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
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
Knowledge on habitat use of the wintering seabirds and the factors governing<br />
their distribution is generally poor, especially <strong>for</strong> the offshore area. Despite<br />
the unknowns it is evident that, seen in a North Atlantic perspective,<br />
the waters off West Greenland are very important <strong>for</strong> seabirds (Barrett et al.<br />
2006).<br />
4.7.5 Selected species<br />
A number of seabird species important <strong>for</strong> the assessment area are briefly<br />
described in the following pages. For some species, the at-sea distribution is<br />
shown <strong>for</strong> different seasons of the year, based on available ship and aerial<br />
survey data collected in the period 1988-2010. At the time of data extraction<br />
this corresponded to 25 ship surveys (1988-2010) and 3 aerial surveys (1996-<br />
2009). Seabird densities were calculated as follows. <strong>The</strong> original survey transects<br />
were split into 3 km segments, and <strong>for</strong> each segment a density was calculated<br />
on the basis of the number of birds of the particular seabird species<br />
observed, the length of the segment, and an effective search width estimated<br />
separately <strong>for</strong> each survey and species by means of distance sampling methods<br />
(Buckland et al. 2001). Survey by survey the densities were interpolated<br />
to 3x3 km raster grids by inverse distance weighting (power 2, radius 15<br />
km), and the densities shown on the maps represent the mean value in an<br />
overlay analysis of these grids (divided into four seasons). Densities were<br />
calculated only within a 15 km buffer around the survey transects. Note that<br />
the number of overlapping surveys varies markedly between seasons and<br />
areas (Fig. 4.7.3).<br />
Northern Fulmar, Fulmarus glacialis<br />
<strong>The</strong> number of breeding fulmars in the assessment area is very low, probably<br />
no more than a few hundred pairs, and, moreover, the few colonies seem<br />
to be unstable in time and space (Boertmann et al. 1996).<br />
In the offshore areas fulmars are numerous and occur almost everywhere,<br />
except <strong>for</strong> in winter when only few are present (Fig. 4.7.4). <strong>The</strong>y usually<br />
avoid areas with high ice coverage. Concentrations are linked to <strong>for</strong>aging areas<br />
and such may occur at ice edges, upwelling areas and areas with commercial<br />
fisheries.<br />
<strong>The</strong> fulmar has a favourable conservation status in Greenland and it is not<br />
included on the Greenland Red List (Boertmann 2007, listed as of ‘Least<br />
Concern’ (LC)).<br />
Fulmars have medium sensitivity to oil spills both on an individual level<br />
and a population level. Breeding colonies are among the most sensitive areas,<br />
because fulmars often rest on the water surface here. Recurrent offshore<br />
concentration areas are not known, but may occur e.g. at upwelling areas.<br />
99