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BOC Immingham Dissolved Acetylene Project Environmental Statement: Vol. 2 Main Text<br />

11.20 Section 2 of the guidance note outlines the measurement and evaluation procedures that should<br />

be followed. It describes the key components of a noise assessment which include: identification<br />

of the sensitive receptors; review of complaint history; risk assessment; impact assessment; and<br />

implementation of noise control measures if required. It advises the use of:<br />

� BS 4142: Method for Rating Industrial Noise Affecting Mixed Residential and Industrial Areas<br />

for determining the impact of the installation; and<br />

� BS 7445: Description and Measurement of Environmental Noise, Parts 1 to 3, for guidance<br />

on the measurement of environmental noise.<br />

11.21 Section 3 gives guidance on noise control techniques and technologies.<br />

11.22 The guidance refers to the possibility that vibration may need to be assessed and recommends<br />

that specialist advice is sought where impacts from vibration are considered to be a risk.<br />

BS 4142 Method for Rating Industrial Noise Affecting Mixed Residential and Industrial<br />

Areas, 1997<br />

11.23 BS 4142:1997 describes methods for determining and assessing noise levels from fixed plant with<br />

a view to determining the likelihood of complaints.<br />

11.24 The likelihood of complaints about noise from the occupiers of nearby residential properties can<br />

be assessed using the method described in BS 4142:1997. This method compares the rating<br />

noise level to the measured background noise level in the absence of the source. Rating noise<br />

level is defined as the noise level from the source, adjusted for certain acoustical features. It is<br />

measured in terms of dB LAeq which is an energy based acoustic indicator. The standard defines<br />

the ‘specific noise level’ as the LAeq of the source, and the ‘background level’ as the LA90 level<br />

without the source operating.<br />

11.25 Guidance on how to measure the background noise level, LA90, is also provided in the standard.<br />

The length of measurement should be sufficient to obtain a representative value for the<br />

background noise level and should cover all periods when the specific noise will operate.<br />

11.26 The standard states that certain acoustic features can increase the likelihood of complaint over<br />

that expected from a simple comparison between the specific noise level and the background<br />

noise level. Where present at the assessment location, such features are taken into account by<br />

adding +5 dBA to the specific noise level to obtain the rating noise level. A +5 dBA correction is<br />

applied if one or more of the following features occur, or are expected to be present for new or<br />

modified noise sources:<br />

� the noise contains a distinguishable, discrete, continuous note (whine, hiss, screech, hum,<br />

etc);<br />

� the noise contains distinct impulses (bangs, clicks, clatters, or thumps); or<br />

� the noise is irregular enough to attract attention.<br />

11.27 The standard then rates the likelihood of complaints by comparing the rating noise level with the<br />

background noise level:<br />

� where the rating noise level is more than 10 dB above the background level, then complaints<br />

are likely;<br />

� where the rating noise level is more than 10 dB below the background noise level, then this is<br />

a positive indication that complaints are unlikely; and<br />

� where the rating noise level is 5 dB above the background noise level, then this is of marginal<br />

significance.<br />

5100935.404 Environmental Statement August 2011 191

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