There were 501 sightings of marine mammals (13,398 individuals) during seismic surveys in UK waters and some adjacent areas in 1999. 14,341 hrs 19 mins were spent watching for marine mammals during seismic surveys in 1999
There were 501 sightings of
marine mammals (13,398 individuals) during seismic surveys in UK
waters and some adjacent areas in 1999. 14,341 hrs 19 mins were
spent watching for marine mammals during seismic surveys in
1999.
The most frequently seen species
was the white-beaked dolphin. White-sided dolphins, sperm whales,
minke whales and killer whales were also seen with moderate
frequency, with lower numbers of sightings of other species. There
were significantly more sightings of minke whales and white-beaked
dolphins when compared to previous years. Sightings of marine
mammals peaked in August, with most occurring to the west of
Shetland and in the northern North Sea, which reflected the
location and timing of surveys.
After allowing for potential
sources of bias (location, season, weather conditions) the sighting
rate of white-sided dolphins was found to be significantly lower
during periods of shooting (excluding during low power site
surveys). Sighting rates of minke whales, sperm whales,
white-beaked dolphins and all dolphins combined did not differ
significantly with seismic activity.
After taking account of weather
conditions at the time of the sighting, white-beaked dolphins, all
dolphins combined and all baleen whales combined were found to be
significantly further from the airguns when they were firing than
when they were silent (excluding site surveys).
Some effects of seismic activity
on the behaviour of marine mammals were evident during seismic
surveys (excluding site surveys). There was an increased tendency
for cetaceans to engage in fast swimming and breaching, jumping or
somersaulting during periods of shooting. This increased tendency
was evident at distances of up to 4 km or more from the source for
breaching, jumping or somersaulting, and at distances of up to 3 km
for fast swimming. Positive interactions of cetaceans with the
survey vessel or its equipment occurred significantly more often
when the airguns were not firing.
When all cetaceans were combined,
significantly more were found to be heading away from the vessel
and fewer heading towards it during periods of shooting (excluding
site surveys). More were also milling or travelling in various
directions during periods of shooting. When all baleen whales were
combined, significantly more were found to be heading away from the
vessel during periods of shooting; for white-beaked dolphins and
all dolphins combined significantly fewer were heading towards the
vessel when the airguns were firing.
No significant effects of seismic
activity were observed for site surveys, but sample sizes were low,
precluding allowance for potential sources of bias such as weather
conditions.
Both notification and a report
were received by JNCC for 81% of seismic surveys taking place
during 1999 (in blocks licensed in the 16th, 17th and 18th rounds
of offshore licensing).
The duration of pre-shooting
searches for marine mammals met or exceeded the required minimum of
30 minutes for 85% of occasions when the airguns were used during
daylight hours in blocks where compliance with the guidelines was a
licence condition. On 6% of occasions when the airguns were used
during daylight hours in these blocks there was no pre-shooting
search, while on 9% of occasions the pre-shooting search was
shorter than the required minimum duration or was terminated
prematurely. The proportion of short or absent pre-shooting
searches was higher in other blocks. Short or absent pre-shooting
searches occurred more frequently when fishery liaison officers or
members of ships' crews were acting as marine mammal observers than
when dedicated marine mammal observers were used; members of ships'
crews were the least likely to perform an adequate pre-shooting
search.
Excluding site surveys, 87% of
soft-starts met or exceeded the required minimum duration of 20
minutes in blocks where compliance with the guidelines was a
licence condition. Short or absent soft-starts were more frequent
in other blocks. Short or absent soft-starts were more frequent
when dedicated marine mammal observers were not present.
Marine mammals were seen within
500 m of the airguns shortly before shooting was due to commence on
seven occasions in blocks where compliance with the guidelines was
a licence condition. The guidelines require that in such
circumstances shooting should be delayed for a minimum of 20
minutes after the animals are last seen; on two of the seven
occasions no action was taken to minimise disturbance to the marine
mammals and shooting commenced shortly after they were seen, while
on a third occasion the delay was shorter than the minimum required
and the subsequent soft-start was also short.
Dedicated marine mammal observers
were much more efficient at detecting marine mammals than other
personnel - mean sighting rates for dedicated marine mammal
observers were more than eight times higher than that of other
personnel. Dedicated marine mammal observers also made fewer errors
when completing the recording forms.
The proportion of seismic surveys
using dedicated marine mammal observers has steadily increased
since the introduction of the guidelines, although in 1999 it was
still only on a minority of surveys that such observers were used.
The use of dedicated marine mammal observers is recommended, both
in terms of compliance with the requirements of the guidelines and
the provision of accurate data. Sole reliance on members of ships'
crews to carry out observations of marine mammals was found to be
the least effective alternative.
Revised standard recording forms
are proposed in line with comments and suggestions received. A
number of items for consideration when the Guidelines for
minimising acoustic disturbance to marine mammals from seismic
surveys are next revised are discussed.
Low sample sizes for many species
limited the use of the data. It is recommended that the next
analysis performed combines data from 1998, 1999 and 2000. As the
recording forms have remained the same throughout these three years
this would provide an opportunity to increase sample sizes, both
for individual species and for site surveys.