The Davis Strait - DCE - Nationalt Center for Miljø og Energi
The Davis Strait - DCE - Nationalt Center for Miljø og Energi
The Davis Strait - DCE - Nationalt Center for Miljø og Energi
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192<br />
both until the end of the beluga whale hunt and the period of occupation of<br />
especially important beluga whale habitats. Some particularly important beluga<br />
whale areas were even completely closed <strong>for</strong> surveys.<br />
In the NERI guidelines <strong>for</strong> seismic surveys (Boertmann et al. 2010) some important<br />
issues to consider in assessing the impacts of seismic surveys were<br />
listed:<br />
• <strong>The</strong> species that could be affected; as tolerance to seismic surveys varies<br />
between species<br />
• <strong>The</strong> natural behaviour of these species when surveys are taking place.<br />
Disturbance varies according to species' annual cycles, e.g. the degree of<br />
sensitivity of animals engaged in mating and calving or those feeding or<br />
migrating.<br />
• <strong>The</strong> severity and duration of impact. Even a strong startle reaction to an<br />
approaching survey vessel may have only a small total impact on the animal<br />
whereas a small, but prolonged (days or weeks) disturbance to feeding<br />
behaviour could have a much greater impact.<br />
• Total number of animals likely to be affected. It is not possible to conduct<br />
seismic surveys in the Arctic without affecting marine mammals at all.<br />
<strong>The</strong> number of animals likely to be affected should be assessed in relation<br />
to the size of the population, local stocks and season.<br />
• Local conditions <strong>for</strong> sound transmission, such as hydr<strong>og</strong>raphic and<br />
bathygraphic conditions, may result in highly unusual sound transmission<br />
properties. Potential consequences of these effects should be included<br />
in the assessment.<br />
When planning surveys ef<strong>for</strong>ts should be made to minimise the overall exposure<br />
to the degree possible by using the smallest airgun array that enables<br />
collection of the data needed. Total exposure is a complex function of the<br />
number of animals exposed, the time each animal is exposed and the sound<br />
level each animal experiences. Nevertheless, reducing any of these three parameters<br />
would reduce the total exposure, so the possibility of reducing one<br />
or more factors should be considered in the planning phase.<br />
Conclusions on disturbance from seismic noise (Table 10.1.1)<br />
<strong>The</strong> VECs most sensitive to seismic noise in the assessment area are the baleen<br />
whales, minke, fin, blue and humpback, and toothed whales such as<br />
sperm and bottlenose whales. <strong>The</strong>se may be in risk of being displaced from<br />
critical summer habitats. A displacement will also impact the availability<br />
(<strong>for</strong> hunters) of whales if the habitats include traditionally hunting grounds.<br />
Narwhals, beluga whales, bowhead whales and walruses are also sensitive<br />
to seismic noise, but their occurrence will only overlap with seismic surveys<br />
during winter.<br />
As seismic surveys are temporary, the risk of long-term impacts is low. But<br />
long-term impacts have to be assessed if several surveys are carried out<br />
simultaneously or in the same potentially critical habitats during consecutive<br />
years (cumulative effect). <strong>The</strong>re is a small risk of long-term effects <strong>for</strong><br />
toothed whales suffering permanent auditory damage caused by critical exposure<br />
to seismic noise.