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9.6.2 Operational Phase 129. There are very few reported measurements of wind turbine noise and much of the data that is publicly available is summarised in Wahlberg and Westerberg (2005) and Madsen et al. (2006), with Tougaard and Henriksen (2009) providing a more recent update.


130. Underwater noise from an operational turbine mainly originates from the gearbox and the generator and has tonal characteristics (Madsen et al. 2005; Tougaard and Henriksen 2009). The radiated levels are low and the spatial extent of the potential impact of the operational windfarm noise on marine receptors is generally estimated to be small and turbine noise has generally been considered unlikely to result in any injury to marine mammals (e.g. Tougaard and Henriksen 2009) or fish (Wahlberg and Westerberg 2005). Besides the sound source level the potential for impact will also depend on the propagation environment, receptor’s hearing ability and the ambient sound levels.


131. Marine animals may perceive the radiated tonal components where they exist above the ambient noise levels, which may result in a behavioural response of the receptor or lead to a reduced detection of other sounds due to masking. Previous studies have reported behavioural response to only be likely to occur at close ranges from the turbine (a few metres for fish and harbour porpoise (Wahlberg and Westerberg 2005 and Tougaard and Henriksen 2009, respectively) and possibly up to a few hundred metres for seals (Tougaard and Henriksen 2009). Touggard and Henriksen (2009) further show that even masking from operational noise is unlikely to impact harbour porpoise and seal acoustic communication due to the low frequencies and low levels produced.


132. A relatively recent study, by Scheidat et al. (2011), has reported an attraction of harbour porpoise to an operational Dutch windfarm site where abundance was higher within the windfarm compared to a similar environment in near-by areas. This was assumed to be due to decreased fishing and vessel activity and increased food availability (Scheidat et al. 2011). The authors, however, caution against generic transfer of these results to other windfarms as the response is likely a net result of various factors, which may differ between scenarios. A similar study at the Nysted windfarm for example showed only a partial recovery in harbour porpoise abundance two years into the operational cycle of the windfarm (Tougaard et al. 2005). It should also be noted that the response of a receptor will depend on its physical state and its presence may depend on the drivers for it being in the area and may also result from a change in the environment or habitat.


Preliminary Environmental Information May 2014


East Anglia THREE Offshore Windfarm Appendix 9.1 Underwater Noise Modelling 61


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