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2.4
Waterways Bird Survey
The Waterways Bird Survey (WBS) has monitored the population
trends of up to 24 riparian bird species on canals and rivers throughout
the UK since 1974. WBS uses a territory-mapping method like that of
its parent scheme, the Common Birds Census,
to estimate the breeding population of waterbirds on each plot. Detailed
territory maps are prepared that can be compared with habitat data
to show which features of linear waterways are important to breeding
birds. The plots average 4.4 km in length; almost half are slow-flowing
lowland rivers with the rest either fast-flowing rivers/streams or
canals. There are currently around 90 plots distributed throughout
the UK. The proportion of plots in the north and west of England is
higher than existed in the CBC (Marchant
et al. 1990). Wales, Scotland and especially Northern
Ireland are relatively poorly covered.
All fieldwork
is carried out by volunteers. Observers are asked to survey their
plot on nine occasions between March and July, mapping all the birds
seen or heard onto 1:10,000-scale maps. Registrations are then transferred
to species maps, which are analysed to reveal the numbers and positions
of territories for each species. Since 1994, observers have completed
their own territory analysis, based on the scheme's written guidelines,
with results checked by BTO staff. This has successfully speeded
up the processing of WBS data at BTO headquarters. As WBS employs
very similar methods to those of CBC, the validation studies carried
out for the latter generally hold true for WBS (see section
2.2). Marchant
et al. (1990) found that there has been little change
in the composition of the WBS sample in terms of waterway type or
geographical spread. Trend analysis and presentation follows the
same pattern as CBC (section 2.2),
except that the "unrepresentative?" caveat has not been
used. A caveat of "small samples" is provided when the
number of plots is between 10 and 19.
Population changes
along waterways are reported annually in BTO News for around
20 riparian species, of which Goosander is not covered by BBS monitoring.
For specialist waterbirds, including Little Grebe, Mute Swan, Common
Sandpiper, Kingfisher, Sand Martin, Grey Wagtail, Dipper and Reed
Warbler, targeted surveys along waterways can provide a better precision
of monitoring than is possible through the more generalised BBS
surveys. WBS indices can also add a new perspective on trends in
waterbirds that are monitored, largely in other habitat types, by
CBC/BBS. For Lapwing, populations
declined rapidly on arable farmland during the late 1980s while
numbers on WBS plots, typically representing populations along river
floodplains, showed greater stability. Yellow
Wagtails have declined much more steeply in WBS habitats
than elsewhere.
WBS has similar limitations as a monitoring scheme that led to
the CBC's replacement by BBS. In particular, plot distribution is
biased geographically and possibly also towards sites that are good
for birds, and an intensive survey method is used that severely
limits the sample size
(Marchant et al.
1990). A drawback specific to WBS is that it covers
only waterbirds.
BTO has addressed these issues by setting up the Waterways
Breeding Bird Survey (WBBS), which has been running since
1998 in parallel with WBS. WBBS uses BBS-style transect methods
along random waterways, and includes all species of birds. If, once
its development is completed, WBBS becomes an ongoing scheme, it
will provide useful monitoring data to supplement BBS.
Data
analysis
Smoothed population trends are estimated using Generalized Additive
Models, with confidence intervals calculated by bootstrapping (Fewster
et al. 2000). The analytical procedure is the same
as that used for the CBC (section 2.2).
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