Sound, Noise and Vibration

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Sound, Noise and Vibration An explanation Rupert Thornely-Taylor July 2014 P5 (1) HOC/10003/0002

Outline of Presentation What sound is - sources, and ways in which is it transmitted from source to receiver What vibration is - sources, and ways in which is it transmitted from source to receiver Human perception of sound and vibration Measurement scales and indices Assessment approaches - relationship between noise and vibration and human response to them Ways in which noise and vibration and their effects can be reduced Government policy regarding assessment and decision making HS2's application of government policy P5 (2) 2/46 HOC/10003/0003

Scope of sound and vibration issues SURFACE CONSTRUCTION TUNNEL CONSTRUCTION SURFACE OPERATION - RAILWAY SURFACE OPERATION - FIXED PLANT UNDERGROUND OPERATION P5 (3) 3/46 HOC/10003/0004

Basics what sound is Sound is air oscillation that is propagated by wave motion at frequencies between 20 cycles per second (called Hertz, abbreviated Hz) and 20,000 cycles per second (20kHz) P5 (4) 4/46 HOC/10003/0005

Basics what sound is Sound decays with distance It spreads out, is reduced by soft ground surfaces and by intervening obstacles Sound decay is known as attenuation P5 (5) 5/46 HOC/10003/0006

Basics what sound is Sound is measured in decibels, abbreviated as db frequency-weighted to approximate the response of the human ear in units of db(a) P5 (6) 6/46 HOC/10003/0007

Basics what sound is Noise is unwanted sound The human ear is much more complex than any sound level meter Human beings are more complex still there is no simple relationship between noise measurements and human response to the noise P5 (7) 7/46 HOC/10003/0008

Basics what vibration is Vibration is oscillation of solids that can be propagated through wave motion Vibration in soil decays with distance when it spreads out, and is also attenuated by energy absorption in the soil and by obstacles and discontinuities P5 (8) 8/46 HOC/10003/0009

Basics what vibration is Vibration is mainly of interest in the frequency range 0.5Hz to 250Hz and is measured in units of acceleration, velocity or displacement, but it can give rise to audible sound which is then measured in decibels P5 (9) 9/46 HOC/10003/0010

Basics what vibration is Like sound, vibration needs to be frequencyweighted to match the response of the human tactile senses P5 (10) 10/46 HOC/10003/0011

Basics what vibration is As with sound, human response to vibration is much more complex than can be measured with a meter P5 (11) 11/46 HOC/10003/0012

Basics - sound Every 10 db increase is about double the loudness Every 10 db decrease is about a halving of loudness P5 (12) 12/46 HOC/10003/0013

Basics - sound A 1 db change is only perceptible under controlled conditions P5 (13) 13/46 HOC/10003/0014

Basics - sound A 3 db change is the minimum perceptible under normal conditions P5 (14) 14/46 HOC/10003/0015

Basics - noise P5 (15) 15/46 HOC/10003/0016

Basics - sound Sounds that vary in level are measured in indices such as equivalent continuous sound level, used internationally L eq,t (or L Aeq,T ) T = time period As well as maximum sound level such as L pafmax P5 (16) 16/46 HOC/10003/0017

L Aeq is no ordinary average Decibel scale 70 60 decibels 50 40 17/46 30 0 50 100 150 200 250 300 350 400 time, seconds P5 (17) HOC/10003/0018

L Aeq is no ordinary average Logarithmic energy scale 10000000 1000000 energy 100000 10000 18/46 1000 0 50 100 150 200 250 300 350 400 time, seconds P5 (18) HOC/10003/0019

L Aeq is no ordinary average Linear energy scale 8000000 7000000 6000000 5000000 energy 4000000 3000000 2000000 1000000 Average Energy 19/46 0 P5 (19) 0 50 100 150 200 250 300 350 400 time, seconds HOC/10003/0020

L Aeq is no ordinary average 70 L pafmax 60 L Aeq decibels 50 40 AVERAGE LEVEL 30 0 50 100 150 200 250 300 350 400 time, seconds P5 (20) 20/46 Comparison between arithmetic average of the decibel values, L aeq and L pafmax HOC/10003/0021

Basics - sound With L Aeq : doubling the energy in the sound, doubling the number of sources, doubling the duration of a sound event, doubling the number of similar events each give +3dB P5 (21) 21/46 HOC/10003/0022

Basics - sound With L Aeq : ten times the energy in the sound, ten times the number of sources, ten times the duration of a sound event, ten times the number of similar events each give +10dB P5 (22) 22/46 HOC/10003/0023

Basics sound and vibration In terms of human response at environmental sound levels: Sound levels on their own mean nothing. Social surveys link sound levels with human response There is always a wide distribution of responses There is never a clear distinction between acceptable and unacceptable or significant and not significant The same is true of vibration P5 (23) 23/46 HOC/10003/0024

Basics - sound Comparison of percentage highly annoyed for different sources (Source: Miedema and Oudshoorn 2001) percentage of the population 100 90 80 70 60 50 40 30 20 10 Aircraft Road Rail P5 (24) 24/46 0 45 50 55 60 65 70 75 Noise level (L den ) HOC/10003/0025

Basics - sound Noise from fixed plant is assessed by comparing the L Aeq with 5dB added unless the noise is characterless against the background noise in L A90. L A90 measures quiet moments e.g. between passing vehicles or aircraft. P5 (25) 25/46 HOC/10003/0026

Basics - sound 50 decibels 40 L A90 30 0 50 100 150 200 250 300 350 400 P5 (26) 26/46 time, seconds HOC/10003/0027

Basics vibration (affecting people) Vibration felt by the sense of touch is assessed using Vibration Dose Value (VDV) P5 (27) 27/46 HOC/10003/0028

Basics vibration (affecting buildings) Vibration affecting buildings is assessed using peak vibration velocity called Peak Particle Velocity or PPV. P5 (28) 28/46 HOC/10003/0029

Basics vibration (heard as noise) Groundborne noise may be assessed using maximum sound level, L pasmax where S is the slow time weighting (1 second) P5 (29) 29/46 HOC/10003/0030

Government Policy Noise Policy Statement for England aims: Through the effective management and control of environmental, neighbour and neighbourhood noise within the context of Government policy on sustainable development: Avoid significant adverse impacts on health and quality of life Mitigate and minimise adverse impacts on health and quality of life Where possible, contribute to the improvement of health and quality of life P5 (30) 30/46 HOC/10003/0031

Government Policy Noise Policy Statement for England Explanatory note: Avoid impacts on health and quality of life above Significant Observed Adverse Effect Level (SOAEL) Mitigate and minimise impacts on health and quality of life between Lowest Observed Adverse Effect Level (LOAEL) and SOAEL. Proactively manage noise taking into account the guiding principles of sustainable development Not focussing solely on the noise impact without taking into account other related factors Not possible to have a single objective noise-based measure that defines SOAEL that is applicable to all sources of noise in all situations. SOAEL is likely to be different for different noise sources, for different receptors and at different times. P5 (31) 31/46 HOC/10003/0032

Government Policy Planning Practice Guidelines: Neither the NPSE nor the National Planning Policy Framework expects noise to be considered in isolation, separately from the economic, social and other environmental dimensions of proposed development Above LOAEL consideration needs to be given to mitigating and minimising those effects (taking account of the economic and social benefits being derived from the activity causing the noise) Above SOAEL the planning process should be used to avoid this effect occurring, by use of appropriate mitigation such as by altering the design and layout. Such decisions should be made taking account of the economic and social benefit of the activity causing the noise, but it is undesirable for such exposure to be caused. Unacceptable effects should be prevented from occurring P5 (32) 32/46 HOC/10003/0033

HS2 implementation of government policy Achieve Noise Policy aims Set LOAEL and SOAEL values having due regard to Established practice Research results Guidance in national and international standards Guidance from national and international agencies Independent review by academic, industry and government employees on the Acoustics Review Group P5 (33) 33/46 HOC/10003/0034

Operational airborne noise effect levels P5 (34) 34/46 HOC/10003/0035

Operational groundborne noise and vibration effect levels (including temporary railways) P5 (35) 35/46 HOC/10003/0036

Construction noise effect levels P5 (36) 36/46 HOC/10003/0037

Fixed plant noise control Under BS 4142: If the rating level (L Aeq plus 5dB for tonal noise) around +10: around +5: below -10: minus L A90 is Complaints are likely Marginal significance Complaints positively unlikely P5 (37) 37/46 HOC/10003/0038

Mitigation Operational Noise Operational noise can be mitigated by Train design Noise barriers Noise insulation where eligible P5 (38) 38/46 HOC/10003/0039

Mitigation Train design Current European TSI compliant trains do not have pantographs / wells designed to minimise aerodynamic noise (TGV / Eurostar) P5 (39) 39/46 Current Asian HS trains do have pantographs / wells designed to minimise aerodynamic noise (Shinkansen N700) HOC/10003/0040

Mitigation Noise barriers P5 (40) 40/46 HOC/10003/0041

Mitigation Operational Vibration Operational vibration can be mitigated by Train design and maintenance Track design and maintenance P5 (41) 41/46 HOC/10003/0042

Mitigation Operational groundborne noise Operational groundborne noise can be mitigated by Track design and maintenance Continuous welded rail Resilient rail support P5 (42) 42/46 HOC/10003/0043

Mitigation Track design Optimised track solutions e.g. HS1 London Tunnels slab track P5 (43) HOC/10003/0044

Mitigation Construction Noise Construction noise can be mitigated by Up-to-date methods of working Modern plant Noise barriers Noise enclosures Monitoring and management All subject to Section 61 consent Noise insulation/temporary rehousing P5 (44) 44/46 HOC/10003/0045

Mitigation Construction Vibration Construction vibration can be mitigated by methods of working monitoring and management All subject to Section 61 consent P5 (45) 45/46 HOC/10003/0046

HS2 Information Papers E20 - Control of airborne noise from altered roads and the operational railway E21 - Control of ground-borne noise and vibration from the operation of temporary and permanent railways E22 - Control of noise from the operation of stationary systems E23 - Control of construction noise and vibration P5 (46) 46/46 HOC/10003/0047