Kastelein Ronald A, Jennings Nancy, Kommeren Aimée, Helder-Hoek Lean, Schop Jessica
Sea Mammal Research Company (SEAMARCO), Julianalaan 46, 3843 CC Harderwijk, The Netherlands.
Dotmoth, 1 Mendip Villas, Crabtree Lane, Dundry, Bristol BS41 8LN, United Kingdom.
Mar Environ Res. 2017 Sep;130:315-324. doi: 10.1016/j.marenvres.2017.08.010. Epub 2017 Aug 31.
The foundations of offshore wind turbines are attached to the sea bed by percussion pile driving. Pile driving sounds may affect the behavior of fish. Acoustic dose-behavioral response relationships were determined for sea bass in a pool exposed for 20 min to pile driving sounds at seven mean received root-mean-square sound pressure levels [SPLrms; range: 130-166 dB re 1 μPa; single strike sound exposure level (SEL) range: 122-158; 6 dB steps]. Initial responses (sudden, short-lived changes in swimming speed and direction) and sustained responses (changes in school cohesion, swimming depth, and speed) were quantified. The 50% initial response threshold occurred at an SEL of 131 dB re 1 μPa s for 31 cm fish and 141 dB re 1 μPa s for 44 cm fish; the small fish thus reacted to lower SEL than the large fish. Analysis showed that there is no evidence, even at the highest sound level, for any consistent sustained response to sound exposure by the study animals. If wild sea bass are exposed to pile driving sounds at the levels used in the present study, there are unlikely to be any adverse effects on their ecology, because the initial responses after the onset of the piling sound observed in this study were short-lived.
海上风力涡轮机的基础通过打桩与海床相连。打桩声音可能会影响鱼类的行为。在一个水池中,对海鲈进行了实验,使其暴露于七种平均接收的均方根声压级[SPLrms;范围:130 - 166 dB re 1 μPa;单次撞击声暴露级(SEL)范围:122 - 158;步长为6 dB]的打桩声音下20分钟,确定了声学剂量 - 行为反应关系。对初始反应(游泳速度和方向的突然、短暂变化)和持续反应(鱼群凝聚力、游泳深度和速度的变化)进行了量化。对于31厘米长的鱼,50%初始反应阈值出现在SEL为131 dB re 1 μPa·s时;对于44厘米长的鱼,该阈值为141 dB re 1 μPa·s;因此小鱼对较低的SEL做出反应。分析表明,即使在最高声级下,也没有证据表明研究动物对声音暴露有任何一致的持续反应。如果野生海鲈暴露于本研究中使用的打桩声音水平,对其生态不太可能有任何不利影响,因为在本研究中观察到的打桩声音开始后的初始反应是短暂的。