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BBWC
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> Breeding Bird Survey
In 1994 the
BTO/JNCC/RSPB Breeding Bird Survey (BBS) was launched following
two years of extensive pilot work and earlier desk-based studies.
The introduction of the BBS was a response to the limitations of
the Common Birds Census (CBC),
which has monitored bird populations since 1962. It was recognised
that there was a need to improve the geographical representation
of UK bird monitoring and, thereby, both species and habitat coverage.
The BBS uses line transects rather than the time-consuming territory-mapping
method used by the CBC. This makes the survey relatively quick and
convenient to undertake, and has been successful in encouraging
a large number of volunteers to take part.
The sampling units are 1
x 1 km squares of the National Grid. They are selected randomly by computer (see
Data Analysis below). The BBS requires a relatively
large sample of survey squares and the aim is to achieve coverage of about 2500
squares in the UK. An important aspect of BBS is its coordination through a network
of BBS Regional Organisers, who are also volunteers. Information and survey forms
are distributed to organisers, who contact volunteers willing to survey the squares
every year, and after the field season, forms are returned to BTO headquarters
via the Regional Organisers.
Fieldwork involves three
visits to each survey square each year. The first is to record details of habitat
and to establish the survey route, the second and third to count birds. A survey
route is made up of two roughly parallel lines, each 1 km in length, although
for practical reasons routes typically deviate somewhat from the ideal. Each of
these lines is divided into five sections, making a total of ten 200 m sections,
and birds and habitats are recorded within these units. The two bird-count visits
are made about four weeks apart (ideally early May and early June), ensuring that
late migrants are recorded. Volunteers record all the birds they see or hear as
they walk along their transect routes. Birds are noted in three distance categories
(within 25 m, 25-100 m, or more than 100 m on either side of the line) measured
at right angles to the transect line, or as in flight. Recording birds within
distance bands is important because it provides a measure of bird detectability
in different habitats and allows population densities to be estimated. The total
numbers of each species, excluding juveniles, in each 200 m transect section and
distance category, are recorded on summary forms, as well as the timing of the
survey and weather conditions. The average time observers spend per visit is around
90 minutes.
In the first year (1994),
1569 plots were surveyed. The number has increased steadily from 1751 in 1995,
1919 in 1996, 2194 in 1997 and 2310 in 1998 to 2379 in 1999, close to the original
target of 2500. Only around a quarter of these plots were covered in 2001, however,
owing to Foot & Mouth Disease access restrictions. Squares are distributed
throughout the UK, and cover a broader range of habitats than the CBC, including
uplands and urban areas. In 1999, 217 species were recorded, 88 from more than
100 squares and a further 13 species from 50-100 squares. For a small number of
species, which are colonial or flocking in habit, it is unclear how well they
are monitored by the BBS but they are not currently monitored by other BTO schemes,
and have therefore been included.
Data
Analysis
Survey squares are chosen randomly using a stratified random sampling approach
from within 83 sampling regions, which in most cases are the standard BTO regions,
based on membership distribution. "Stratified random" means that the
country is divided up into regions ("strata") within each of which a
certain number of survey squares are chosen at random. BBS regions with larger
numbers of potential volunteers are allocated a larger number of squares, enabling
more birdwatchers to become involved in these areas. This does not introduce bias
into the results because the analysis takes annual differences in the coverage
of each region into account.
Change measures between
years are assessed using a log-linear model with Poisson error terms. For each
species, the higher count from the early or late counts for each square is used
in the model (or the single count if the square was visited only once). Counts
are modelled as a function of square and year effects. Each observation is weighted
by the number of 1-km squares in each region divided by the number of squares
counted in that region, to correct for the under- or over-sampling of BBS regions
within the UK. The upper and lower confidence limits of the changes indicate the
certainty that can be attached to each change measure. When the limits are both
positive or both negative, we can be 95% confident that a real change has taken
place.
Trends are presented as
graphs in which annual estimates are shown in blue and their 95% confidence limits
in green. A caveat of "Small sample" is provided where the mean sample
size is less than 50 plots per year.
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