Abstract

Abstract1. Offshore windfarms require construction procedures that minimize impacts on protected marine mammals. Uncertainty over the efficacy of existing guidelines for mitigating near‐field injury when pile‐driving recently resulted in the development of alternative measures, which integrated the routine deployment of acoustic deterrent devices (ADD) into engineering installation procedures without prior monitoring by marine mammal observers.2. We conducted research around the installation of jacket foundations at the UK's first deep‐water offshore windfarm to address data gaps identified by regulators when consenting this new approach. Specifically, we aimed to (a) measure the relationship between noise levels and hammer energy to inform assessments of near‐field injury zones and (b) assess the efficacy of ADDs to disperse harbour porpoises from these zones.3. Distance from piling vessel had the biggest influence on received noise levels but, unexpectedly, received levels at any given distance were highest at low hammer energies. Modelling highlighted that this was because noise from pin pile installations was dominated by the strong negative relationship with pile penetration depth with only a weak positive relationship with hammer energy.4. Acoustic detections of porpoises along a gradient of ADD exposure decreased in the 3‐h following a 15‐min ADD playback, with a 50% probability of response within 21.7 km. The minimum time to the first porpoise detection after playbacks was > 2 h for sites within 1 km of the playback.5. Our data suggest that the current regulatory focus on maximum hammer energies needs review, and future assessments of noise exposure should also consider foundation type. Despite higher piling noise levels than predicted, responses to ADD playback suggest mitigation was sufficiently conservative. Conversely, strong responses of porpoises to ADDs resulted in far‐field disturbance beyond that required to mitigate injury. We recommend that risks to marine mammals can be further minimized by (1) optimizing ADD source signals and/or deployment schedules to minimize broad‐scale disturbance; (2) minimizing initial hammer energies when received noise levels were highest; (3) extending the initial phase of soft start with minimum hammer energies and low blow rates.

Highlights

  • Offshore windfarm developments are anticipated to provide over 30% of UK electricity needs by 2030 (BEIS 2019)

  • Hammer energies increased from approximately 266 kJ to between 744 and 1735 kJ during the 3990 min that it took to install each of the 16 piles

  • Distance from source had the greatest influence on received noise levels (Table 1)

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Summary

Introduction

Offshore windfarm developments are anticipated to provide over 30% of UK electricity needs by 2030 (BEIS 2019). Together with data on local species densities, the number of individuals potentially impacted are used within various modelling frameworks to predict long-term population consequences of construction in relation to baseline (King et al, 2015; Nabe-Nielsen et al, 2018). These assessments have not generally estimated how many animals might be within the near-field zone of instantaneous death or injury during piling activity. If marine mammals are detected, piling should not commence until 20 min after the last detection

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