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9 UNDERWATER NOISE MODELLING


9.1 Introduction 1.


This report estimates the underwater acoustic emissions associated with construction, operation and decommissioning at East Anglia THREE and assesses the potential for the impact piling noise to impact marine fauna. The National Physical Laboratory (NPL) has been contracted by East Anglia THREE Limited (EATL) to undertake an assessment of piling noise to inform the Environmental Statement for East Anglia THREE. The methodology for this assessment, described in detail in Section 9.4 and Section 9.5, is designed to estimate the likely underwater noise levels generated by East Anglia THREE construction in order to inform of the potential for the radiated underwater noise to impact sensitive marine fauna. Consideration was also given to the potential for auditory injury from prolonged exposure and the effect of multiple concurrently operating piling vessels on the extent of the impacted area.


2.


The assessment was undertaken in the context of guidance documents and directives relating to underwater noise (JNCC 2010; NPS EN-1 July 2011; NPS EN- 3 July 2011; MSFD 2008/56/EC 2008; Robinson 2014). The Joint Nature Conservation Committee (JNCC) protocol for minimising the risk of injury to marine mammals from piling noise, (JNCC 2010), was used to inform the best practice mitigation approach.


3.


A thorough literature review was conducted to obtain and summarise the most relevant, up-to-date and internationally accepted impact criteria from peer reviewed literature in order to assess the impact on marine mammals and fish. For marine mammals, the work of Southall et al. (2007) and Lucke et al. (2009) was adopted and supported by empirical field work by Brandt et al. (2011) and Tougaard et al. (2009) on free-ranging harbour porpoise. Consideration has also been given to recent work by Kastelein et al. (2012; 2013a; 2013b; 2013c) in test tanks. Fish criteria were adopted from Popper et al. (2006) and Carlson et al. (2007) in terms of injury, while behavioural criteria were devised following the work of McCauley et al. (2000a) and Pearson et al. (1992). Consideration has also been given to recent work by Halvorsen et al. (2011) on fish injury and Mueller-Blenkle et al. (2010) on fish behaviour resulting from sound exposure. The risk posed to fish larvae has also been considered based on the finding of a recent study by Bolle et al. (2011; 2012).


4.


The criteria adopted for this assessment take into account current scientific evidence, and may result in different estimated impact ranges when compared to previous UK windfarm developments. It should also be acknowledged that there are still considerable knowledge gaps in understanding the effects of underwater sound


Preliminary Environmental Information May 2014


East Anglia THREE Offshore Windfarm Appendix 9.1 Underwater Noise Modelling 1


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