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Project background
One area of Scotland that has been documented as a
particular stronghold of white-beaked dolphins is the Minch, situated
between Lewis and the west Scottish mainland. In this region high
densities of white-beaked dolphins were recorded during the 1980s and
1990s at latitudes of 58º–58º30'N (Weir et al., 2001; Reid et
al., 2003). However, a recent study reported an apparent decline in
the occurrence and abundance of white-beaked dolphins in the Minch based
on both long-term stranding records and sightings recorded from the
Ullapool to Stornoway ferry since 2001 (Macleod et al., 2005).
It was suggested that this decline was primarily driven by local
increases in water temperature, with the implication that this species
may decline along the west coast as a result of future climate change
(MacLeod et al., 2005). A simultaneous increase in the
occurrence of short-beaked common dolphins (Delphinus delphis)
within the same region since 2001, has led to the suggestion that this
warmer water species may be moving northwards into the Minch, resulting
in potential competition with white-beaked dolphins (MacLeod et al.,
2005, 2007). The interaction between white-beaked and common dolphins,
their current status and their relation to sea water temperature within
the Minch remains unclear, and the purpose of this project was to
collect dedicated preliminary survey data to clarify these issues.
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Aims
and objectives
The White-Beaked Dolphin Project aims to
improve knowledge of the status and ecology of white-beaked dolphins within
Scottish waters to aid their future conservation and management.
The 2007 field survey was
conducted as a preliminary study into the occurrence of white-beaked dolphins in
the Minch, intended to form a baseline for future fieldwork. The main aims and
objectives of the fieldwork were:
Aim 1
To establish
to what extent white-beaked dolphins still inhabit the Minch, and
whether their distribution and relative abundance remains similar to
that reported in previous years (e.g. in Reid et al., 2003) or
has changed significantly. Simultaneous recording of water temperature
and sightings of other cetacean species (particularly common dolphins)
would allow consideration of reported declines in white-beaked dolphins
related to increasing temperature and competition with other species.
Aim 2
A secondary aim of the project was to collect baseline
data (particularly via photo-identification, behavioural and acoustic
work) on the ecology of white-beaked dolphins in the Minch, to further
understanding of this poorly-studied species in Scottish waters and
examine the potential for a future long-term at-sea study of this
species.
Objectives
The key questions that the survey work aimed to address
were:
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What is the current occurrence (distribution and
relative abundance) of white-beaked dolphins in the Minch, and
has this changed since the 1980/90s? |
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Does white-beaked dolphin distribution in the
Minch contrast with that of any other odontocete species? |
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Are habitat variables such as water temperature
or depth a crucial factor governing white-beaked dolphin
distribution in the Minch? |
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Is it feasible to
establish a long-term study of white-beaked dolphins in the
Minch based on photo-identification methodology? |
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References
MacLeod, C.D., Bannon, S.M., Pierce, G., Schweder, C., Learmonth,
J.A., Reid,R.J. and Herman, J.S. (2005). Climate Change and the Cetacean
Community of North-West Scotland. Biological Conservation, 124: 477-483.
Reid, J.C., Evans, P.G.H. and Northridge, S.P. (2003). Atlas of
cetacean distribution in Northwest European waters. Joint Nature Conservation
Committee, Peterborough, UK.
Weir,
C.R., Pollock, C., Cronin, C. and Taylor, S. (2001). Cetaceans of the Atlantic
Frontier, north and west of Scotland. Continental Shelf Research, 21:
1047-1071.
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© WBDP 2007
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