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Draft National Wind Farm Development Guidelines - July 2010

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Table B-4<br />

Suggested methods for assessment of noise characteristics<br />

Noise<br />

characteristic<br />

Amplitude<br />

modulation<br />

Impulsiveness<br />

Suggested assessment<br />

procedure<br />

Tasmania Department<br />

of Primary Industries,<br />

Water and<br />

Environment (2004)<br />

Noise measurement<br />

procedures manual,<br />

Also Western<br />

Australian<br />

Environmental<br />

Protection (Noise)<br />

Regulations 1997<br />

Australian Standard<br />

1055.1:1997 Acoustics<br />

– Description and<br />

measurement of<br />

environmental noise<br />

Part 1: General<br />

Procedures<br />

Comments<br />

Amplitude modulation may be present where there is a<br />

greater than normal degree of fluctuation of sound level.<br />

The suggested assessment procedure indicates the<br />

presence of amplitude modulation where there is a<br />

regular, cyclic and audible variation in sound level of more<br />

than 3dB.<br />

It should be noted that LA90,T may not be appropriate for<br />

assessing amplitude modulation. LAeq, LA01 or LAMax indices<br />

may be more suited to identification measurements.<br />

Further, it is noted that any assessment of amplitude<br />

modulation should take place at the Receiver location<br />

being assessed. It is not suitable to carry out an assessment<br />

within the wind farm site as, at the Receiver location,<br />

emission from several different turbines may be contributing<br />

to the observed effect. Also, the measurement position<br />

should not be unduly affected by facade reflections in the<br />

area immediately around the measurement location.<br />

This assessment requires the use of a sound level meter with<br />

fast response and impulse response time weightings. It is<br />

recommended that impulsiveness assessments be carried<br />

out on calibrated digital recordings of the suspected<br />

impulsive sound, so that the impulsive and fast time<br />

weighting may be applied to the same audio sample. In<br />

some cases, impulsiveness may be indicated using the<br />

AS1055.1 assessment method when, subjectively, it is not<br />

considered to be present. These cases should be discussed<br />

with the relevant authority<br />

Infrasound DIN 45680:1997<br />

Measurement and<br />

evaluation of lowfrequency<br />

environmental noise,<br />

Deutsches Institut für<br />

Normung<br />

DIN45680 does not prescribe acceptable noise limits but<br />

discusses a method for assessing perceptibility. Although a<br />

given low frequency noise or infrasound may be<br />

perceptible, this does not imply a negative effect on<br />

health.<br />

The assessment frequency range of DIN 45680:1997 extends<br />

down to 8Hz and so may exclude some frequencies which<br />

are considered part of the infrasound range. Complaints<br />

resulting from noise emission in this extremely low frequency<br />

range are considered unlikely. Nonetheless, it is important<br />

to recognise this limitation of the assessment method.<br />

Low<br />

frequency<br />

noise<br />

Tonality<br />

DIN 45680:1997<br />

Measurement and<br />

evaluation of lowfrequency<br />

environmental noise,<br />

Deutsches Institut für<br />

Normung<br />

Assessment<br />

procedures as<br />

identified in Section<br />

7.2 of AS4959–<strong>2010</strong><br />

The noise level threshold curves included in the standard<br />

are reasonably conservative. However, they are based on<br />

a 50% threshold level and some research suggests that a<br />

10-12dB margin to the 10% threshold may exist.<br />

Accordingly, it may be that some individuals can hear a<br />

sound level which is measured to be less than the threshold<br />

limit. Where the measured level is within 12dB of the<br />

threshold value and the measured level is greater than the<br />

background noise level further investigative work is likely to<br />

be required.<br />

Note: The assessment method proposed for amplitude modulation should be considered as nominal<br />

and is proposed in the absence of a more suitable method specific to wind farms. It may be used as<br />

an indicator of amplitude modulation; however, the assessment should be carried out in conjunction<br />

with a subjective assessment of the sound by the assessor and the relevant authority. It may be more<br />

suitable in this case to explore adjustments in the operation of particular turbines under certain<br />

meteorological conditions, for example by using noise management settings at particular wind<br />

speeds, to try and alleviate the issue<br />

Page 60 <strong>Draft</strong> <strong>National</strong> <strong>Wind</strong> <strong>Farm</strong> <strong>Development</strong> <strong>Guidelines</strong> – 2 <strong>July</strong> <strong>2010</strong>

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