Abstract

Impact assessments of offshore wind farm installations and operations on the marine fauna are performed in many countries. Yet, only limited quantitative data on the physiological impact of impulsive sounds on (juvenile) fishes during pile driving of offshore wind farm foundations are available. Our current knowledge on fish injury and mortality due to pile driving is mainly based on laboratory experiments, in which high-intensity pile driving sounds are generated inside acoustic chambers. To validate these lab results, an in situ field experiment was carried out on board of a pile driving vessel. Juvenile European sea bass (Dicentrarchus labrax) of 68 and 115 days post hatching were exposed to pile-driving sounds as close as 45 m from the actual pile driving activity. Fish were exposed to strikes with a sound exposure level between 181 and 188 dB re 1 µPa2.s. The number of strikes ranged from 1739 to 3067, resulting in a cumulative sound exposure level between 215 and 222 dB re 1 µPa2.s. Control treatments consisted of fish not exposed to pile driving sounds. No differences in immediate mortality were found between exposed and control fish groups. Also no differences were noted in the delayed mortality up to 14 days after exposure between both groups. Our in situ experiments largely confirm the mortality results of the lab experiments found in other studies.

Highlights

  • The increasing demand for renewable energy has led to innovative techniques and numerous ambitious projects

  • A first step in this process is to assess the sound level range causing immediate or delayed mortality [2]. Such assessments have been performed for Chinook salmon (Oncorhynchus tschawytscha), hybrid striped bass and common sole (Solea solea), through lab experiments, using different methods to generate highintensity ‘pile driving’ sounds in acoustically controlled chambers [5,6,7]

  • The pile driving sound levels that were measured during the four experiments at 2.5 m below the water surface reached on average SELss = 181–188 dB re 1 mPa2s, rose to SPLpeak = 210– 211 dB re 1 mPa2, and led to SELcum = 215–222 dB re 1 mPa2.s, with 1739 up to 3067 strikes per monopile (Table 2)

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Summary

Introduction

The increasing demand for renewable energy has led to innovative techniques and numerous ambitious projects. For common sole larvae that were exposed to a SELss of 186 dB re 1 mPa2.s for 100 strikes, leading to a SELcum of 206 dB re 1 mPa2.s, no difference in mortality was found between control and exposed groups up to 7 days after exposure [5] Since these laboratory experiments have not yet been verified in the field, there is a need to expose juvenile fishes to the sound exposure levels present in the immediate vicinity of the pile driving activity in order to examine direct or delayed mortality. Sound pressure was measured alongside a piling platform (45 m from the pile) and immediate and delayed mortality in young sea bass (Dicentrarchus labrax) were assessed

Material and Methods
Sound analyses Metrics for the sound pressure p were calculated using Matlab
Results
Findings
Discussion
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