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Abstract from BTO Research Report No
443:
Banks, A.N., Ellis, P., Holloway, S.J.,
Holt, C., Horner, R., Maclean, I.M.D., Marchant, J., Musgrove, A.J.,
Schofield, R.A., Sheldon J. & Stenning, J.
Surveying waterbirds in Morecambe Bay for the Wetland Bird Survey
(WeBS) Low Tide Count Scheme.
ISBN: 1-904870-76-7
Executive summary
1. Morecambe Bay, north west England, is situated at the confluence
of four major rivers (Kent, Leven, Lune and Wyre) and holds the
largest continuous area of intertidal habitat in the UK. It is designated
as a Special Protection Area (SPA) and Ramsar site on the basis
of its non-breeding waterbird interest.
2. The Wetland Bird Survey (WeBS) is divided into two schemes:
Core Counts, which aim to quantify bird numbers when aggregated
at roost sites, and Low Tide Counts (LTCs), which aim to elucidate
distribution of waterbirds across likely feeding areas.
3. Large sites such as Morecambe Bay are often difficult to survey
at low water, owing to problems such as the range of visibility,
access to potentially dangerous areas of intertidal habitat, and
attracting numbers of volunteers necessary to achieve full coverage.
4. A first attempt was made to undertake co-ordinated counts of
the four Sites of Special Scientific Interest (SSSIs) within the
bay, including five main estuarine channels covered using standard
methodology. The remainder of the bay was covered by aerial survey.
Four counts were made in total, one during each winter month (November
– February).
5. Bird distribution data were plotted on pre-defined sectors on
the estuarine areas, and assigned to cells of a 1 km2 grid for the
aerial survey counts. Relative density of birds at low water across
the whole of Morecambe Bay could thus be determined for the winter.
Important areas for each species found in nationally or internationally
important numbers at the site are considered.
6. Cluster analysis revealed significant ‘hot spots’
of Oystercatcher and small waders within the bay. Although mean
distributions of these species sometimes overlapped with high densities
of cockles and Macoma bivalves, no relationship was found between
mean bird densities and mean bivalve densities.
7. Disturbance events appeared to occur where recorded bird density
was comparatively low, but there are likely to be issues with the
resolution of bird data.
8. No obvious patterns in temporal use of different parts of the
bay were evident, with mean centres of both Oystercatcher and small
waders tending typically towards the east and middle of the bay.
9. Estimates of counter error were made from aerial survey simulations,
with an estimated overall mean error of –31%. At this level
of error, corrected aerial survey counts would still represent underestimates
of Core Count figures from 2004/05.
10. Further ground-truthing of aerial survey counts was not possible
to any degree of accuracy, but broad comparison of counts of one
area made by standard and aerial survey suggested again that aerial
surveys returned lower counts.
11. The suitability of aerial survey for use in WeBS LTCs at Morecambe
Bay and at other large sites is discussed. Refinements to standard
ground survey practice at Morecambe Bay are also suggested.
12. Further research necessary to more closely determine feeding
behaviour and distribution of waterbirds within Morecambe Bay is
considered.
13. Preliminary analysis of digital images of intertidal habitat
taken at another large site with internationally important numbers
of waterbirds (The Wash), obtained through collaboration with RAFOS,
is outlined, as are recommendations for the advancement of this
approach.
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