Rating level in BS 4142 and how it is derived
Rating level is specific sound level plus corrections for tonality, impulsivity and intermittency. Every correction, including a zero one, needs a stated basis.
The rating level is the specific sound level of the source plus any corrections for acoustic character. It is written as L Ar,Tr, and it is the number that gets compared against the background sound level to reach a conclusion under BS 4142:2014+A1:2019. Everything contentious in an assessment sits in one of two places: how the specific sound level was obtained, and what justified the corrections added to it.
Reviewers spend most of their time on the corrections, because a correction of a few decibels moves a conclusion from low impact to adverse impact without anything changing on site.
Deriving the rating level step by step
The sequence in the standard is fixed, and a report that departs from it is usually doing so for a reason worth examining.
- Define the assessment location and the reference time interval.
- Determine the specific sound level at that location over that interval.
- Assess the acoustic character of the specific sound and apply corrections for tonality, impulsivity, intermittency and any other distinctive characteristic.
- Add the corrections to the specific sound level to give the rating level.
- Determine the representative background sound level for the same interval.
- Subtract the background from the rating level to give the excess.
- Interpret that excess in context.
Reference time intervals matter and are frequently wrong. The standard uses one hour during the day and 15 minutes at night, and the night-time interval starts at 23:00. A report using an hour at night has diluted a short noisy event into an average, which is precisely what the shorter interval exists to prevent.
Measuring the specific sound level
The specific sound level is the A-weighted equivalent continuous sound pressure level produced by the source alone, at the assessment location, over the reference interval. The difficulty is separating it from everything else.
Three routes are used in practice. Direct measurement where the source can be run in isolation, which is the cleanest and rarely possible. Measurement with and without the source running, subtracting logarithmically, which needs an adequate difference between the two to be reliable. Or measurement at close range combined with calculation to the receptor, which is the usual approach for proposed plant and for existing plant that cannot be switched off.
For a proposed development the specific sound level is calculated rather than measured, from manufacturer sound power data, and the report should state the source data, the attenuation applied, and the assumptions about directivity, screening and distance. Where sound power data comes from a supplier rather than a test certificate, say so.
The measurement position should represent the receptor. Where measurements are taken close to a facade, the reflection correction has to be applied or the measurement has to be made in free field conditions, and reports regularly compare a facade measurement against a free field background without adjusting either.
Corrections for tonal, impulsive and intermittent character
The standard allows a subjective assessment of character, supported by objective methods where the case warrants it.
Tonality is corrected in three steps according to how perceptible the tone is at the receptor: a small correction where it is just perceptible, a larger one where it is clearly perceptible, and the largest where it is highly perceptible. An objective one-third octave analysis, or a reference method, should support anything beyond the smallest correction.
Impulsivity carries a wider range, again graded by how distinctive the impulsive element is, and the upper end is reserved for sound where the impulsive character dominates.
Intermittency attracts a correction where the sound is readily distinctive against the residual sound and switches on and off in a way that draws attention. A compressor cycling every few minutes is the classic case.
A further correction is available for other characteristics that make the sound more noticeable than its level alone suggests.
The rule for reviewers is simple. Every correction needs a stated reason and a stated basis, and zero corrections need the same. A report that applies no character correction to a fan installation with an audible tone is as defective as one that applies six decibels without analysis.
Comparing against the background sound level
The background sound level is the L A90 over the same reference interval, determined at the same location, and it has to be representative rather than the lowest value recorded. Choosing it is the other half of the assessment and deserves its own attention, which is why choosing the background sound level is treated separately.
Subtract the background from the rating level. The standard's indicative interpretation runs from an excess of around ten decibels, which indicates a substantial adverse impact depending on context, through an excess of around five decibels indicating an adverse impact depending on context, down to a rating level at or below the background, which indicates a low impact.
Those words carry weight. The standard never says that an excess of ten decibels is unacceptable. It says the assessment depends on context, and the phrase appears in the standard itself rather than being an argument invented by consultants.
Context and its role in the conclusion
Context is a required part of the method, not a softening device applied at the end.
It covers the absolute level of the rating level, since an excess of eight decibels over a background of 25 dB in a rural area is a different proposition from the same excess over a background of 50 dB beside a main road. It covers the character of the residual sound, because a source that is similar in character to what is already there is less noticeable. It covers the sensitivity of the receptor and the presence of existing internal noise controls such as acoustic glazing.
A conclusion that recites the excess and stops has not completed the assessment. A conclusion that uses context to explain away a large excess without reasoning has overreached. The defensible version sets out the excess, then states the contextual factors and how each affects the judgement.
Reporting uncertainty
BS 4142 expects uncertainty to be addressed, and most reports treat it as a paragraph of boilerplate.
The sources worth quantifying are instrument and calibration tolerance, the representativeness of the survey period, the variability of the source operating condition, the accuracy of any sound power data used, meteorological conditions during measurement, and the difference between measured and calculated levels where propagation modelling was used.
Where the excess is close to a threshold in the indicative interpretation, uncertainty determines whether the conclusion holds. Say what it is and say which way it could move the result.
Errors that recur in submitted reports
Reviewers see the same faults repeatedly.
Background taken as an L Aeq rather than an L A90. The lowest measured background used instead of a representative value. The wrong reference time interval at night. Facade measurements compared with free field values, or the reverse. Character corrections applied without any stated basis, or omitted where a tone is plainly audible. Sound power data taken from a brochure without a test standard. Assessment positions chosen for access rather than for representativeness. And a conclusion drawn from the excess alone with context mentioned but never applied.
The counterpart errors in the background determination are covered in more depth alongside rating and background sound levels, and the two halves of the assessment should be reviewed together rather than in isolation.
Browse the full list of report types to see where a noise assessment sits in an application pack, or enter your postcode on PlanScope to see which reports a site is likely to need.
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Frequently asked questions
What is the difference between the specific sound level and the rating level?
The specific sound level is the A-weighted equivalent continuous sound pressure level produced by the source alone at the assessment location over the reference time interval. The rating level is that figure plus any corrections applied for acoustic character, covering tonality, impulsivity, intermittency and other distinctive features. Only the rating level is compared with the background sound level.
Which reference time intervals does BS 4142 use?
One hour during the daytime and 15 minutes at night, with the night period beginning at 23:00. The shorter night-time interval exists so that a brief noisy event is not averaged away across a longer period. A report that uses an hour at night has diluted the assessment and the conclusion should be treated with caution.
How much correction can be applied for tonality?
The standard grades the correction by how perceptible the tone is at the receptor, from a small correction where it is just perceptible up to the largest where it is highly perceptible. Anything beyond the smallest correction should be supported by objective analysis rather than by assertion, and the report should state which method was used.
Does an excess of ten decibels mean the scheme is unacceptable?
No. The standard describes an excess of around ten decibels as indicating a substantial adverse impact depending on context, and around five decibels as indicating an adverse impact depending on context. Context is part of the method: absolute levels, the character of the residual sound, receptor sensitivity and existing controls all bear on the conclusion.
Why does uncertainty matter in a BS 4142 report?
Because a difference of two or three decibels can move a conclusion between categories. Quantify instrument and calibration tolerance, the representativeness of the survey period, variability in source operation, the accuracy of any sound power data, and the weather during measurement. Where the excess sits close to a threshold, state which way uncertainty could move it.
Sources and further reading
This article is general guidance about the planning system in England and, where stated, the rest of the UK. It is not legal or professional advice. Check your local planning authority’s validation requirements and take professional advice for your specific site.