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Ringing &
Migration
Journal of the BTO Ringing Scheme |
Ringing & Migration Volume
22 Part
Abstracts
[ For abstracts from Ringing
Group Reports click here
]
Plumage temperatures of Dippers Cinclus
cinclus on the roost and in the hand: implications for handling
small passerines
JOHN DAVENPORT*, JOHN O’HALLORAN and PAT SMIDDY
Department of Zoology, Ecology and Plant Science, and Environmental
Research Institute, University College Cork, Lee Maltings, Prospect
Row, Cork, Ireland.
The outer breast plumage temperature of Dippers Cinclus cinclus
roosting beneath river bridges was measured using an infra red thermometer
over the environmental temperature range –0.8 to +10.9°C.
Plumage temperature was close to, and directly related to, the temperature
of the birds’ surroundings, but significantly higher (ΔT
= 2.87°C), suggesting slight heat loss across the plumage to
the environment. Plumage temperatures were also measured in Dippers
held in the hand; they were much elevated over environmental temperatures
(ΔT = 17-18°C at 0°C), indicating substantial heat loss
during handling.
The Origins of moulting Goosanders on
the Eden Estuary
P. LESLIE HATTON1 and M. MARQUISS2*
1Edenvale, Lydox Cottages, Dairsie, Fife KY15 4RN, UK 2Centre for
Ecology & Hydrology, Hill of Brathens, Banchory AB31 4BW, UK
Moulting Goosanders were counted on the Eden estuary, Fife, UK
from 1979 to 1994, and some of these birds were caught and wing-tagged
from 1992 to 1994. This paper documents changes in numbers of moulting
birds, and their provenance, as determined from subsequent sightings.
Goosanders only started to moult on the Eden estuary in the 1980s
and their numbers have increased since the late 1980s. This increase
also occurred elsewhere on other, geographically similar, Scottish
east-coast estuaries. The birds are adult females, and many, though
not all, seem faithful to their moult site. Moulting flocks persist
from June to October, with a turnover of birds occurring during
this period. The moulting birds are drawn primarily from wintering
and breeding areas to the south and west of the Eden estuary, in
southwest Scotland, England and Wales.
Some aspects of Chaffinch Fringilla coelebs
biology, based on an analysis of individuals ringed during 1991
to 2003 in Norfolk, England
STEPHEN J. BROWNE
The Game Conservancy Trust, Fordingbridge, Hampshire SP6 1EF, UK
From 1991 to 2003, 2,954 Chaffinches Fringilla coelebs were caught
and ringed, year-round, at Hilborough, Norfolk, England. The age
and sex composition of Chaffinches varied between winters, but no
systematic pattern was apparent. The age and sex composition of
Chaffinches caught during winter did not vary significantly from
that of Chaffinches caught during the breeding season. Chaffinch
wing lengths and body weights did not vary significantly between
seasons. Male Chaffinches had wings that were on average 6 mm longer
than females and adult wings were on average 2-3 mm longer than
immatures and juveniles. Male Chaffinches were on average 2 g heavier
than females. Approximately 40% of juvenile Chaffinches retained
unmoulted greater coverts after their post-juvenile moult, retaining
1.47 ± 0.04 and 1.67 ± 0.09 for males and females
respectively. Compared to immature females, twice as many immature
males retained juvenile greater coverts. Over the period of study,
Chaffinches showed relatively consistent annual productivity, with
captures of between 1.5 and 2 times as many juveniles or immatures
as adults during the months following the breeding season. The higher
productivity in some years was not explained by variations in average
monthly temperature during the breeding season. The mean duration
between initial and final capture on the study site was between
1.6 and 2.3 years, and the longest period between initial capture
and last recapture was over ten years. Only 0.14% of Chaffinches
were recorded moving distances greater than 5 km from the site of
capture, confirming the sedentary nature of the species. This study
shows that few, if any, continental immigrants supplement the local
Chaffinch population at the study site in Norfolk.
Bird ringing in Britain and Ireland in
2003
Jacquie A. Clark*, Robert A. Robinson,
Dawn E. Balmer, Sue Y. Adams, Mark P. Collier, Mark J. Grantham,
Jeremy R. Blackburn and Bridget M. Griffin
BTO, The Nunnery, Thetford, Norfolk IP24 2PU, UK
This is the 67th annual report of the British Trust for Ornithology’s
Ringing Scheme, covering work carried out, and data received, in
2003. During the year, reports of ringed birds were used to assess
the post-release survival of rehabilitated individuals. Varying
proportions of different species were able to re-enter the population,
with Mute Swan Cygnus olor being the most successful. The origins
and age structure of Guillemots Uria aalge ringed in Britain &
Ireland and found dead after five major oil spills in European waters
were found to vary depending on the location of the oil spill. More
immature birds and birds from eastern colonies tended to be found
after spills that were further south, whereas spills in the north
had a greater effect on adults and birds from western colonies.
Work on mass gain strategies in Blackbirds Turdus merula showed
that they put on mass in winter, when the threat of starvation is
greatest, as well as changing mass through the day, again probably
in response to the likelihood of starvation. A study of the survival
of passerines in the few weeks after fledging found that the survival
rate during this critical period is only about one sixth of the
rate in the rest of the first year of life. A study of the demography
of Spotted Flycatcher Muscicapa striata showed that changes in post
fleding survival were the most likely mechanism for the observed
population decline. Data gathered as part of the Constant Effort
Sites (CES) Scheme showed that adult abundance among resident species
was generally high, following a good breeding season in 2002. When
compared to 2002, fledgling productivity in 2003 was lower, probably
as a result of cold, wet weather during the breeding season. A total
of 111 Retrapping Adults for Survival (RAS) studies submitted data
covering 43 species. Target species for future work were identified.
Continuing work on the winter movements of farmland passerines showed
variations in the distances moved by different species. Over 11,000
Swallows Hirundo rustica were ringed as part of the Swallow Roost
Project. The total number of birds ringed (848,532) increased for
the second year and was 5% above the mean of the previous five years
(1998-2002). The recovery total (11,554) was also 5% up on the five-year
mean (1998-2002). Recoveries of 180 BTO-ringed birds and 76 ringed
abroad are presented in the report; those included confirm known
or suspected movement patterns or are unexpected movements.
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