be an acceptable level in a home?
  (Mr Thornely-Taylor) No, that would have been well above 40. I have been going to a lot of theatres in the course of the studies I have been doing for Crossrail.

  2350.  Mr Elvin: It is a hard job, Mr Thornely-Taylor.
  (Mr Thornely-Taylor) There had not been any plays on at the time. I have not been to the Victoria theatre, because, although future Crossrail lines may affect that area, line one does not, but some theatres do have very bad conditions; some of them have got worse, some of them have got slightly better. The first time Crossrail was promoted in one of the West End theatres you could actually feel through the soles of your feet vibration from a train going by. Those levels are well above the levels, certainly well, well above the levels we set for theatres, but they are well above levels for residential buildings, but it is useful to experience that because there is a huge change in the fundamental design of the track from the Victoria line, which, as I say, was rigidly fastened to wooden blocks set in concrete. From the Jubilee line extension onwards—not the old Jubilee line but from Green Park south to Stratford—all modern underground railways are installed such that the rails themselves are on resilient base plates, they are known as, which are quite soft, the rail deflects anything up to five millimetres as the train goes over it, and in circumstances where you need even lower noise levels—recording studios and things like that—the technique is to construct the track so that the rails are supported from a concrete slab which itself is mounted on rubber bearings; and there are several stretches like that on the Jubilee line extension. There are one or two stretches on some of the older railways. The extension of the Piccadilly line from Houndslow West to Heathrow was one of early floating slab cases, and way back in the 1960s a floating slab was installed when the Circle, Metropolitan and Moorgate lines were realigned at the Barbican, which we will hear about later in the proceedings.
  (Mr Thornely-Taylor) The Jubilee line was constructed with 40 dB LAmax S as a design aim and it has worked there very well. I, in fact, set out on behalf of Crossrail after the Jubilee line opened to get some measurements to compare the measurements with the predictions and validation model, and it was intensely difficult to find anywhere that one could actually detect the passage of trains on the Jubilee line. It is, of course, also interesting that the District and Circle line was reconstructed through Westminster station and it runs through the basement of Portcullis House, and that is on a floating track slab, and, although it has got a bit noisier than it was when it opened, because it is about time the rails were reground, I am not aware of any part of Portcullis House where you can hear the District and Circle line, and it is running effectively through the building.  When Crossrail came to be designed in the early 1990s, clearly the data from the scientific advisers to London Underground that I mentioned were beginning to get a bit long in the tooth and we set about getting more information and commissioned a social survey and vibration measurement survey. It was not as successful as it ought to have been rather a large number of people were happy to answer the questions in the social survey but were not too keen on having the instruments in to measure the vibrations; so it is not as big a sample as we would have liked, but it very forcefully confirmed that, particularly if, as is the case with modern railways, there is no 'feelable' vibration—what I was describing a moment ago about the Victoria theatre or West End theatres where you can feel the vibration through the soles of the feet.  With modern railways that effect is completely absent no matter what the audible sound level is.  When vibration is completely absent the results of the social survey showed a zero response from the public at 40 dB LAmax S That well and truly reinforced the (inaudible) policy, and it has carried through many railways—Docklands Light Railway, its several extensions, and through to Crossrail, CTRL and it is well established, having been tested, in fact, twice in Parliament and in public inquiries with arguments from local authorities and others who felt it should be reduced to a lower number, and it has always come out unscathed from whatever tribunal it has been tested in.

  2351. Finally, on that point, can I understand this? Is the 40 dB ground-borne noise a target that Crossrail seeks to achieve or is it something else?
  (Mr Thornely-Taylor) What it is not is just a numerical target. Mr McCracken was concerned that people would be going out with noise meters to see if it was 40 or not. That is not the way it works. It is a design standard that is used for selecting the basic track form of the system and for designing those lengths of the track which have to have special treatment—I mentioned the floating track slab—to meet the special requirements of things like recording studios, so where it bites is the moment that the permanent way engineers set about designing the track. After the railway opens, if there should be some problem somewhere, somebody complained and it was found to be above 40, or whatever the appropriate limit was according to the use of the building, then somebody might well do some measurements and see if there was a problem which could be rectified and bring the noise level down, but it is fundamentally a design principle given to the engineers when they start designing the railway.

  2352. From your analysis, what is the likelihood of 40 dB being reached on the design which is to be adopted for Crossrail?
  (Mr Thornely-Taylor) It is probably quite well illustrated on my next two slides. If you go to slide 22 first, which says that, if you do set the 40 limit for the permanent way designers, you will end up with much better than 40 in large areas of the railway.

  2353. Slide 23 is another of those contour maps—we saw one this morning—and the green contour, which is the biggest one there, is only 25 and even that vanishes in some places; so that is an example of what you get when your starting point is: "Tell the engineers we want no more than 40 wherever possible." So they choose a rail support system of very high resilience, very good vibration isolation performance, and they choose that for the whole railway even where you might not strictly have needed it. I remember having an argument during JLE design as to whether we should continue it under the Thames, because nobody was going to hear it there, but we did. There is vibration isolation even under the Thames; so it is a very important point. It is not uncommon to have people, either a Petitioner at a Parliament Bill or objector to a transport and works order saying 40 is too big a number, we need a smaller number, but it is always essential to read the words that go with the number. There are the railways in the world that use smaller numbers, but the words that go with the number are much less effective than the approach which Crossrail takes, which, I believe, is far and away the best approach, that you use it to the design standards from end to end and you do get a much better railway as a result.

  2354.  We will leave ground borne noise now and move on to slide 24. There are other kinds of noise, obviously, arising from a railway scheme of this kind. One of the important ones is fixed plant, and the biggest pieces of fixed plant are tunnel ventilation fans, which compared with the fans which most people come into contact with, are enormous. They, like all fans, generate noise and because it is one of the oldest sources of noise that has been addressed in the control of environmental noise, there has long been a British standard which is appropriate for assessing this kind of source.  What I am talking about is continuous unvarying noise that occurs as long as the plant is running, and it might be running at night, but not always. This uses a much stricter method of assessment, largely because this kind of noise can be more annoying than other kinds, and, particularly if it occurs at night, one has to be very strict.  We use the LAeq scale that I have already described, but except in the very rare cases where the noise could be described as completely characterless, by which I would mean the noise of a waterfall or something like that, it has no tones in it, no rattles or clinks or clanks or anything like that, we add a notional five, a sort of tax put on the LAeq for the fact that this kind of noise can be more annoying, and then we compare it not with the baseline LAeq, as is normally the case, but we compare it with something new, which I will have to explain, called LA90.

  2355.  When I was introducing the LAeq scale a few minutes ago I said when sound varies it is quite a lot of the time relatively low and goes up as a plane goes by or as a car or a lorry goes by so that it would be very cumbersome to say it is this level for such and such a percentage of the time, that level for such and such a percentage of the time. I was in fact anticipating the fact that we do sometimes talk about noise climates—the word that was used—in terms of statistical percentile, and the LA90, strictly speaking, is the level exceded for 90 per cent of the time. It is actually the troughs in a rising and falling sound-scape, if you put it like that. If the peaks, the crests of the waves are the passing vehicles—passing trains, passing aircraft—LA90 represents the troughs, which are when there is no vehicle or aircraft passing and the moment is quiet, that is the LA90.

  2356.  In slide 25, you can see there is the LA90 right down near water level. I have taken the Lake District nomenclature off, but it is the same chart. The most important thing about British Standard 4142 is that we are comparing that orange line at the top LAeq, with the tax on it, the five dB added, against the LA90, which is way below it.  We are not the comparing like with like in a way and we are looking at what is always an index of higher value than the yardstick against which we test it, and on slide 26 here is the important part of the standard. It says that if the LAeq with its five dB tax on it, which we call the rating level, is about 10 units greater than the background expressed in the LA90 you can expect complaints from people. If the difference is only five, and because of that tax on the LAeq that actually means the real physical LAeq is the same as the background LA90, the standard says it is marginal; and it also says that if it is more than 10 dB below the LA90, which effectively means it is completely inaudible, then, not surprisingly, you can say confidently complaints are unlikely.

  2357.  Mr Elvin: We then move on to mitigation. I think we are going to have to ask you to skim through this fairly rapidly so that we can make sure, given the Committee's other commitments, we can manage to fit in Professor Mair as well. I would be grateful if you could take this relatively shortly, please.
  (Mr Thornely-Taylor) The ways of mitigating construction noise—obviously the best thing to do is to find quieter methods of working, and, indeed, over the years quieter methods of working have come about—selection of quiet plant, use of noise barriers, noise enclosures for noisy machines, monitoring and management. I have already talked about noise insulation and temporary rehousing schemes. All of this is subject to the provisions of Control of Pollution Act, section 61, under which contractors will be required to seek consent and local authorities in granting that consent have the power to ensure that the best practicable means have been used to reduce the noise.

  2358. Slide 28 is for vibration. Not so many opportunities, but again methods of working and, by monitoring and management, levels of received vibration are controlled, and in section 61 vibration is technically noise and subject to the same provisions that I have just outlined.

  2359. Slide 39, the surface railway is mitigated with line-side noise barriers, and I have already mentioned the noise insulation scheme.


 
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