PURCHASED
TRING LIBRARY
Bulletin of the African Bird Club Vol 17 No 1 March 2010
Identification and
geographical variation
in African Goshawk
Status of Short-clawed
Lark in south-east
Botswana
The Lubango Bird Skin
Collection, Angola
Bird observations from
Sao Tome: Monte
Carmo as a priority site
for conservation
Identification of
Friedmann’s Lark
Madagascar
Serpent Eagle
Finding the special
endemics of southern
Ethiopia
ISSN 1 352-481 XISSN 1352-481X
African
• • .
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• provide a worldwide focus for African ornithology
• encourage an interest in the conservation of the
birds of the region
• liaise with and promote the work of existing region-
al societies
• publish a twice-yearly colour bulletin
• encourage observers to visit lesser known areas of
the region
• encourage observers to actively search for globally
threatened and near-threatened species
• run the ABC Conservation Programme
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Membership is open to all. Annual subscription rates are:
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ABC is always looking for drawings and photos to publish in the
Bulletin. If you are interested in contributing, please contact the
Graphics Editor, Pete Leonard, pleonard@care4free.net
Bird Club
ABC Council
Phil Atkinson (Vice-Chairman, co-opted), Keith Betton (Chairman),
John Caddick (Treasurer), Stephen Cameron (co-opted), Clive
Dickson, Chris Magin, Geoff Randall (Secretary), Nigel Redman,
Stephanie Tyler and Alan Williams
President: Tasso Leventis
Vice President: Martin Woodcock
Bulletin Editorial Board
Chairman of the Board: Keith Betton
Managing Editor: Guy Kirwan
Assistant Editor: Ron Demey
David Allan, Chris Bowden, Callan Cohen, Lincoln Fishpool, Peter
Lack, Pete Leonard (Graphics Editor), Jeremy Lindsell and Steph
Tyler
Contact ABC
African Bird Club, c/o BirdLife International, Wellbrook Court,
Girton Road, Cambridge CB3 ONA. E-mail: • info@africanbirdclub.
org • website: http://www.africanbirdclub.org
Further information can be obtained directly from individual
Council members by writing to them at the Club’s postal address,
or by e-mail as follows:
Chairman Keith Betton • chairman@africanbirdclub.org
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Treasurer John Caddick • treasurer@africanbirdclub.org
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Conservation Officer Steph Tyler
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• reps@africanbirdclub.org
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• corporatesponsors@africanbirdclub.org
ABC particularly wishes to thank its Corporate Sponsors for their invaluable financial support in 2010: Abacus African Safaris, Ashanti
African Tours, Access Africa Safaris, Aim 4 Africa, Ben’s Ecological Safaris, Bird Feeding Station, Birdfinders, Birding Africa, Birding
and beyond Safaris, Birding Ecotours, Birdquest, Birdwatching Breaks, Calluna Books, Crystal Safaris, Field Guides, Greentours, Hyde-
Lascelles, Lake Kitandara Tours and Travel, Lawson’s Birdwatching Tours, Limosa Holidays, MKA Ecology, Naturetrek, Ornitholidays,
Rockjumper, Sarus Bird Tours, Sunbird, Turaco Tours, Turtle Bay Beach Club, WildSounds, Wildwings, and Zeiss.
The Bulletin of the African Bird Club
The Bulletin of the ABC provides a forum for news, letters,
notices, recent publications, expedition results, reviews and
interim publication of studies on African birds by contribu-
tors from throughout the world. Publication of results in the
Bulletin of the ABC does not preclude publication of final
results as journal papers either by the ABC or elsewhere. No
material should, however, be submitted simultaneously to the
Bulletin of the ABC and to any other publication.
Brief notes for contributors appear elsewhere in this Bulletin
and further details are available from the Editor (editor@
africanbirdclub.org).
©2010 Copyright African Bird Club and contributors. Quotations should carry a full acknowledgement. No part etc may be
reproduced, copied or stored in a retrieval system without the prior written permission of the Club or authors.
Contents
Bull ABC Vol 17 No 1
— " V »4 € -f#W
^tSTORTMUSEUM
2 6 APR 2010
tring library
News & Comment
2
Club News
Compiled by Alan Williams
19
5
Conservation Fund News
10
Africa Round-up
Compiled by Ron Demey, Guy
32
M. Kirwan and Peter Lack
43
18
Advertising information
65
Corrigenda
99
Little-known African bird:
Madagascar Serpent
54
Eagle Eutriorchis astur
Jonathan C. Eames
66
72
102
Photospot: Friedmann’s
Lark Mirafra pul pa
Nik Borrow
79
114
Recent Reports
Compiled by Ron Demey
82
128
Reviews
132
Letters to the Editor
85
136
Notes for Contributors
Photographs
Jason Anderson, Ruben Barone, P.
Bentley, Kris Blachowiak, Nik Borrow,
R. S. Boyes, Artur Bujanowicz, John 90
Caddick, Simon Colenutt, Toby Collett,
John Cooper, Daniel Cornelis, Greg
Davies, Paul Donald, Jonathan C.
Eames, Augusto Faustino, S. Ferwerda, **
Daphne Gemmill, Bernard Hanus, Jens
Hering, A. P. Leventis, Tess Macdonald, 97
Ian Merrill, Johannes & Sharon Merz,
Michael Mills, Phoebe Munyoro, Georges
Olioso, Fdbio Olmos, Phil Palmer, 1 06
Guillaume Passavy, Bruno Portier, Dave
Richards, Adam Riley, Steve Rooke, Peter
Ryan, Eugenie Skelton, Axel Smets, Claire
Spottiswoode, GeojJJ & Hilary Welch,
Manfred Wichmann, Alan Williams,
Malcolm Wilson.
Front cover plate
Double-toothed Barbet /
Barbican bidente Lybius bidentatus
by Ian Fulton
Features
Plumage variation in African Goshawk Accipiter tachiro and
its separation from congenerics in equatorial Africa Michel
Louette; illustrated by Nik Borrow
Status of Short-clawed Lark Certhilauda chuana in south-
eastern Botswana Chris A. Brewster, Keddy Mooketsa and Marc Herremans
Cataloguing the Lubango Bird Skin Collection: towards
an atlas of Angolan bird distributions Michaels. L. Mills, Ursula
Franke, Grant Joseph, Francisco Miato, Suzanne Milton, Ara Monadjem, Dieter
Oschadleus and W. Richard J. Dean
Bird observations from Sao Tome: Monte Carmo as a priority
Conservation site Fdbio Olmos and Longtong G. Turshak
First records of eight bird species for Eritrea Jason Anderson
Recent bird records from Fogo, Cape Verde Islands Ruben
Barone and Jens Hering
The separate African winter quarters of Pied Flycatcher
Ficedula hypoleuca and Collared Flycatcher F. albicollis Robert J.
Dowsett
First breeding record and passage of Eurasian Sparrowhawk
Accipitar nisus in Libya Jens Hering, Elmar Fuchs and Stefan Brehme
Correction of three historical bird records from Libya Adriano
De Faveri and Nicola Baccetti
Rock Firefinch Lagonosticta sanguinodorsalis and its
brood parasite, Jos Plateau Indigobird Vidua maryae,
in northern Cameroon Michaels. L. Mills
Rufous Fishing Owl Scotopelia ussheri camera-trapped at
midday near Tiwai Island, Sierra Leone April Conway, Sonia
Hernandez and John P. Carroll
Noteworthy bird records from Sao Tome and Principe Phillip
Hall, A. P. Leventis, Fdbio Olmos, Stephen Rumsey and Longtong Turshak
Display behaviour of Shelley’s Oliveback Nesocharis shelleyi
Michael S. L. Mills
Finding southern Ethiopia’s endemic birds Claire N. Spottiswoode
Bull ABC Vol 17 No 1 (2010) - 1
Club News
2009 British Birdwatching Fair
The worldwide economic difficulties
led to much concern about the
impact this might have on the
premier UK birdwatching event,
the annual Birdwatching Fair held
at Rutland in central England.
Everyone was pleased to see a
favourable weather forecast, and
this brought record attendances
over the three days of the fair in
August 2009. Business seemed as
brisk as usual. The Club had its
usual presence, a stand in Marquee
4, which was manned by Council
members and other volunteers. Once
again, thanks go to those who give
freely of their time to ensure that
members can meet those involved
in running the Club. In particular,
Geoff & Bev Randall designed and
set up the stand, and ensured that
the sales section was as successful
as usual. It is also an opportunity
to promote the pleasures of birding
in Africa and to persuade interested
non-members to join the Club. One
member of Council, Nigel Redman,
had a particularly busy time with
his talk on ‘Birds of the Horn of
Africa’, as our representative on the
Figure 1. Nigel Redman signing a
copy of Birds of the Horn of Africa at
the Rutland Birdfair, August 2009
(Alan Williams)
Nigel Redman signant un exemplaire
de Birds of the Horn of Africa au
Birdfair de Rutland, aout 2009
(Alan Williams)
‘Bird Brain of Britain’ quiz team and
helping out on the stand. The fair
also permits the Club to meet some
of our Corporate Sponsors, of which
there are currently over 30. Their
invaluable financial support helps
maintain the standard of the Bulletin.
The full list of Corporate Sponsors
appears on the inside front cover.
ABC AGM Minutes and Accounts
In future, to save space it has been
decided not to publish the summary
accounts and AGM minutes in the
Club News section of the Bulletin.
Copies of these will be posted on the
website and any member can obtain a
copy from the Secretary by e-mailing
secretary@africanbirdclub.org or by
writing to the Club's postal address.
Overseas payment schemes
The Club has set up several
local payment schemes whereby
membership payments can be made
in local currency via a partner
organisation. The membership
benefits are the same as for a member
paying in sterling. The income
received is, however, retained in the
country where the scheme is run
Figure 2. A visitor to the ABC stand
being persuaded to ‘Find the Plover’
by Chris Bowden, Rutland Birdfair,
August 2009 (Alan Williams)
Un visiteur au stand du ABC en train
de se laisser persuader de «Trouver le
Pluvian d’Egypte» par Chris Bowden,
Birdfair de Rutland, aout 2009
(Alan Williams)
and is used to fund agreed local
conservation projects. Local payment
schemes are currently active in
Kenya, Uganda, Madagascar, South
Africa and Zimbabwe. If you are a
resident of any of these countries and
wish to pay your membership fees in
your local currency (at a significant
discount compared to the prevailing
sterling fees) please contact Alan
Williams, Membership Secretary via
membership@africanbirddub.org.
Martin Woodcock’s Safari
Sketchbook
The last few years have seen the
publication of many fine new or
revised field guides to various African
countries, but a completely different
look at African birds is now in the
offing. Six years after the last volume
of The Birds of Africa appeared,
Martin Woodcock, the principal
illustrator of those volumes, has gone
back to the sketchbooks and journals
made during his field trips for that
work and selected the material for
a new book, Safari Sketchbook — A
Bird Painter’s African Odyssey, to be
published in spring 2010.
While many of the African trips
involved fairly intensive birding,
others allowed time for much
drawing in the field. Sketches in
pencil and watercolour, and some
in oil, show a wide variety of birds.
Some trips were focused on netting
forest birds, whilst others were more
general, so that the work ranges from
impressions of birds as you see them
in the field to more detailed portraits,
studies of birds in the hand, and
sketches of landscapes and habitats.
Much of this work resulted from
some lengthy visits to East Africa,
especially Tanzania and Kenya, but
studies from Ethiopia, Uganda and
Cameroon are also included.
Nearly 200 pages from the
sketchbooks are complemented by
a lively text, in which anecdotes,
2-BullABCVol17No1 (2010)
Club News
Figure 3. Kenneth Gbenga, ABC’s
representative in Sierra Leone and
Rockjumper’s ground agent receiving a
copy of Birds of Western Africa donated
by ABC and presented by John
Caddick (John Caddick)
Kenneth Gbenga, representant du
ABC en Sierra Leone et agent de
Rockjumper, recevant un exemplaire
de Birds of Western Africa offert par
le ABC et remis par John Caddick
(John Caddick)
‘incidents of the route’, a little
poetry and some history enhance
the underlying ornithology. All this
will bring back vivid memories for
anyone who has birded in Africa.
For further derails and an
order form, see Martin’s website
(martinwoodcock.co.uk) or write
to The Esker Press, Furlongs, Long
Lane, Wiveton, Norfolk NR25
7DD, UK. Sales to ABC members,
if they mention this when ordering,
will benefit the Club’s Conservation
Fund.
Sales Officer vacancy
Geoff & Bev Randall are standing
down from their roles as Secretary
and Sales Officer respectively.
Although the post of Secretary is
likely to be filled at the 2010 AGM,
that of Sales Officer remains vacant
at present. Anyone interested who
can spare time for this important
post should contact Chairman Keith
Betton (chairman@africanbirdclub.
org). Council would like to thank
Geoff and Bev for all their work on
behalf of the Club over many years.
Back issues
Newly joining members are offered
a set of back bulletins at a discount.
However, Vol. 2(1), Vol. 3(1-2),
Vol. 5(1) and Vol. 6(1) are no longer
available and the photocopies we
provide are an inferior substitute. If
you have copies of these issues you
no longer wish to keep', we would be
grateful if you could return them to
the Club at the usual address: African
Bird Club, c/o Birdlife International,
Wellbrook Court, Girton Road,
Cambridge CB3 ONA, UK.
ABC Conservation Tour to Sierra
Leone, 9-23 December 2009
1 he ABC / Rockjumper conservation
tour to Sierra Leone in December
2009 was a great success. Five of the
eight participants travelled direct
from London Heathrow to Freetown,
the country’s capital, on 9 December,
where we were met by Kenneth
Gbenga, our local ground agent and
ABC’s representative in Sierra Leone.
From there we transferred to our
hotel overlooking the Atlantic Ocean.
David Hoddinott, the Rockjumper
tour leader, had been travelling in
Ghana and flight delays meant he
was unable to arrive until the evening
of 10th, whilst the other three
participants, from South Africa, only
joined the group in the afternoon of
the 1 1th due to a flight cancellation.
Birding in the heavily populated
Freetown and Western Peninsula
areas was remarkably productive.
Kenneth took us east of the city for
some roadside and coastal birding,
whilst David took the same direction
next day to the Guma Valley Forest
Reserve, which is owned by the local
water company, and on the 12th
to Freetown’s golf course and the
Regent Forest Reserve. Highlights of
these days included a single White-
backed Night Heron Gorsachius
leuconotus, four Yellow-casqued
Hornbills Ceratogymna elata, an
obliging Little Green Woodpecker
Campethera maculosa and a stunning
male Crimson Seedcracker Pyrenestes
sanguineus. In addition, we found
time to visit the first of two White-
necked Picathartes Picathartes
gymnocephalus roosts only an hour’s
drive from our hotel on poor roads.
After a silent and uncomfortable wait
of an hour on stony ground, we had
good views of a Spotted Honeyguide
Indicator maculatus before the main
event of at least three picathartes
showing well.
Figure 4. Egyptian Plover / Pluvian
fluviatile Pluvianus aegyptius, Moa
River, Tiwai Island, Sierra Leone,
December 2009 (John Caddick)
Figure 5. Forbes’s Plover / Gravelot de
Forbes Cbaradrius forbesi, Kenema rice
fields, Sierra Leone, December 2009
(John Caddick)
The following two days we birded
the pristine forest of Tiwai Island
on the Moa River, situated at the
western edge of Cola West Forest
Reserve, and took an evening boat
trip around the island. Here we
enjoyed a very obliging Egyptian
Plover Pluvianus aegyptius, a Brown
Nightjar Caprimulgus binotatus flying
over the river at dusk, two Hartlaub’s
Ducks Pteronetta hartlaubii with
ducklings, Fire-crested (White-
tailed) Alethe Alethe diademata in the
forest, a stunning male Buff-throated
Sunbird Chalcomitra adelberti
and several Red-vented Malimbes
Malimbus scutatus at a nest.
Having spent the night at
Zimmi, we left early next day for
Gola South, where we had good
views of a juvenile Long-tailed
Hawk Urotriorchis macrourus , Blue
Cuckooshrike Coracina azurea ,
Sharpe's Apalis Apalis sharpii, Red-
billed Helmetshrike Prionops caniceps
and Ussher’s Flycatcher Muscicapa
ussheri. Later, we drove to the large
town of Kenema and spent a couple
Club News
Bull ABC Vol 17 No 1 (2010) -3
of hours birding the rice fields, which
held three species of snipe — Jack
Lymnocryptes minimus , Common
Gallinago gallinago and Great
Snipes G. media — as well as Greater
Painted-snipe Rostratula benghalensis.
Other waders included Forbes’s
Plover Charadrius forbesi as well as
Palearctic migrants such as Yellow
Wagtail Motacilla flava and Red-
throated Pipit Anthus cervinus.
From 16 to 19 December we
visited Gola North. Having started
from Kenema at 04.30 hrs, we
arrived at the local village just after
dawn and spent the rest of the
day birding around the village and
along the 9-km trail to our camp.
We then enjoyed two full days of
birding in the forest, followed by
a final day along the trails back to
the village, before returning to the
hotel at Kenema. The local villagers
participated in the logistical exercise
of getting all the camping gear, food
and cooking equipment to our forest
campsite. Gola North provided views
of several species that may be hard
to observe elsewhere, including Afep
Pigeon Columba unicincta, Blue-
headed Bee-eater Merops muelleri,
Narina’s Trogon Apaloderma narina,
Black Dwarf Tockus hartlaubi,
Red-billed Dwarf T. camurus and
Brown-cheeked Hornbills Bycanistes
cylindricus, Rufous-sided Broadbill
Smithornis rufo lateralis, Green-
tailed Bristlebill Bleda eximius,
Yellow-bearded Greenbul Criniger
olivaceus, Finsch’s Flycatcher Thrush
Stizorhina fins chi, Forest Scrub
Robin Cercotrichas leucosticta, Red-
cheeked Dyaphorophyia blissetti
and Yellow-bellied Wattle-eyes D.
concreta, Fraser’s Sunbird Deleornis
fraseri, Lagden’s Malaconotus lagdeni
and Many-coloured Bushshrikes
Telophorus multicolor and everyone’s
favourite, a single stunning male
Gola Malimbe Malimbus balmanni,
seen after two days searching the
forest. In the evenings back at
camp we enjoyed the delicious tood
prepared by our cook, Edna, sampled
the local ale and listened to the Gola
North choir.
We remained in the Kenema area
on 20 December. After another early
start, we arrived at Kambui North
in time for a pre-dawn breakfast
before setting out on a long climb
to the hill forest. Highlights of the
morning included a single Red-
chested Goshawk Accipiter toussenelii,
a flock of c. 30 Mottled Swifts
Tachymarptis aequatorialis, Red-
headed Malimbe Malimbus rubricollis
and five species of hornbills: African
Pied Tockus fasciatus , a single Black
Dwarf, Piping Bycanistes fistulator,
Brown-cheeked and Yellow-casqued
Hornbills. Following lunch, we set
off for Kambui South and our second
picathartes site. Our local guide
introduced us to the village elders
before we climbed through the forest
to the roost site. This site was more
open and situated alongside a stream
with a small sandy beach, which
afforded us outstanding views of four
White-necked Picathartes coming to
roost. For an hour, we watched these
magical birds just c. 10 m away before
returning to Kenema.
The final three days were
spent birding in savanna between
Kenema and Makeni and in the
Bumbuna area. In this more open
habitat birding and photography
were easier. My personal highlights
were Brown Circaetus cinereus,
Western Banded C. cinerascens
and Beaudouin’s Snake Eagles C.
beaudouini, male and female Red-
chested Flufftails Sarothrura rufa,
a male Yellow-throated Cuckoo
Chrysococcyx flavigularis, Pearl-
spotted Owlet Glaucidium perlatum,
Abyssinian Roller Coracias abyssinicus,
Cassin’s Honeybird Prodotiscus
insignis, Eurasian Wryneck Jynx
torquilla, Fine-spotted Woodpecker
Campethera punctuligera, a
party of White Helmetshrikes
Prionops plumatus. White-breasted
Cuckooshrike Coracina pectoralis,
several Turati’s Boubou Laniarius
turatii. Blackcap Babbler Turdoides
reinwardtii , Emerald Starlings
Lamprotornis iris, Red-winged
Pytilia Pytilia phoenicoptera,
Dybowski’s Twinspot Euschistospiza
dybowskii, Jambandu Vidua raricola
and Cameroon Indigobirds V.
camerunensis , and a male Togo
Paradise Whydah V togoensis in
breeding plumage.
We all enjoyed our time in Sierra
Leone immensely. The people are
very friendly and birds are plentiful
with some 340 species observed
during the tour. The forests also
produced eight species of primate.
Thanks are due to Rockjumper for
organising the tour so successfully
and to David for his ability both to
find new birds and ensure that all
members of the party saw them well.
Kenneth and the local team provided
good logistical support throughout
the tour. The tour continued the
theme of ABC conservation tours of
visiting poorer known countries with
a view to finding little-known species
and, in so doing, generating funds
for ABC’s conservation work. You
can read more about Sierra Leone
and its birds on the Club’s website at
www.africanbirdclub.org/countries/
SierraLeone/introduction.html and
regular visits to the home page will
keep you informed about future tour
plans.
Contributed by John Caddick
A request from the
Slender-billed Curlew
Working Group (SBCWG)
As part of the SBCWG’s work,
the identification of several forms
of Numenius in the Palearctic
and adjacent areas is being
investigated. The group is seeking
photos of Slender-billed Curlew
N. tenuirostris, Eurasian Curlew
N. a. arquata, and the races N. a.
orientalis and N. a. suschkini, as
well as the following subspecies
ofWhimbrel N. phaeopus, the
nominate, N. p. alboaxillaris, N.
p. variegatus, N. p. hudsonicus and
N. p. phaeopus. Photographs taken
in Eastern Europe / Western Asia
are particularly sought. All photos
should be sent to rossahmed@
gmail.com; please include relevant
details such as photographer, date
taken and location. Photos should
preferably not be ‘manipulated’
before sending, although edited
photos are welcome.
4 -Bull ABC Vol 17 No 1 (2010)
Club News
V African Bird Club Conservation Fund
Despite the difficult financial times, ABC has,
with the much-appreciated help of sponsors,
made eight new awards since my last report.
Avifaunal and threat status survey at Yala
Swamp, Kenya
ABC awarded UK£850 to Martin Odino for
an avifaunal and threat status survey in the
north of Yala Swamp IBA in Kenya. This was
made possible by generous sponsorship from
Paul Lascelles (Hyde-Lascelles). The project’s
aims were to: (a) assess threats impacting the
IBA inclusive of those associated with Bunyala
Rice Scheme and its surroundings; (b) compile
a thorough updated checklist of birds and their
relative abundance; and (c) provide a basis to
establish a Site Support Group. Martin led a
three-person team representing the National
Museums of Kenya, Ornithology Section.
Wildlife Direct, a Kenyan-based international
wildlife charity organisation to which Martin
is affiliated, provided publicity. An assistant
was hired to help with identification and data
collection, and a local trainee helped disseminate
the idea of a Site Support Group. Martin has
already submitted an interim report, which can
be seen on the ABC website. He and his team
found 172 species, with Black-headed Gonolek
Laniarius erythrogaster the most frequent, but
no papyrus endemics. Worryingly, the team
found much evidence of habitat destruction and
encroachment on the swamp, as well as deliberate
poisoning on the rice scheme land. Some 55 bird
species were affected by this poisoning.
Support for Sam Osinubi
ABC made an exception to its normal guidelines
and, with support from our President, Tasso
Leventis, helped fund Sam Osinubi to attend
a Sound Analysis Workshop organised by the
Cornell Laboratory of Ornithology in September
2009, as well as have some additional training.
ABC provided UK£900. Sam is a Nigerian
doctoral student, who is studying the behaviour
of Double-toothed Barbet Lybius bidentatus and
Yellow-breasted Boubou Laniarius atroflavus in
Ngel-Nyaki Forest Reserve, Nigeria, which is an
Important Bird Area. The forest is threatened by
grazing and burning that has reduced the Afro-
montane forest habitat to 7.7 km 2 within the
48 km 2 of the reserve. L. atroflavus is a poorly
known endemic. Sam is conducting his research
through the School of Biological Sciences of the
University of Canterbury, New Zealand. His
project investigates the influence that the forest
habitat has on behavioural adaptation and how
this affects the fitness of the species inhabiting
this threatened habitat. The focus will be on
determining how territoriality, vocalisations,
foraging strategy and breeding strategy are
influenced by habitat quality and how adaptation
has resulted in different measures of fitness. The
ultimate aim is to assess the efficacy of behaviour
as a rapid and accurate index of species-specific
habitat quality. Sam was able to stay on for an
extra week after the workshop to permit effective
and complete analysis of his sound data. Cornell
University’s Laboratory of Ornithology is at
the forefront of bio-acoustic research and is the
developer of both the Raven and XBAT sound
analysis computer programs.
Vulture awareness day in Kenya
Nature Kenya received an award to help promote
a Vulture Awareness Day on 10-11 October
2009 at NatureKenya’s Bird Fair in the National
Museum’s grounds. The primary objective was
to increase public understanding and compassion
for vultures — one of the most threatened bird
groups in the world. Vulture Awareness Day in
Kenya was organised by the Raptor Working
Group, a subcommittee of NatureKenya’s Bird
Committee, and sought to increase awareness
about the need to save Kenya’s vultures.
NatureKenya planned to achieve this goal by
operating (1) a nationwide art competition (‘the
role of vultures in maintaining the cycle of
life’) for schoolchildren, (2) a stand at the
Bird Fair to educate visitors on the ecological
importance of vultures and air a documentary
on vulture poisoning, and (3) a play at the fair
highlighting poisoning events that have decimated
Kenya’s vulture populations. In addition,
NatureKenya aimed to raise awareness through
radio programmes and articles in newspapers and
magazines. ABC provided UK£1,000 towards
supporting materials, banners, leaflets, radio
time, booth space, audio-visuals, prizes for the
ABC Conservation Fund
Bull ABC Vol 17 No 1 (2010) -5
f African Bird Club Conservation Fund
Double-toothed Barbet / Barbican bidente Lybius
bidentatus (Dave Richards)
art competition and other incidental costs. The
ABC logo appeared on all of the publicity
items.
Dispersal of Southern Masked Weaver and
other passerines on the Cape Peninsula,
South Africa
ABC contributed UK£500 towards this proposed
study led by Dieter Oschadleus, the bird-ringing
Coordinator of SAFRING, based at the Animal
Demography Unit, University of Cape Town.
There was to be a strong training element in
bird ringing. Dieter wrote ‘Natal dispersal is
poorly studied in African passerine birds due
to the difficulty of covering a large enough area
to recapture birds ringed previously as chicks.
In this study a network of sites will be used on
the Cape Peninsula, where the focus will be on
Southern Masked Weaver Ploceus velatus, which
Southern Masked Weaver / Tisserin a tete rousse
Ploceus velatus (Adam Riley)
has expanded its range into the Western Cape
over the last century. The aim of this study is
to use ringing to determine natal dispersal and
movements by adults at the edge of the species’
new range. At the same time it will be possible
to study the movements of many other common
passerines in the area. During Phase 1 (August-
December 2009), chicks will be ringed; chicks
of other species, particularly Cape Weavers P.
capensis, will also be ringed for comparative
purposes, although search effort for nests of
other species will be limited to incidental finds.
Phase 2 (January-December 2010) will consist
of weekly mist-netting to attempt to recapture as
many chicks as possible. In addition, all birds of
other species caught will be ringed to study the
movements of birds on the Cape Peninsula.’
Eritrean Sociable Lapwing surveys
ABC, via sponsorship from Tasso Leventis,
gave UK£500 to Russom Teklay and colleagues
to undertake surveys in Eritrea for Sociable
Lapwings Vanellus gregarius. The Royal Society
for Protection of Birds (BirdLife UK) provided
an additional UK£750 through ABC. The
project commenced in December 2009. The
6 -Bull ABC Vol 17 No 1 (2010)
ABC Conservation Fund
Erratum (Conservation fund news on pages 6-7): Unfortunately it transpires that the plovers
observed by the team in Eritrea were Black-winged Plovers (Lapwings) and not Sociable Plovers.
V African Bird Club Conservation Fund
team aimed to explore the numbers, distribution
and population trend of Sociable Lapwings
in the central highlands of Eritrea, to identify
special threats to the wintering site, and to
increase local awareness of the birds. On the
first day, the survey team reported 17 Sociable
Lapwings 28 km south-west of Asmara, but
next day the team counted only eight birds. On
25 December the survey team counted over 69
in the southern plains, near the small town of
Dibariwa, over 12-15 km, and next day the
team observed 54 around Mendefera. Russom
wrote ‘It is an incredible discovery, which gives
real encouragement to global conservation efforts
to save this Critically Endangered species’. In the
last three weeks of December, the team counted
a total of 208 birds. These findings offer a
significant boost to conservationists working to
save this rare bird from extinction in Kazakhstan,
Russia and the Middle East, and the team
is very optimistic that suitable conservation
action can be taken at this wintering ground.
Some major threats have been identified already:
habitat degradation due to overgrazing, mostly
near human settlements; highly reduced animal
grazing, especially in remote and less populated
areas, due to continuous drought, because animal
manure supports increased insect abundance; and
human disturbance. During the
evenings, lapwings were observed
being chased by domestic dogs
and cats, because some birds
come close to villages at this time.
The team is expecting that other
threats will also be identified in
the future, such as food scarcity
and chemical pollution.
Cape Parrots in South Africa
Dr Steve Boyes from the Percy
Fitzpatrick Institute in South
Africa was awarded UK£820 for a
study of the incidence of psittacine
beak and feather disease (PBFD)
virus in the largest remaining
wild population of the globally
threatened Cape Parrot Poicephalus
robustus. Generous sponsorship
by Julian Francis enabled this
award. This parrot’s population is estimated as
1,000-15,000 birds and is threatened by habitat
loss, illegal capture for the pet trade and avian
diseases. The study’s primary objective is to
capture as many parrots as possible to discover
the incidence of PBFD and other diseases, to
estimate body condition, to profile the population
structure and to take blood for DNA-archiving
(to be used in the forensic investigation into
illegal trade). Steve will also undertake feeding
trials with wild Cape Parrots in field aviaries
to better understand their feeding ecology and
preference lor pecan nuts over indigenous food
resources in Afro-montane forest patches. Dr
Boyes has studied Meyer’s Parrot P. meyeri in
the Okavango Delta and has been experimenting
with using nest boxes there, to determine if
they can be an effective conservation tool for
cavity-nesting bird communities in subtropical
Africa. Fie aims to use data from this study
to derive nest box prescriptions for use by
Cape Parrots. This was the subject of a second
application, but unfortunately ABC was unable
to fund this. However, ABC Council member
Stephen Cameron very kindly helped sponsor
this project. Steve recently wrote ‘We had
Green Wood-hoopoes Phoeniculus purpureus,
Woodland Kingfishers Halcyon senegalensis and
Cape Parrot / Perroquet du Cap Poicephalus robustus (R. S. Boyes)
ABC Conservation Fund
Bull ABC Vol 17 No 1 (2010) -7
African Bird Club Conservation Fund
African Grey Hornbills Tockus nasutus nesting
with signs of several successful attempts (i.e.
good layer of excrement) in c.30% of the nest
boxes, as well as several mammal species. We also
mapped all the habitat types, located over 500
excavated nest cavities and did five cavity-nesting
bird abundance transects in each habitat type.’
Study of birds at Lake Nasser in winter
2009/2010
In Bull. ABC 16: 137, I reported on an award
towards a raptor training workshop organised
by Haitham Ibrahim et al. in Egypt. Due to
communication problems, the UK£850 awarded
by ABC was not taken up, but the workshop
went ahead successfully. Haitham submitted
a new application, which has been approved
by Council and he has now received the same
amount from ABC for a survey, very kindly
sponsored by Tasso Leventis. The project aims
to survey birds at Lake Nasser, comparing
sites on the eastern and western shores of the
lake and in Wadi Allaqi Biosphere Reserve,
and also to build the capacity of young people
working for the Nature Conservation Sector
of the Egyptian Environmental Affairs Agency
(NCS/EEAA) and students at the University
of South Valley. It also aims to raise awareness
among local communities (fishermen, farmers
and Bedouins) in the area. The Nile Valley and
the Red Sea coast are important bird migration
routes through Africa. Lake Nasser, which was
created in 1964, is 496 km long with a mean
width of 15 km. Water levels fluctuate greatly,
between seasons and years, depending on the net
annual volume of water it receives. Lake Nasser
is one of the world’s largest man-made lakes with
a very complex nature shoreline composed of
numerous khors (inundated desert wadis). The
shallow waters of these khors support aquatic
flora and provide good breeding grounds for
fish, whilst their often gently sloping shores
permit vegetation to grow. In contrast, much of
the rest of the lake’s shores are steep and rocky
with little vegetation. Many islands (the tops
of inundated hills) are widespread in the lake.
Fishing and related activities are considered
one of the main threats to birds at Lake Nasser,
whilst farmers use pesticides on their crops,
which kill birds and other wildlife. The Egyptian
government is planning to resettle more of the
surrounding land by the year 2017. Haitham
considers that swift action is needed to collect
data and raise the awareness of decision-makers
and stakeholders about the area’s birds.
A database to monitor common birds and
record rare sightings and range extensions
in Kenya
After discussions with Ian Fisher who is
overseeing Kenya Birdfinder-Worldbirds,
the Conservation Committee approved this
application, subject to suggestions made by Ian
being taken up. An award of UK£1,000 will be
made, kindly sponsored by Tasso Leventis. The
Bird Committee of NatureKenya is very keen to
pursue this work. Oliver Nasirwa wrote that ‘we
are hopeful that with the renewed interest and
support from the National Museums of Kenya,
the work of collating and managing bird records
will get back on track. With this work running
we hope that we shall find ways of addressing
capacity issues that have led to the record
keeping falling behind.’
Further work on Djibouti Francolin in the
Mabla Mountains, Djibouti
ABC has agreed to award UK£ 1,000 towards
field work costs for a follow-up survey to the
March 2009 work on the highly threatened
Djibouti Francolin Francolinus ocbropectus in
the eastern Mabla Mountains, an Important
Bird Area in Djibouti, from which a provisional
population estimate of 108 birds was derived (cf
Bull. ABC 16: 138). This was the first systematic
survey of the species at this site. Unfortunately,
access to the western and northern sides of
the mountains was impractical due to security
concerns at the time. Analysis of Google Earth
images and conversations with a local shepherd
suggest that there is potential habitat elsewhere
in the mountains and that francolins are present.
The team for the March 2010 survey, Houssein
Rayaleh and Aden Dini, will visit the west and
north sides of the mountains to determine if
francolins are present and perform transects to
prepare a more accurate population estimate for
this endangered endemic. As with the March
8 -Bull ABC Vol 17 No 1 (2010)
ABC Conservation Fund
^ African Bird Club
Male Djibouti Francolin / Francolin somali Francolinus
ochropectus (Geoff & Hilary Welch)
2009 survey, the standard survey methodology
developed by the World Pheasant Association
in the species’ main stronghold of the Foret du
Day will be used, and information on habitat
structure and current or potential threats to the
species will also be collected. Houssein Rayaleh
is Executive Secretary of Djibouti Nature, the
principal nature conservation NGO in Djibouti,
and the country’s most experienced native
ornithologist; he was a key member of the March
2009 survey.
Reports
Plight of vultures in Somaliland
Abdi Jama recently sent a report on the second
part of his survey, east of 45°E to the environs
of Erigavo, the capital of the massive Sanaag
region. Abdi’s first stop was the old Burao city
dump where, c. 18 months previously, Egyptian
Neophron percnopterus, Lappet-faced Torgos
tracheliotus , Ruppell’s Gyps rueppellii and White-
backed Vultures G. africanus had been present.
Fie reports; This time Egyptian and Lappet-
Conservation Fund
faced Vultures were present in good numbers, but
Ruppell’s was absent and just one White-backed
Vulture was seen. As we headed east, almost
every hamlet we passed had its own contingent
Egyptian Vultures, but visits to interior bush
communities revealed that the semi-commensal
existence of Egyptian Vultures petered out as
we entered poorer areas with apparently little to
scavenge on. Not a single Egyptian Vulture was
seen away from established villages and towns.
We did not see any other vultures (other than
the ubiquitous Egyptian) between Burao and
Yuffle, a distance of c.400 km, other than a
single contingent of 12 Lappet-faced Vultures,
attesting to the drastic decline of vultures.
Furthermore, the large dump just outside
Erigavo had been cleared for development since
the team’s last visit and the vultures were gone
completely. Possible causes for the absence of
vultures could include the general environment
being cleaner and, perhaps, the decline in the
once-abundant livestock herds and antelope.
The string of drought years since the 1990s has
possibly also reduced the food source for vulture
species.’
ABC is particularly grateful to the individual
sponsors who have personally pledged support
for particular projects. This is a really valuable
way to help the Club to achieve one of its
main aims — to assist individuals and small
groups undertake research that advances our
knowledge of African birds. Several members
have indicated that they are interested in helping
the Club in this work, and without any
obligation they are sent details of projects that the
Conservation Committee feel merit support. If
you would be interested in finding out how you
can support projects such as these, please contact
ABC Chairman, Keith Betton (chairman@
africanbirdclub).
Steph Tyler, on behalf of the
Conservation Committee
ABC Conservation Fund
Bull ABC Vol 17 No 1 (2010)- 9
Africa Round-up
General
Translating biodiversity
monitoring into action
In late 2009, BirdLife Partners
from eight countries attended a
workshop in Entebbe, Uganda, to
discuss how to turn monitoring
results from Africa’s Protected Area /
Important Bird Area (IBA) network
into policies and actions that ensure
their sustainable use and improve
the livelihoods of local communities.
The workshop was organised to share
ideas and learn lessons from across
the BirdLife Africa Partnership.
At present, 163 African I BAs are
also Protected Areas. These sites
are monitored to establish the state
of their bird populations, identify
the pressures that they face and to
outline responses which counter these
pressures. Humans are responsible
for many threats to IBAs but climate
change, with impacts already visible,
may be the most serious threat of
all. “African countries are most
vulnerable to its [climate change]
devastating impacts and least able to
adapt”, said Jessica Eriyo (Minister
of Environment ol the Republic of
Uganda) who opened the workshop.
“Climate change is affecting wildlife
in the same manner it is affecting the
people”, Ms Eriyo added. In keeping
with the theme of the workshop,
the Minister encouraged delegates to
engage in advocacy with a meaning
in order to address challenges
facing both the people and the
environment. Participants committed
themselves to: influence governments
to designate IBAs as legally Protected
Areas and allocate adequate resources
for enforcement of the conservation
policies; influence landowners to
adopt wise-use principles in water
catchments and basins; lobby for
inclusion of bird species as indicators
for biodiversity within National
Biodiversity Strategy Action Plans;
and, ensure full enforcement of
national Environmental Impact
Assessment regulations, among other
actions. The workshop was facilitated
by a team of experts with regional
and international experience, and
included lectures, discussions, group
exercises, case studies from Burkina
Faso, Kenya, Nigeria, Uganda and
Tunisia, and a field visit to the
Lutembe Bay IBA. The workshop
was organised and sponsored by the
BirdLife Africa I BA/PA Monitoring
Project funded by the European
Commission through the Royal
Society for the Protection of Birds
(RSPB, BirdLife in the UK) and was
hosted by Nature Uganda.
Source: BirdLife International
press release, October 2009
Wildlife poisoning in Africa
A widely available poison is being
used to kill thousands of birds every
month in an area of Kenya, and by
game poachers in Botswana to kill
vultures. The poisoning of wildlife
seems to have increased across the
continent recently, and BirdLife is
calling for increased concerted efforts
to address this threat. Situated in
western Kenya near Lake Victoria
and the Ugandan border, the
White-backed Vultures /
Vautours africains Gyps africanus
(Daniel Cornelis)
Bunyala Rice Scheme is a heavily
irrigated area, and the water-logging
also creates suitable feeding habitat
for many birds, which are being
targeted by local people who view the
meat as a delicacy. The poison used
is called Carbofuran (or Furadan)
and is designed to control insects in a
wide variety of field crops. However,
it is also toxic to animals, and has
one of the highest acute toxicities
to humans of any insecticide widely
used on field crops. In Bunyala the
poison is placed inside snail shells.
Decoy birds are also used, and
poachers disturb the surroundings to
encourage wild birds to settle into the
baited areas. Once captured, target
birds are killed and sold for human
consumption.
Throughout eastern and southern
Africa there are increasing reports
of the use of Carbofuran to illegally
poison wildlife. In Botswana,
poachers have recently been observed
lacing giraffe carcasses with poison
to attract vultures and kill them.
In two recent incidents, over 80
vultures including White-backed
Gyps africanus and Hooded Vultures
Necrosyrtes monacbus have been
deliberately poisoned in the country.
The BirdLife Africa Partnership
and many other conservation
organisations across Africa — -like
Wildlife Direct— are already working
to address this problem and are
calling for increased efforts to deal
with it. In Kenya, Martin Odino
from the National Museums of
Kenya — with funding from the
African Bird Club and Rufford
Small Grants — is working with
NatureKenya (the BirdLife Partner)
to quantify the threat, focusing
specifically on the Bunyala Rice
Scheme. BirdLife Botswana is also
working to educate local people
about the use of poisons. In response
to problems caused by wildlife
poisoning across the continent,
10 -Bull ABC Vol 17 No 1 (2010)
Africa Round-up
the BirdL.ile Africa Secretariat has
also been focusing on chemicals
and drugs as one of the threats
to birds and their habitats. Over
2,000 posters are being distributed
to raise awareness of the threat to
vultures and coordinated counts
will be undertaken in East Africa
to verify the extent of the problem
and make recommendations for
mitigation. A high-resolution PDF
of the poster is available at www.
birdlife.org/regional/africa/pdfs/
vulture_poster_highres.pdf. It may be
possible to send copies to institutions
/ individuals who need several-
high quality copies; e-mail: paul.
ndanganga@birdlife.or.ke
Source: BirdLife International
press release, November 2009
BirdLife Africa Wildlife Clubs
Project
The BirdLife Africa Wildlife Clubs
Project has taken a step closer to
its goal of connecting over 400,000
children across the continent with
conservationists around the world.
The project combines biodiversity
conservation with education and
sustainable development initiatives,
and uses bird conservation to help
bridge the digital divide in Africa.
Along with the people responsible for
the project, representatives from 1 3
other environmental organisations
and educational institutions
participated in a workshop in Accra,
Ghana.
The workshop’s host, the Ghana
Wildlife Society (GWS; BirdLife in
Ghana), has unrivalled experience in
organising environmental education
and conservation activity among
young people. The junior wing
of GWS, the Wildlife Clubs of
Ghana, recently celebrated its 21st
birthday. Starting with just two
clubs in 1987, it now has over 1,000
clubs throughout the country. The
participants developed a wildlife
club / environmental education
coordinators’ network, reviewed
the contents of a draft manual
for wildlife clubs in Africa, and
discussed ways of persuading national
governments to incorporate the
manual into their education systems.
As part ol the project, BirdLife
Zimbabwe recently organised a
High Schools Public Speaking
Competition in partnership with the
Environmental Management Agency
(EMA) and the Mukuvisi Woodlands
Association. Schoolchildren from
around Harare were given questions
posed by BirdLife Zimbabwe and
EMA. Mukuvisi Woodlands sourced
varied prizes and BirdLife Zimbabwe
donated Enjoy the Birds of Zimbabwe
books to the children. Additional
prizes were donated by the British
Council, WWF, EMA and the
IUCN.
Source: BirdLife International
press release, September 2009
Cory’s Shearwater / Puffin cendre
Calonectris diomedea (Augusto Faustino)
Spatial segregation between
two closely related shearwaters
breeding in sympatry
Joan Navarro and co-workers used
satellite-tracking and stable isotope
data to study spatial segregation
of Cory’s Shearwaters Calonectris
diomedea borealis and Scopoli’s
Shearwaters C. d. diomedea breeding
in sympatry at a Mediterranean
colony. It was found that Cory’s
foraged mainly in the Atlantic,
whilst Scopoli’s fed exclusively in
proximity to the breeding colony in
the Mediterranean. This segregation
could reflect the foraging behaviour
of Cory’s Shearwaters before they
arrived in the Mediterranean from
the nearby Atlantic colonies: they
probably have remained faithful
to their previous foraging area in
the Atlantic. Alternatively, Cory’s
Shearwaters are larger and have
a greater wing loading compared
with Scopoli’s, and therefore are
probably better prepared to fly across
the strong winds in the Strait of
Gibraltar. The wintering areas of
both taxa were also different: Cory’s
Shearwaters wintered along the coast
of southern Africa, whereas Scopoli’s
wintered mainly in the Canary
Islands Current.
Source: Biol. Lett. 5, pp. 545-548
Understanding the Amur Falcon’s
migrations
Amur Falcon Falco amurensis
conducts one of the most remarkable
of avian migrations: the birds leave
their Asian breeding range and travel
to north-east India and Bangladesh,
where they fatten up for the overland
flight over peninsular India. It is
believed to then undertake the
longest regular over-water passage
of any raptor, crossing the Indian
Ocean between south-west India
and tropical East Africa, a journey
of >4,000 km, which also includes
nocturnal flight. Birds arrive in their
southern African winter range in
November-December and depart
by early May. In contrast, its return
is probably largely overland, to the
north and west of its southbound
route. However, recent observations
in late November— early December
in Ethiopia suggest that there may
be a regular overland passage at
higher latitudes than previously
known. Now, BirdLife South
Africa, Microwave Telemetry,
Inc., USA, and members of the
World Working Group on Birds
of Prey have commenced a satellite
telemetry programme to study the
migration routes and other aspects
of the biology of this little-known
raptor. At the largest winter roost
known in South Africa (numbering
r.26,000 birds) almost 30 birds
were trapped in early 2010, and the
biggest ten adults were fitted with
5g solar-powered satellite tags. Even
Amur Falcon / Faucon de 1’Amour
Falco amurensis (Phil Palmer,
www.Birdholidays.co.uk)
Afiica Round-up
Bull ABC Vol 17 No 1 (2010) -11
after just a few days surprising new
information was gathered, with one
female roosting >100 km from the
trap site.
Source: Bernd Meyburg in litt. to
AfricanBirding January 2010
More Eleonora’s Falcons GPS-
tagged
Following a German’s team study
using GPS-tagged Eleonora’s Falcons
Falco eleonorae (see Bull. ABC 16:
14), four Eleonora’s Falcons were
fitted with satellite transmitters in
Greece in spring 2009, to investigate
the migration routes followed by
the birds to their wintering areas in
south-east Africa and Madagascar.
The four started their journey to
Africa in mid October. By late
October, two were in Sudan, one in
western Ethiopia and one in central
Egypt. In early November, two had
reached Madagascar, whilst the other
two remained in central Africa, in
Chad and Central African Republic,
respectively. For maps showing the
migratory routes of the four birds, see
the website below.
Source: www. ornithologiki.gr/life/
falcoellenlprogramlsatellite_map.htm
North Africa
Local group makes its mark at
Egypt’s Lake Qarun
Egypt’s first Important Bird Area
(IBA) Site Support Group (SSG)
(see Bull. ABC 16: 144) has
persuaded one of the country’s largest
construction groups to end the
dumping of waste at Lake Qarun,
which supports regionally important
numbers of wintering waterbirds.
Lake Qarun occupies the deepest
part of the Fayoum Depression,
>40 m below sea level. Once a
large body of fresh water, the lake
now receives almost all its water as
drainage from irrigated land. As a
result, and because the only outflow
is via evaporation, levels of salinity
have been steadily increasing. Because
of these environmental changes, a
local subspecies of Sardinian Warbler
Sylvia melanocephala norrisae has
become extinct, while Slender-billed
Gull Larus genei, which first breed
Slender-billed Gull / Goeland railleur
Larus genei (Georges Olioso)
in the 1990s, now numbers c.8,500
pairs. Numbers of breeding Spur-
winged Lapwing Vanellus spinosus
also meet IBA criteria, as does the
wintering population of Black-
necked Grebe Podiceps nigricollis. A
salt extraction processing plant has
been set up, which over time will
improve water quality and permit
habitats to be restored, as well as
providing employment. However,
unregulated tourist development in
the south of the lake is destroying the
best waterbird habitats and leading
to increased disturbance. Hunters,
including organised parties from
Europe, regularly ignore the lake’s
protected status.
The SSG was established to
enhance biodiversity conservation
and benefit-sharing with local
communities, in recognition that
local people could make a significant
contribution towards conservation
efforts by reducing exploitation and
hunting in the protected area. Its
members have removed shooting
blinds used by duck hunters, and
plan to erect signboards with
information about the lake and its
importance as an IBA. They are
also involved in awareness-raising
and education activities with
schoolchildren. The local government
has an ecotourism strategy for Lake
Qarun, so when the construction
company began work on a tourist
development, the SSG went into
action, and the bulldozers were
quickly pulled back to 30 nr from
the shoreline. The construction
company’s owner has pledged to set
aside a proportion of his shoreline
for saltmarshes to be re-established,
providing a small bird sanctuary on
the lake. This was to have been a
hunting lodge in his original plan,
and he has made a commitment not
to allow or sanction hunting parties
along the lake.
Source: BirdLife International
press release, September 2009;
World Birdwatch 31(4), p. 7
Range extension of Plain Martin
in north-western Morocco
In November 2007-February 2008,
Plain Martins Riparia paludicola were
found breeding in an abandoned
sand extraction site at Lower
Loukkos, north-western Morocco.
This is the north-westernmost
breeding record of this species
in the country and constitutes a
range extension of c. 1 00 km from
Khenichet, the nearest previously
known breeding site. Morocco’s
isolated population of the endemic
subspecies R. p. mauritanica, has
steadily expanded its range north
since the 1960s.
Source: Dutch Birding 31, pp. 304—
306
Mute Swan in Algeria
In February 2009, three Mute Swans
Cygnus olor were photographed
at Lake Tonga, a Ramsar site in
north-east Algeria. There are veiy
few previous records of any Cygnus
species in the country, the most
recent in the late 1990s.
Source: Alauda 77, p. 314
A Humblot’s Heron in Tunisia
Endemic to the Malagasy region,
the rare Humblot’s Heron Ardea
humbloti, which was photographed
at Oued Gouifla in October 2008,
seems a highly unlikely vagrant.
However, to date, the observers have
been unable to locate any captive
individuals in, for instance, Europe
that might otherwise account for the
record.
Source: Alauda 77 , p. 313
A migration bottleneck in Egypt
Gudrun Hilgerloh of the Johannes
Gutenberg University in Mainz
has provided some counts from a
migration bottleneck on Egypt’s
Red Sea coast, at Zait Bay, in the
coastal desert west of the main
Suez-Hurghada road. Counts in late
12 -Bull ABC Vol 17 No 1 (2010)
Africa Round-up
February-early May 2007 produced
almost 125,000 storks and nearly
40,000 raptors, with nearly 180,000
soaring birds counted in all.
Source: Bird Conserv. Intern. 19,
pp. 338-352
Atlantic Ocean Islands
Aberrantly dark Fea’s Petrel found
in the Cape Verde Islands
In March 2007, an odd Fea’s
P etrel Pterodroma feae was trapped
and photographed on Fogo, Cape
Verde Islands. Unlike normal birds,
which are clean white below, the
entire underparts of this individual
were ashy grey and the underwing-
coverts lacked any white. The head
was also darker than in normal
birds. Melanism is considered to
be a very rare phenomenon in
Procellariiformes, with only five
known cases up to 2005, none of
which referred to Fea’s Petrel or
the closely related Zino’s Petrel P.
madeira.
Source: Dutch Birding 31, pp. 302-
304
The former range of the Razo Lark
The Critically Endangered Razo Lark
Alauda razae, which is nowadays
restricted to the tiny island of Raso,
in the Cape Verde archipelago, and
is thought to number in the region
of just 100 individuals, was formerly
present on the other north-western
islands of Santo Antao, Sao Vicente
and Santa Luzia. This is the finding
of a group of Spanish researchers,
based on a survey of subfossil bone
deposits from all of the ten major
islands of the Cape Verdes. All of
the deposits date from before the
arrival of the Portuguese in the
15th century. This finding confirms
previous speculation that the species’
modern range is relictual and that
the Razo Lark was formerly more
widespread.
Source: Alauda 77, pp. 309—312
Last words on the kites of the
Cape Verdes?
'Sabine Hille (University of Wien)
and Nigel Collar (BirdLife) have
taken a detailed look at the Milvus
kites in the Cape Verde Islands.
Sadly, it seems that the Red Kite M.
milvus fasciicauda which occurred
on the north-west and south-west
islands ol the group is almost or
actually extinct; and numbers of
Black Kite M. migrans , which occurs
on the eastern islands and differs
morphometrically from mainland
birds, are critically low. There has
been much confusion between these
forms. Many earlier visitors did not
realise that two forms occur in the
archipelago, and it may now already
be too late to save either bird.
Source: Bull. Br. Ornithol. Club 129,
pp. 217-221
More on Cape Verde Warbler
A recent survey of the island of
Fogo, in the Cape Verde Islands,
found that Cape Verde Warbler
Acrocephalus brevipennis is widespread
across the northern half of the island
between 200 m and 975 m, with an
estimated total population of 500
pairs there. On Fogo, the species
favours coffee plantations and other
introduced crops, including maize.
The authors of the study, Jens
Hering and Elmar Fuchs, also looked
at the species’ breeding biology, and
found that both sexes are responsible
for incubating the eggs.
Source: Vogelwarte 47, pp. 157-164
Red-billed Tropicbird breeding in
the Canary Islands
In November 2007, a pair of Red-
billed Tropicbirds Phaethon aethereus
was found breeding in the Canary
Islands for the first time, on the
westernmost island of El Hierro. One
young successfully fledged. The next
Red-billed Tropicbird / Phaeton
a bee rouge Phaethon aethereus
(Augusto Faustino)
year, a pair again bred successfully on
the island. The nearest breeding sites
of this species are in the Cape Verde
Islands and on lies de la Madeleine,
off Dakar, Senegal, 1,300 and 1,400
km distant, respectively.
Source: Quercus 281, p. 44
(July 2009)
West & Central Africa
Black-tailed Godwit / Barge a
queue noire Limosa limosa
(John Caddick)
Black-tailed Godwit’s migration
followed by satellite
A Black-tailed Godwit Limosa limosa
fitted with a satellite transmitter flew
non-stop within 48 hours from the
Netherlands to Senegal via Spain
and over the Sahara, a distance of
over 4,000 km. Its average speed
was nearly 80 km per hour. In May
2009, Theunis Piersma’s research
group fitted 15 Black-tailed Godwits
in Friesland, Netherlands, with tiny
transmitters that were placed into the
abdominal cavity of the birds. The
researchers are intent on discovering
exactly how the birds migrate
between their winter and summer
grounds and, for example, whether
they migrate in a ‘loop’. Indeed,
it looks as if at least some godwits
that arrive in West Africa via Spain
and Morocco, use a more easterly
route, via Mali and Italy, to return to
their breeding grounds in Friesland.
The project has revealed that the
godwits have a flexible strategy, both
during their migration and on their
wintering grounds. The satellite-
wearing godwits started to leave
in late June and all had departed
Friesland by early August. One bird
initially also flew to Senegal, but
continued to Guinea-Bissau and,
Africa Round-up
Bull ABC Vol 17 No 1 (2010) -13
foilwing a three-month stay, flew
1,200 km east to the Niger Delta in
Mali, where it was killed in a fishing
net in November. The migration
routes of the birds can be seen at
www.vogelbescherming.nl/grutto
Source: http://www. rug. nil
biologie/ 1 02_09
A scops owl on Principe?
The Gulf of Guinea islands of Sao
Tome and Principe are well known
for their spectacular avian endemism,
but no owl species is definitely
known from the latter island, despite
the presence of an endemic scops
owl, Otus hartlaubi, on Sao Tome.
Martim Melo and Martin Dallimer
have recently published details of
their recordings of owl-like calls
in low- altitude primary forest on
Principe during surveys in 2007. The
calls are within the frequency range
of Otus owls and differ from known,
non-avian calls, suggesting that an
endemic scops owl is present on
the island, as had been speculatively
reported since as long ago as 1928.
Source: Malimbus 31, pp. 109-115
Partnerships strengthen
migratory bird conservation in
West Africa
Six countries in West Africa have
committed to conserving Important
Bird Areas (IBAs) for migrant birds
along their coastlines, following a
recent joint workshop organised by
BirdLife and Wetlands International.
“The project offers an opportunity
for coordinated monitoring and
conservation of IBAs along the coast
of West Africa, and for capacity
building, which is crucial for
migratory bird conservation, as well
as enhancement of the livelihoods of
local communities”, said Dr Hazell
Thompson, Africa regional director
of BirdLife International.
Over 40% of long-distance
migrants in the African-Eurasian
flyway have shown signs of decline
during the last three decades. Of
these 10% are classified by BirdLife
as globally threatened or Near
Threatened on the IUCN Red List.
Along the coast of West Africa —
from Guinea to Mauritania — over
170 migrants have been recorded
Marbled Teal / Marmaronette
marbree Marmaronetta angustirostris
(Georges Olioso)
Aquatic Warbler / Phragmite aquatique
Acrocephalus paludicola (Bruno Portier)
including the Vulnerable Marbled
Teal Marmaronetta angustirostris
and Aquatic Warbler Acrocephalus
paludicola, and the Near Threatened
Ferruginous Duck Aythya nyroca.
However, of the 43 IBAs in the
region that qualify for their migratory
birds, 22 lack any conservation
action. Key threats identified
include agricultural intensification,
pollution, commercial and residential
development, unsustainable
harvesting and hunting, modification
of habitats such as wetlands, invasive
species and human disturbance.
Some of the critical IBAs for
migratory birds in the region include
Banc d’Arguin National Park and
Chott Boul (Mauritania), Delta
du Saloum and Djoudj Wetlands
(Senegal), Arquipelago dos Bijagos
(Guinea Bissau), Sierra Leone River
Estuary, and lies Tristao (Guinea).
Participants from Guinea Bissau,
Guinea, Mauritania, Senegal,
Sierra Leone and Gambia met at
the four-day workshop in Dakar,
Senegal. They represented civil
society organisations, government
institutions and conservation
programmes and initiatives in the
region. Together, they identified
and agreed on a network of sites
and species, as well as a menu of
conservation actions that will be
undertaken over the four-year life
span of the project.
Source: BirdLife International
press release, December 2009
White-necked Picathartes survey
in Gola Forest, Sierra Leone
A survey conducted in October
2006-January 2007 within Gola
Forest Reserve and in surrounding
community forest found 47 White-
necked Picathartes Picathartes
gymnocephalus breeding sites, of
which 35 were active. A total of 109
active nests were counted, 64 of
them located within the reserve. It
is possible that the actual number is
slightly higher, as some undiscovered
nest colonies could exist at remote
locations in the reserve.
Source: Ibis 1 52, p. 205
Grey-necked Picathartes survey
in Cameroon
Taku Awa et al. from Reading
University, in the UK, surveyed
Grey-necked Picathartes Picathartes
oreas in various parts of the
Cameroon mountains, in particular
Mbam Minkom Mountain Forest.
During a complete survey in
January-March 2006 they found
90 breeding and 24 potential
breeding sites, but the whole area
is under considerable pressure from
agricultural encroachment and illegal
timber use. The authors suggest
various possible remedial actions
and that the situation needs to be
monitored.
Source: Bird Conserv. Intern. 19,
pp. 254-264
Good news for Ibadan Malimbe
The globally Endangered Ibadan
Malimbe Malimbus ibadanensis,
whose population is considered to
number fewer than 2,500 individuals
confined to a tiny area circumscribed
by Ibadan, Ife, Iperu and Ilaro, in
south-west Nigeria, has recently been
discovered in the Ifon Forest Reserve,
14 -Bull ABC Vol 17 No 1 (2010)
Africa Round-up
a newly created protected area of
282 knv, which now qualifies as an
Important Bird Area. The finding
extends the species’ range c. 140
km to the east, and observations
made in the reserve suggest some
degree of dependence on Kola Cola
gigantea trees, a previously unknown
association.
Source: Malimbus 31, pp. 121-122
Plantations are not only bad news
for birds
Lars Holbech of the University of
Ghana has been looking at tree
crop plantations and their use by,
mainly lower storey, forest birds.
Such plantations have included rustic
cocoa, neglected coconut and various
plantations of exotic tree species. He
found that those areas adjacent to or
within large forest areas are superior
to smaller areas near small species-
poor forests, and a high forest tree
density and a luxuriant undergrowth
that is uncut for several years are the
most important actors permitting
forest specialists to survive. Fifty
percent of species of conservation
importance were found in such
plantations, thus revealing that they
are an important reservoir for such
species. The considerable majority
of the plantations lack formal
protection.
Source: Bird Conserv. Intern. 19,
pp. 287-308
Sao Tome Short-tail is more
widespread than thought
A team from the Sao Tome
Association of Biology has found
three, perhaps four, family groups
of the Sao Tome Short-tail
Amaurocichla bocagii in the montane
forests of the island. Previously
the species was thought only to
occur in the lowlands, but clearly it
breeds higher up too. Similarly, one
individual of Newton’s Fiscal Lanius
newtoni was also found. Perhaps the
conservation of both these species is
not quite as critical as was thought?
Source: Bull. Br. Ornithol. Club 129,
pp. 213-216
East Africa
East African Rarities Committee
changes its remit
The East African Rarities Committee
has just changed its remit and
will now consider the first to fifth
records of any species from each of
Kenya, Tanzania and Uganda. It is
hoped that this will make it easier
for observers to establish whether
their sightings need to be submitted
to the committee or not. If you see
a species that has been recorded
fewer than five times in any of the
three countries please submit details
to the EARC Secretary, Jeremy
Lindsell, RSPB, The Lodge, Sandy,
Bedfordshire SG19 2DL, UK,
e-mail: jeremy.lindsell@rspb.org.uk.
Past records of such rarities are also
sought.
Source: D. J. Fisher in litt. 2009
NABU protects unique wild coffee
forests in Ethiopia
NABU (BirdLife in Germany),
in partnership with the Ethiopian
government and others, is to operate
a project to protect the last natural
forests where the world famous
'arabica’ coffee is produced. In the
last ten years, almost 43% of these
forests have disappeared, having been
transformed into arable land. “The
clearing of tropical forests is a major
source of greenhouse gases. Over
the past 40 years, 35% of Ethiopian
forests have been lost through
deforestation. If we do not act now,
Ethiopia will lose all its forests by
2020”, said NABU’s President.
Experts estimate that the remaining
forest — c.200,000 ha — contains
c.25 million tonnes of carbon
dioxide in soil biomass. It absorbs
600,000 tonnes p.a. of the harmful
greenhouse gas from the atmosphere.
The NABU project will provide
the restoration of 700 ha of natural
forest and cultivated areas with
native wildlife and timber, whilst the
reforestation of 10,000 ha will be
jointly managed with the Biosphere
Reserve following the principles of
sustainable forestry. Special tourist
infrastructures, such as animal
and birdwatching towers, outdoor
museums and hiking trails will also
be constructed. After receiving special
training, local people will be able to
guide tourists and explain the effects
of climate change and agriculture
practices.
Source: BirdLife International
press release, December 2009
Natron community vows to
protect its flamingos
Villagers around Tanzania’s Lake
Natron have vowed to protect
the lake and its Lesser Flamingos
Phoemconaias minor from industrial
development. BirdLife’s Tanzanian
Partner — the Wildlife Conservation
Society of Tanzania (WCST) — has
put forward an alternative to the
environmentally destructive soda
ash extraction plant proposed for
the lake, calling instead for its
unmatched tourism potential to
be developed, and for the people
of Lake Natron to be enabled to
benefit from the income generated.
Three-quarters of the global Lesser
Flamingo population occurs in East
Africa, with Lake Natron by far their
most important breeding site. In
2007, the Indian-based multinational
company, Lake Natron Resources
Ltd., proposed to construct a major
soda ash extraction plant to exploit
the very alkaline nature of the lake
(see Bull. ABC 15: 18).
The company appears to have
withdrawn its interest following
a successful appeal by BirdLife
and the Lake Natron Consultative
Group, a coalition of community
and environmental groups in East
Africa. But in 2009 BirdLife learned
that the Tanzanian government had
published invitations to tender for
soda extraction equipment, and plans
an extension of the rail network
to link Lake Natron to the port of
Tanga. The government subsequently
denied being responsible for the
invitations. Speaking at a meeting
organised by WCST, a Maasai elder,
Lasoi Ole Nareshoi, said: “God gave
us this resource for use by ourselves,
our children and children’s children.
We will protect it from any industrial
exploitation that may chase away
the flamingos and damage the
environment”. Paul Nnyiti, of the
Africa Round-up
Bull ABC Vol 17 No 1 (2010) -15
WCST, said the time had come for
stakeholders and the government to
come to the assistance of the Lake
Natron community so that they can
benefit from tourism, whilst Ken
Mwathe, who is the Coordinator of
the Lake Natron Consultative Group,
said that although the soda ash
mining plans have been put on hold,
stakeholders remain worried that the
plans have not been abandoned.
Source: BirdLife International
press release, October 2009;
World Birdwatch 31(4), p. 7
House Crows eradicated from
Socotra
House Crows Corpus splendens,
which are native to the Indian
subcontinent and are recognised as
an invasive species in many parts
of the world, were eradicated from
Socotra, Yemen, in 2009. The first
individuals arrived in 1996 and
the population built up slowly to
ten pairs, raising concerns about
the damage the species could do to
native biodiversity. Over the last 1 50
years the species has been spreading,
aided largely by ships, which have
enabled them to colonise many
parts of the Arabian Peninsula. In
mainland Yemen, they had reached a
high density by the 1980s, posing a
threat to agriculture. Half a million
were exterminated, but complete
eradication proved impossible.
Source: Sandgrouse 31, p. 204 &
www. birdwatch. co. uk! website I content!
viewl2673l32l
Indian Ocean Islands
Madagascar NGOs unite against
plunder of natural resources
Asity Madagascar (BirdLife in
Madagascar) has joined a group of
Malagasy civil society organisations,
Voahary Gasy, in calling for an end
to the plundering of natural resources
in the national parks of north-east
Madagascar. Following the change
of government in March 2009, all
but essential humanitarian aid has
been withdrawn by the international
community, leaving Madagascar s
national park and forestry services
practically unfunded. Loggers
have moved into protected areas,
removing valuable hardwoods such
as rosewood, ebony and mahogany.
They work for influential business
people in possession of illegal but
‘official’ documentation permitting
them to export these hardwoods.
Local communities who depend on
forest resources and tourism have
been threatened and attacked for
their opposition to these highly
destructive activities. A new trade
in bushmeat has developed and
lemurs in particular are being killed
in large numbers. Several endemic
birds are largely or entirely confined
to pristine primary forest in this
region, including the Endangered
Madagascar Serpent Eagle Eutriorchis
astur and Vulnerable Helmet Vanga
Euryceros prevostii and Bernier s
Vanga Oriolia bernieri. With the
complete breakdown of protected
area regulation, and armed gangs
operating with impunity in the
forests, it is impossible to assess the
impact on these and other threatened
species.
Voahary Gasy is calling for
an immediate halt to exports of
hardwoods, particularly rosewood,
the enforcement of protected area
regulation, the creation of a task
force to combat environmental
crime, and a campaign to raise
awareness within Madagascar ol the
nature and extent of the destruction
of the island’s remaining forests.
The umbrella organisation is also
emphasising that the range of new
and extreme threats to Madagascar s
environment and biodiversity is very
broad and not restricted to the north-
east of the country or to precious
hardwoods. Other parts of the
country, and valuable resources such
as reptiles, shark fins and rare plants,
are also affected or at least at risk.
Asity Madagascar is working with
other groups to control or prevent
problems in the far south-east, where
the largest expanse of lowland forest,
Tsitongambarika, is under threat,
and similar initiatives are taking place
elsewhere. ‘These events are a disaster
for Madagascar, profiting a tiny
number of individuals at immense
cost to the country’s economy and
extraordinary heritage", said Dr
Roger Safford, Senior Programme
Manager at BirdLife International.
“The global community must
help to resolve the situation, but
the emergence of Voahary Gasy is
a very positive step, showing the
commitment of Malagasy institutions
and individuals to lead in publicising
and tackling the problems.
Source: World Birdwatch 31(4), p. 10
Southern Africa
Pygmy Falcon / Fauconnet
d’Afrique Polihierax semitorquatus
(Dave Richards)
Polyandrous Pygmy Falcons
During a photographic trip to
the Kalahari Desert, in August
2009, photographer Albie Venter
documented two different
male Pygmy Falcons Polihierax
semitorquatus copulating with the
same female, which had a nest
nearby. An instance of cooperative
breeding, wherein rwo male Pygmy
Falcons had provisioned a single
female, had been documented
recently but such behaviour was
unexplained, until now. It seems
that, at least occasionally, the more
strikingly coloured female Pygmy
Falcon may avail herself of more than
one mate.
Source: Africa — Birds & Birding
14(6), pp. 16-18
Avian biodiversity in South Africa
and the BirdLife South Africa List
Committee
There has recently been a major
focus on the Southern African
bird list, which includes the seven
countries south of the Zambezi River.
Remarkably, South Africa itself has
never received much attention, and
few birders even know how many
species this remarkably diverse
16 -Bull ABC Vol 17 No 1 (2010)
Africa Round-up
country holds. BirdLife South Africa
has now reconvened the BirdLife
South Africa List Committee and the
resulting official South Africa bird list
contains 90% of the species known
from the entire southern African
sub-region. The South African bird
list (which can be downloaded on
the BirdLife South Africa website:
www.birdlife.org.za) includes 84 1
species, plus another seven occurring
in South African territory, on the
subantarctic Prince Edward Islands.
The list is highly conservative,
as vagrants have been subject to
approval by BirdLife South Africa’s
Rarities Committee. Of the 841 bird
species recorded in South Africa, 20
are true endemics, 50 others are near-
endemics occurring in Swaziland and
Lesotho or very marginally spreading
into countries further north, three
are breeding endemics and one is
apparently a winter endemic (Long-
tailed Pipit Anthus longicaudatus) ,
whilst 120 are vagrants and of the
remaining 721, 80% are resident.
An exciting prospect is that all nine
provinces of South Africa may hold
new species for the South African list.
Limpopo and North West provinces
are diverse yet relatively poorly
studied, whilst the Northern Cape
has an unidentified canary that could
even be new to science. The coastal
provinces could generate new seabirds
and waders, and the Eastern Cape
has also been poorly explored. Chris
Lotz, Chairman of BirdLife South
Africa’s List Committee, urges birders
to submit sightings of species new to
the South Africa list to the BirdLife
South Africa Rarities Committee and
the List Committee; please contact
him for more information (info@
birdingecotours.co.za).
Source: Chris Lotz in litt.
January 2010
Damara Terns in Angola
While it has been strongly suspected
for some years that the globally Near
Threatened Damara Tern Sterna
balaenarum might breed in extreme
south-western Angola, specifically
in the region of the Baia dos Tigres,
irrefutable evidence for this was
lacking until January 2009. In
that month, Rob Simmons visited
Damara Tern / Sterne des baleiniers
Sterna balaenarum (Peter Ryan)
this remote area with the express
intention of surveying it for the
species. His trip was fantastically
successful; around 35 km north
ol the Cunene River mouth, Rob
found a breeding colony of Damara
Terns numbering approximately 570
individuals and 200 pairs. He found
five nests with either eggs or young.
Source: Africa — Birds & Birding
14(6), pp. 56-60
Taxonomic proposals
A new boubou species
Laniarius willardi has been described
as a new species of boubou from
the Albertine Rift by a team of
researchers, based on its grey to blue-
grey irides, external morphometries
and genetic data, which indicate
that its closest relative is Mountain
Sooty Boubou L. poensis camerunensis
from Cameroon. Crimson-breasted
Bushshrike L. atrococcineus and
Sooty Boubou L. leucorhynchus
are together the sister clade to
L. willardi / L. p. camerunensis.
Laniarius willardi (the specific
name honours David Willard,
Curator of Birds at Chicago’s Field
Museum of Natural History) and
the geographically sympatric L.
p. holomelas differ by 1 1.5% in
uncorrected sequence divergence,
whilst elevational data from
specimens suggest the possibility of
elevational segregation at c.2,000
m, with L. willardi occurring below
this. The team’s broad sampling of
black and sooty boubou taxa also
indicate that: L. poensis races do not
form a monophyletic clade; L. p.
camerunensis may represent multiple,
non-sister lineages; and that at
least one race of Fiilleborn’s Black
Boubou L. fuelleborni usambaricus
is genetically distinct from the other
races of that species.
Source: Auk online , doi:10.1525/
auk. 2009. 09014
A new ‘Winifred’s Warbler’
species
Rauri Bowie et al. have studied
genetic samples from the various
populations of Winifred’s Warbler
Scepomycter winifredae in the
mountains of central Tanzania. The
species was originally known solely
from the Uluguru Mountains, but
it has more recently been found in
the Ukaguru and Rubeho ranges,
with one record from the eastern
scarp of the Udzungwas. The latter
three populations lie >100 km from
the Uluguru population with no
contact as far as is known. They are
also morphologically distinguishable,
and their DNA is different at several
localities, suggesting that these might
be recognised specifically under the
name Rubeho Warbler Scepomycter
rubehoensis.
Source: Ibis 151, pp. 709-719
How many species of Pterodroma
occur in Macaronesia?
Jose Jesus et al. from the University
of Madeira have been examining
the taxonomy and relationships of
the gadfly petrels Pterodroma spp.
in Macaronesia using cytochrome
£-gene data and morphometries.
Results suggest that all three forms:
Zino’s Petrel P. madeira , and the
two forms of Fea’s Petrel P. f. feae
(from the Cape Verdes) and P.f.
deserta (from Bugio) constitute a
monophyletic clade most closely
related to Bermuda Petrel P. cahow
and Black-capped Petrel P. hasitata.
The authors consider that all three
Macaronesian forms warrant species
status, which in turn has conservation
implications as P. f. deserta might
qualify as Vulnerable (see also Bull.
ABC 16: 18).
Source: Bird Conserv. Intern. 19,
pp. 199-214
Dohrn’s Thrush Babbler is a Sylvia
The taxonomic position of Dohrn’s
Thrush Babbler Horizorhinus dohrni,
the sole representative of this genus
endemic to the Gulf of Guinea
Africa Round-up
Bull ABC Vol 17 No 1 (2010) -17
island of Principe, has remained
uncertain since the species was
formally described nearly 150 years
ago. It has been variously placed in
babblers (Timaliidae), flycatchers
(Muscicapidae), thrushes (Turdidae)
and warblers (Sylviidae). Molecular
analysis by Gary Voelker, Martim
Melo and Rauri Bowie resulted in
strong support for the placement of
Horizorhinus within babblers, and
as part of the (babbler) genus Sylvia.
Specifically, Horizorhinus was placed
as sister to African Hill Babbler Sylvia
(. Pseudoalcippe ) abyssinica , in a small
Sylvia subclade that also included
Blackcap S. atricapilla and Garden
Warbler S. borin. The researchers
therefore suggest that Horizorhinus
be subsumed into Sylvia , and that
Dohrn’s Thrush Babbler henceforth
be recognised as Sylvia dohrni.
Source: Ibis 151, pp. 580-583
Genetic work reveals surprising
new relative of the Fairy
Flycatcher
Endemic to southern Africa, the
Fairy Flycatcher (or Fairy Warbler)
Stenostira scita has been variously
placed close to the Monarchidae,
within the Muscicapidae, as Incertae
Sedis with other warblers, such
as the tailorbirds Orthotomus, of
uncertain relationships, or in the
so-called Stenostiridae, which also
comprises the genera Elminia , of the
Afrotropics, and the Indo-Malayan
Culicicapa (canary- flycatchers). The
Stenostiridae is just one of seven
lineages identified within the old
Fairy Flycatcher / Mignard enchanteur
Stenostira scita (Peter Ryan)
Mount Moco website
www.mountmoco.org
expanded view of the Muscicapidae
by recent molecular work. Now,
further genetic sequencing, by
Jerome Fuchs et al. suggests that
the Asian taxon, Yellow-bellied
Fantail Rhipidura hypoxantha, also
belongs within the Stenostiridae.
Because of this, the authors of the
study recommend that this fantail be
returned to the genus Chelidorhynx.
Given strong, independent and
multi-local support for the definition
of this family group, Fuchs and his
co-workers have now formally erected
the name Stenostiridae under the
rules of the International Code of
Zoological Nomenclature.
Source: Mol. Phyl. & Evol. 53,
pp. 384-393
Internet resources
Mount Moco website
A new website, www.mountmoco.
org, is devoted to ornithological work
at Mount Moco, Angola’s highest
mountain and arguably the most
important site for bird conservation
in Angola. The mountain has no
formal conservation status and the
few remaining Afromontane forest
patches, <85 ha in extent, are being
eroded by a single community of
c.300 people. The region is thought
to support half of all Afromontane
forest in Angola, making it vital for
the protection of birds dependent on
these forests, the most notable being
Swierstra’s Francolin Francolinus
sutierstrai, with an estimated 80
pairs. No other viable population is
currently known. The main aims are
to have the site officially recognised
as a conservation area and to reduce
impacts on the forest by providing
alternative sources of wood and
increasing efficiency of natural
resource use. Ultimately, it is hoped
to start a small reforestation project
and promote tourism to the site. A
Portuguese version of the website
should be available soon.
Source: Michael Mills & Martim Melo
in litt. October 2009
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18 -Bull ABC Vol 17 No 1 (2010)
Africa Round-up
Plumage variation in African Goshawk Accipiter tachiro and its
separation from congenerics in equatorial Africa
Michel Louettt f; illustrated by Nik Borrow b
Variation dans le plumage de 1 Autour tachiro Accipiter tachiro et la distinction de ses congeneres
en Afrique equatoriale. Le plumage de 1 Autour africain Accipiter tachiro presente une grande variation
geographique et individuelle. Certains plumages lies a l’age et au sexe, ainsi que d’autres caracteristiques,
sont souvent mal decrits dans la litterature. L auteur analyse les differences morphologiques caracteristiques
et indique comment distinguer 1 Autour africain d autres especes d’ Accipiter en Afrique equatoriale, avec
reference speciale a 1 Autour a flancs roux A. castanilius. Differents plumages adultes et immatures sont
illustres et compares a ceux d’especes similaires et sympatriques du genre Accipiter.
Summary. African Goshawk Accipiter tachiro displays remarkable geographical and individual variation;
some of these plumages and other characteristics are often poorly described in the literature. Here I discuss
the distinctive features and indicate how to separate African Goshawks from other Accipiter species in
equatorial Africa, with special reference to Chestnut-flanked Sparrowhawk A. castanilius. Various adult and
immature plumages are illustrated and compared with those of sympatric congenerics.
A frican Goshawk Accipiter tachiro is one of the
commonest raptors in African forests and
woodlands. However, in the field as well as in the
museum tray, the species can be easily confused
with others of the same genus. Indeed, individual
morphological variation is quite extensive, and
the species also displays remarkable geographical
variation, whilst some age- and sex-related
plumages and other characteristics are often
poorly described in the literature. Because the
species' breeding season is prolonged in equatorial
regions (yet seasonal elsewhere) and post-juvenile
moult can take almost 12 months, moulting birds
can be present virtually year-round here. These
birds in post-juvenile moult are especially tricky to
identify. Like all Accipiter species worldwide, size
dimorphism is the rule, with the female being the
larger of the sexes: in African Goshawk the wing-
chord of females is up to c. 15% longer than that
of males in Cameroon and up to c. 19% longer
in the eastern Democratic Republic of Congo
(hereafter DRC; also Congo-Kinshasa). Weight
differences are even more important: the female
usually weighs almost twice as much as the male
(Louette 2001, 2003) Although the forest forms
are monomorphic in colour, with both sexes being
colourful, Chapin (1932) already noted that in the
woodland forms ‘females have much less rufous
on flanks and tibiae [than males] and often none
at all’.
Taxonomy
The taxonomy of the genus Accipiter is not yet
entirely clear. Robust results from molecular
studies are best awaited in order to decide on
the number of species in each of the three
complexes (or ‘superspecies’) — Shikra A. badius
(and relatives), African Little Sparrowhawk A.
minullus (plus Red-thighed Sparrowhawk A.
erythropus ) and African Goshawk (which has
several recognisable forms). Stresemann (1923)
unified, purely on morphological grounds, all of
the described taxa into a single species in each
of these three cases. Then followed a long period
of taxonomic stability and some recent works
(Kemp & Kemp 1998, Borrow & Demey 2001,
2004, Ferguson-Lees & Christie 2001, Allan
2005) still consider African Goshawk as a single
species. Under any of the phylogenetic species
concepts, which tend to afford species rank to
all recognisable forms, other works prefer to
split African Goshawk into two species: African
Goshawk A. tachiro sensu stricto and ‘Red-chested
Goshawk’ A. toussenelii (Kemp 1994, Clark &
Davies 2000, Sinclair & Ryan 2003) and this
will also be the case in a forthcoming field guide
to African raptors (W. S. Clark pers. comm.).
Ail recent works retain Shikra as one species but
separate African Little Sparrowhawk from Red-
thighed Sparrowhawk.
Helbig et al. (2002) proposed guidelines
for assigning species rank, and, anticipating the
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -19
results of molecular work by ML s team ot
the Royal Museum for Central Africa (RMCA),
Tervuren, Belgium, it appears that it is still quite
acceptable to provisionally apply the concept of
superspecies’ in the case of African Goshawk.
There are behavioural arguments too, besides
their morphological resemblance (Dowsett &
Dowsett-Lemaire 1993). However, hybridisation
between the woodland form tachiro and the
forest form toussenelii is not yet proven in the
contact region in Kivu, DRC (Louette 2003; and
preliminary molecular work at the RMCA), and
the plumage of some aberrant individuals might
be due to age or individual variation. I therefore
prefer to employ the term paraspecies for tachiro
on the one hand, and for toussenelii on the other
(Louette 2003, 2007). Each paraspecies has four
morphologically identifiable regional populations
consequently treated here as subspecies.
In mainland equatorial regions, there is
just one subspecies in the paraspecies tachiro
(. sparsimfasciatus , which occurs from Angola to
Somalia), but three in the paraspecies toussenelii
(from west to east: macroscelides, from Senegal
to westernmost Cameroon; nominate toussenelii,
from Cameroon to western DRC; and canescens,
in central and eastern DRC) (see Fig. 1). The close
relationship of all subspecies of African Goshawk
is demonstrable when examining the endemic
island forms. The subspecies lopezi, restricted to
Bioko Island, in the Gulf of Guinea, is a membei
of the toussenelii paraspecies. It is well saturated
with rufous below, especially on the breast, flanks
and thighs and, in some, on the throat, the latter
a feature unique to this population, although it
is derived from macroscelides (Louette 2001). On
the opposite side of Africa, subspecies pembaensis,
a member of the tachiro paraspecies, is endemic
to Pemba Island, off Tanzania. This bird is more
deeply coloured than its founder population,
sparsimfasciatus in mainland Tanzania and on
Zanzibar (Louette 1993).
The isolated Ethiopian form unduliventer ,
which persists within ecological islands , is
intermediate in coloration between the two
paraspecies. According to the preliminary
molecular results, it could either be included in
the tachiro paraspecies or separated in its own,
third, paraspecies.
Figure 1 . Distribution of African Goshawk Accipiter tachiro subspecies.
Repartition des sous-especes de l’Autour tachiro Accipiter tachiro.
20 Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
Size and plumage variation in African
Goshawk
There is a cline in size in equatorial Africa, from
large East African to small West African birds:
eastern DRC birds have a c. 16% longer wing-
chord than those from Liberia, but again, the mass
difference is no doubt much greater, probably
c.40% (Louette 2001, 2003). Thus, macroscelides
in West Africa is the smallest subspecies, toussenelii
is slightly larger and canescens is again somewhat
larger, with sparsimfasciatus being the largest, sex
for sex; in the field, however, this will barely be
noticeable.
The pattern of spotting (in the juvenile) and
barring (in the adult) of the breast feathers is
variable among all subspecies (from heavily in
most subspecies to an almost unspotted immature
in toussenelii and canescens and an unbarred adult
canescens ). I have explained elsewhere (Louette
2000, 2007) that plumage characteristics are
functionally related to habitat (e.g. with plumage
colour intensity increasing with habitat density),
age and possibly mimicry.
The adult female of the woodland
sparsimfasciatus is cryptically coloured (probably
related to nesting activities), with individual
variation, possibly helpful for ‘image avoidance’
(so that potential prey does not learn the predator’s
colour pattern). Specimens from DRC can be
separated into two general morphs (with buff
and whitish bellies), but with a variable amount
of ventral barring. (Here the term ‘morph’ is
used, although Thomsett (2007) prefers to use
‘phase’ for a transitional plumage.) The adult
male is even more variably coloured, which is
in part age-related. A so-called ‘sepia’ morph — a
misleading name — exists (Plate 2: 4); this may
be a ‘first adult’ (subadult) plumage; it occurs in
at least part of the range (southern and eastern
DRC, Burundi, Kenya, Tanzania). Nevertheless,
some immatures, in their first (post-juvenile)
moult, are definitely buff or white ventrally, just
like adult females. These (subadult) plumages,
lacking the reddish flanks, may help to avoid
aggression from older, territorial males. But these
morphs also exist in adults, with no remaining
juvenile feathers. The ‘standard’ morph has not
yet been found in subadults, and may therefore
well be restricted to older birds. It has whitish
underparts, finely barred and dark grey upperparts
and reddish flanks, supposedly becoming darker
with age; it could be more conspicuous than
the buff and sepia morphs. This might assist in
territorial defence or be preferred by females. On
Plate 2, a wide variety of sparsimfasciatus plumages
is illustrated. Notice the paler general colour of
the ‘sepia’ morph compared to the ‘standard’
birds. The specimen used for this illustration
is young. Its juvenile characteristics (the as yet
unmoulted rufous-fringed uppertail-coverts, see
Louette 2003) are invisible on the plate.
The adult evergreen forest canescens shows
enforcement of colourful advertising plumage
and loss of sexual plumage dimorphism — more
pronounced colours may be useful for display in
the shade of the equatorial forest. Here, the first
adult plumage is heralded by the late moult of the
barred juvenile flank-feathers in both sexes. Its
juvenile is peculiar: it lacks (or has very few) breast
spots, suggesting image avoidance, but possibly
also character displacement (in order to help
differentiate individuals from Chestnut-flanked
Sparrowhawk A. castanilius ) or mimicry (of adult
Black Sparrowhawk A. melanoleucus ).
A rare melanistic morph, in both adult
and immature, is only known in East African
sparsimfasciatus.
The ‘normal’ immature of sparsimfasciatus has
two morphs: one with a whitish, the other with
a huffish ground colour (respectively 22 and 17
specimens in the RMCA collection).
Common identification problems
1. Separating African Goshawk from
Chestnut-flanked Sparrowhawk
In the rain forest zone, Chestnut-flanked
Sparrowhawk is the most likely candidate to be
confused with the local brightly coloured African
Goshawk of the toussenelii paraspecies. This is true
for immatures as well as for adults and is mainly
due to their similar size and superficially similar
coloration, combined with poor descriptions and
illustrations in some handbooks and field guides.
Chestnut-flanked Sparrowhawk is undoubtedly
still one of Africa’s least-known raptors. Louette
(1992) provided a key for distinction in the hand,
and Louette & Herroelen (2007) were the first to
publish a photograph.
Unfortunately, several publications (among
them Snow 1978) and some museum catalogues
mention Chestnut-flanked Sparrowhawk in their
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -21
22 -Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
Legend to plate on opposite page
Plate 1 . Adults of the forest taxa (with two woodland
birds for comparison).
Chestnut-flanked Sparrowhawk Accipiter castanilius
1-2 Adult female
3 Adult male
Illustrated are the extremes in variation in the amount of
red intermingled with black in the breast barring (which
exists in both sexes). The dark cast to the yellow legs and
feet is probably a good field character for perched birds.
Both sexes are very similar in coloration and mainly differ
in size.
Red-thighed Sparrowhawk A. erythropus
4 Adult female A. e. erythropus
5 Adult male A. e. zenkeri
A small species with heavily contrasting plumage colours
and especially conspicuous white throat and uppertail-
coverts.
African Goshawk A. tachiro
6 Adult female A. t. macroscelid.es. Underparts are
orange-chestnut barred whitish; the white throat is
finely barred grey.
7 Adult male A. t. toussenelii. Note the very lightly
barred, silvery grey throat.
8 Adult female A. t. sparsimfasciatus. A typical
individual.
9 Subadult male A. t. sparsimfasciatus. This c.l -year-old
individual is unusual as it has no rufous on its flanks.
1 0 Adult female A. t. canescens.
1 1 Adult female A. t. canescens. A less barred individual.
12 Adult male A. t. canescens.
Adult A. t. canescens is less heavily barred whitish below
than macroscelides and most toussenelii , and also than
Chestnut-flanked Sparrowhawk. Some toussenelii and
canescens , especially in the south-west of the range, are
almost plain rufous below, with a silvery cast. Adults of
both sexes of the paraspecies toussenelii are very similar in
coloration.
lists or among their holdings from West Africa,
but my examination of specimens proves this
to be incorrect in all cases. This species has
also been erroneously mentioned from Ethiopia
(BirdLife International 2009). Chestnut-flanked
Sparrowhawk is definitely known only from the
equatorial forest belt from Nigeria to DRC, where
it seems to be quite common. There are 101
Planche 1. Adultes des taxons forestiers (accompagnes
de deux oiseaux provenant de la savane arboree pour
comparaison).
Autour a flancs roux Accipiter castanilius
1-2 Femelle adulte
3 Male adulte
Nous avons illustre les extremes dans la variation du
rouge mele de noir dans les barres horizontales de la
poitrine (presentes dans les deux sexes). Le saupoudrage
noir des tarses et des pieds jaunes est probablement un
bon critere d identification sur le terrain pour les oiseaux
perches. Les deux sexes sont de coloration tres similaire et
different surtout en taille.
Epervier de Hartlaub A. erythropus
4 A. e. erythropus femelle adulte.
5 A. e. zenkeri male adulte.
Une petite espece aux couleurs du plumage tres
contrastees, d'ou ressortent la gorge et les sus-caudales
blanches.
Autour tachiro A. tachiro
6 A. t. macroscelides femelle adulte. Les parties
inferieures sont orange marron barrees de blanc ; la
gorge blanche est finement barree de gris.
7 A. t. toussenelii male adulte. Noter la gorge gris
argente et tres legerement barree.
8 A. t. sparsimfasciatus femelle adulte. Un individu
caracteristique.
9 A. t. sparsimfasciatus male subadulte. Ce specimen
d’environ un an est particulier par fabsence de
coloration rousse sur les flancs.
10 A. t. canescens femelle adulte.
11 A. t. canescens femelle adulte. Un specimen dont les
barres sont moins evidentes.
12 A. t. canescens male adulte.
Les barres blanches sur les parties inferieures de A.
t. canescens adulte sont moins apparentes que chez
macroscelides , la plupart des toussenelii , ainsi que chez
l’Autour a flancs roux. Certains toussenelii et canescens ,
et surtout ceux provenant du sud-ouest de leur aire de
repartition, ont les parties inferieures quasi uniformement
rousses et saupoudrees de gris argente. Les adultes des
deux sexes de la para-espece toussenelii sont de coloration
tres similaire.
specimens of Chestnut-flanked Sparrowhawk in
the collection of the RMCA, compared to 127
specimens of toussenelii — all collected randomly
during colonial times — suggesting that both are
about equally common in forested DRC, unless
there is a behavioural difference, which would
make one or the other more prone to be collected.
The range of Chestnut-flanked Sparrowhawk thus
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -23
Table 1 . Identification features of adults of five Accipiter taxa from mainland equatorial regions: four subspecies of African Goshawk A. tachiro and
Chestnut-flanked Sparrowhawk A. castanilius.
Tableau 1. Criteres d'identification des adultes de cinq taxons de Accipiter de regions equatoriales continentales : quatre sous-especes de
I’Autour tachiro A. tachiro et I’Autour a flancs roux A. castanilius.
Accipiter tachiro
Accipiter
macroscelides
toussenelii
canescens
sparsimfasciatus
castanilius
Upperparts
slate-grey
grey
grey
male: variable; mostly dark grey;
female: blackish brown
blackish
Throat
white, finely barred
grey
plain silvery grey
white or grey
pale grey, finely streaked
white, finely streaked
Breast and belly
rufous barred
greyish white
rufous barred
whitish or grey
most: (almost) unbarred
rufous: some: as toussenelii
whitish barred grey
dirty white with bold blackish-brown bars
(sometimes with chestnut traces)
Flanks
rufous
rufous
rufous
barred greyish brown (male) or
brown (female)
chestnut
Thighs
rufous
rufous
greyish white
barred greyish brown (male) or
brown (female)
plain chestnut
Tail
blackish with three relatively large white spots
white spots present, less distinct
or absent
blackish with 3-4 relatively large spots
Irides
usually yellow, occasionally orange
usually red
Legs and feet
bright yellow
bright yellow
bright yellow
bright yellow
bright yellow with black cast
Table 2. Identification features of immatures of five Accipiter taxa from mainland equatorial regions: four subspecies of African Goshawk A. tachiro
and Chestnut-flanked Sparrowhawk A. castanilius.
Tableau 2. Criteres d'identification des immatures de cinq taxons de Accipiter de regions equatoriales continentales : quatre sous-especes
de I'Autour tachiro A. tachiro et I’Autour a flancs roux A. castanilius.
Accipiter tachiro
Accipiter
macroscelides
toussenelii
canescens
sparsimfasciatus
castanilius
Upperparts
dark brown
blackish brown
blackish brown
brown
dark brown
Throat
dark brown
mesialstripe
white
white
white with central streak
white with central streak
Breast
drop-like spots
few or no spots
few or no spots
drop-like spots
heavily spotted
Belly
drop-like spots
white
white
white
white with a variable amount of spots
Flanks
barred dark
brown
broadly barred
dark brown
variable; some
heavily streaked
spotted
heavily streaked or barred
Thighs
barred dark
brown
white
white
drop-like spots
barred with wider bars than toussenelii
paraspecies
Legs and feet
yellow
yellow
yellow
yellow
yellow with black cast
partially overlaps with that of the three mainland
forms of the toussenelii paraspecies.
Adult Chestnut-flanked Sparrowhawk has
dark blackish upperparts and head-sides; in the
sympatric African Goshawks these are paler slate-
grey (in macroscelides ) or grey (in toussenelii /
canescens). Ventrally, the flanks of Chestnut-
flanked Sparrowhawk are also darker (chestnut
vs. orange or rufous in the toussenelii paraspecies)
and the breast and belly are dirty white with
bold, dark blackish-brown bars, sometimes with
chestnut traces; in African Goshawk these parts
are rufous barred whitish or grey (in toussenelii
and some canescens) or (almost) unbarred rufous
(in most canescens ) or whitish barred grey (in
sparsimfasciatus). The thighs are plain chestnut
24 -Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
Legend to plate on p. 26
Plate 2. Variation in adult African Goshawk woodland
taxon and flight patterns of different species
1-2 Adult male A. t. sparsimfasciatus in flight. The
variation in the amount of reddish on the flanks
and the underwing in A. t. sparsimfasciatus is quite
extensive. In adults the heavy colour saturation
overall is more often than not correlated to an almost
unpatterned underwing. However, underwing pattern
is quite variable, as shown here.
3 Adult male A. t. sparsimfasciatus. A particularly dark
specimen from south Sudan.
4 Apparently subadult male A. t. sparsimfasciatus in the
sepia morph.
3 Adult male A. t. sparsimfasciatus. Another variant with
more rufous colour in the barring, possibly an old
individual.
6 Adult male A. t. sparsimfasciatus. A normal, dark
male with typically barred underparts and rather
pronounced rufous flanks.
7 Adult female A. t. sparsimfasciatus. Some birds from
Kivu, eastern DRC, and especially those from Idjwi
Island in Lake Kivu, like this female, have a yellowish
or even chocolate wash to the underparts.
8 Adult female A. t. sparsimfasciatus. A bird with heavily
barred underparts and reddish flanks which was
suspected to be a hybrid canescens / sparsimfasciatus
(see Louette 2003).
9 Adult Red-thighed Sparrowhawk A. erythropus in
flight. Red-thighed Sparrowhawk is, with African
Little Sparrowhawk A. minullus , unique amongst
the African Accipiter in having a white band on the
uppertail-coverts.
1 0 Adult Chestnut-flanked Sparrowhawk A. castanilius
in flight. The tail spots are small but quite apparent.
1 1 Adult A. t. macroscelides in flight. Tail spots are
variable and may be absent.
12 Adult A. t. sparsimfasciatus in flight. Tail spots are
variable and may be absent.
in Chestnut-flanked Sparrowhawk; they are quite
variable in the African Goshawk: rufous barred
white or greyish, rufous mixed with white or
grey, plain grey or white barred grey. In the
■southern part of the range of toussenelii, there is a
silvery grey barring or cast over the orange-rufous
ground colour of the ventral side and the thighs.
The throat is white with some faint, narrow grey
bars in Chestnut-flanked Sparrowhawk, whereas
it is plain silvery grey in toussenelii and white in
canescens-, in the mainly allopatric macroscelides ,
however, the white throat is also finely barred.
Planche 2. La variation chez 1’Autour tachiro Accipiter
tachiro adulte du taxon de la savane arboree et patterns en
vol de differences especes
1-2 A. t. sparsimfasciatus male adulte en vol. La variation
dans l’intensite de la coloration rousse sur les flancs
et le dessous de 1’aile chez A. t. sparsimfasciatus est
considerable. Chez l’adulte une coloration intense sur
l’ensemble du corps est souvent correlee a un dessous
d’aile sans dessin caracteristique. Cependant, le dessin
du dessous de l’aile est fort variable, comme montre
ici.
3 Male adulte A. t. sparsimfasciatus. Un specimen
particulierement fonce provenant du sud du Soudan.
4 A. t. sparsimfasciatus probablement male subadulte de
la forme sepia.
5 A. t. sparsimfasciatus male adulte. Une autre variante,
avec plus de coloration rousse dans les barres, peut-
etre un individu age.
6 A. t. sparsimfasciatus male adulte. Un male fonce
caracteristique, presentant les barres typiques dessous
et une coloration rousse prononcee sur les flancs.
7 A. t. sparsimfasciatus femelle adulte. Quelques oiseaux
du Kivu, de Test de la RD Congo, et notamment
ceux de Hie Idjwi sur le lac Kivu, comme cette
femelle, ont les parties inferieures lavees de jaune ou
meme de brun chocolat.
8 A. t. sparsimfasciatus femelle adulte. Un oiseau au
dessous fortement barre et aux flancs roux qui fut
suspecte d’etre un hybride canescens / sparsimfasciatus
(voir Louette 2003).
9 Epervier de Hartlaub A. erythropus adulte en vol.
L’Epervier de Hartlaub (ainsi que l’Epervier minule)
est unique parmi les Accipiter africains par la bande
blanche sur les sus-caudales.
10 Autour a flancs roux A. castanilius adulte en vol. Les
taches sur la queue sont petites mais bien apparentes.
11 A. t. macroscelides adulte en vol. Les taches sur la
queue sont variables et peuvent etre absentes.
12 A. t. sparsimfasciatus adulte en vol. Les taches sur la
queue sont variables et peuvent etre absentes.
The two species have white spots on the upper tail
(Plate 2: 10-11).
Adult female Chestnut-flanked Sparrowhawk
is not noticeably smaller than male African
Goshawk in the area of overlap, but the black
breast barring, bright chestnut flanks and deeply
coloured chestnut thighs distinguish it from its
congener (Plate 1: 1-2).
Immature African Goshawks are quite variable
according to subspecies and region: toussenelii
and especially canescens are only sparingly spotted
ventrally, some even without spots; in macroscelides
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -25
Legend to plate is on p. 25
26 -Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
Legend to plate is on p. 28
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -27
Legend to plate on p. 27
Plate 3. Immatures (with adult Black Sparrowhawk A
melanoleucus)
1 Immature male A t. macroscelides. Resembles
immature Chestnut-flanked Sparrowhawk (2); they
are, however, sympatric only in southern Nigeria and
westernmost Cameroon.
2 Immature female A. castanilius. Note the browner
upperparts than A. t. macroscelides, more richly
coloured barring on the flanks and thighs, the
different shape to the ‘tear-drop’ breast markings,
and more mottling on the nape and back.
3 Immature female A. e. erythropus. Upperparts darker
than in any race of tachiro.
4 Immature female A. e. zenkeri. The underparts
pattern is quite distinctive: buffy-white with uniquely
spotted breast-sides and dark-barred flanks slightly
washed rusty.
5 Adult male A. melanoleucus. Note black patches on
flanks and thighs.
6 Immature male A. t. sparsimfasciatus (buff morph).
Generally a brownish bird, with much less
contrasting plumage than immatures of the toussenelii
paraspecies.
7 Immature female A. t. sparsimfasciatus (white morph).
Somewhat more contrasting than 6.
8 Immature female A. t. canescens. May look
superficially similar to 3, but has many fewer or no
black markings on flanks and plain white thighs.
9 Immature male A. t. canescens. As 8, but distinctly
smaller.
10 Immature male A. t. toussenelii. May look
superficially similar to 5, but has many fewer black
markings on flanks and thighs. Some specimens of
this subspecies have slightly more brown markings on
the underparts.
the spotting is well marked (Plate 3: 1, 8-10).
Nevertheless, the sympatric subspecies can be
difficult to separate from immature Chestnut-
flanked Sparrowhawk, which however always
has heavy ventral spotting. Immature Chestnut-
flanked Sparrowhawk also has darker brown
upperparts (especially after the rufous juvenile
feather tips have worn off) and the brown bars on
the thighs are equally both darker and wider than
in the paraspecies toussenelii. Within the range
of Chestnut-flanked Sparrowhawk the confusion
forms would be macroscelides in south-east Nigeria
Planche 3. Immatures (avec 1’adulte de 1’Autour noir A.
melanoleucus )
1 A. t. macroscelides male immature. Ressemble a
l’immature de l’Autour a flancs roux (2) ; ils ne sont
toutefois sympatriques qu'au sud du Nigeria et dans
l’extreme ouest du Cameroun.
2 Autour a flancs roux A. castanilius femelle immature.
Noter les parties superieures plus brunes que chez
macroscelides, les barres sur les flancs et les cuisses
plus richement colorees, les formes differences des
marques sur la poitrine, et le dos et la nuque plus
marbres.
3 Epervier de Hartlaub A. e. erythropus femelle
immature. Les parties superieures sont plus foncees
que chez n’importe quelle sous-espece de tachiro.
4 Epervier de Hartlaub A. e. zenkeri femelle
immature. Le pattern des parties inferieures est assez
caracteristique : blanc chamois avec les cotes de la
poitrine tachetes et les flancs avec des barres sombres
legerement lavees de roux.
5 Autour noir A. melanoleucus male adulte. Noter les
taches noires sur les flancs et les cuisses.
6 A. t. sparsimfasciatus male immature (forme chamois).
En general un oiseau brunatre, avec un plumage
beaucoup moins contraste que les immatures de la
para-espece toussenelii.
7 A. t. sparsimfasciatus femelle immature (forme
blanche). Quelque peu plus contrastee que 6.
8 A. t. canescens femelle immature. Peut sembler
superficiellement similaire a 3, mais possede
beaucoup moins ou quasi pas de marques noires sur
les flancs. De plus, les cuisses sont uniformement
blanches.
9 A. t. canescens male immature. Comme 8, mais
nettement plus petit.
10 A. t. toussenelii male immature. Peut paraitre
superficiellement similaire a 5, mais possede
beaucoup moins ou quasi pas de marques noires sur
les flancs et les cuisses. Certains specimens de cette
sous-espece presentent legerement plus de marques
brunes sur les parties inferieures.
/ south-west Cameroon or a small juvenile
male sparsimfasciatus (as illustrated on Plate 3).
Immature / juvenile toussenelii and canescens are
easier to separate, as they have a plainer white
breast with fewer or no drop-shaped markings.
Chestnut-flanked Sparrowhawk’s tail has fewer
and smaller white spots than sympatric African
Goshawk. If seen well the darker legs and feet of
the former should be distinctive in both adults
and immatures.
Photographs suggest some differences in the
amount of naked skin around the eye, the cere,
28 -Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
bill, legs and feet colours, and the head shape.
Adult Chestnut-flanked Sparrowhawk may have
the brighter yellow cere and facial skin of the two,
but this could be due to temporal, individual or
even sexual variation. 1 here is a photograph taken
at the nest in Kenya of a male sparsimfasciatus
showing a restricted amount of naked skin around
the eye (van Someren 1956), whereas this seems
quite extensive in the female. Legs and feet are
yellow in both species, but in Chestnut-flanked
Sparrowhawk it seems as if a black cast has been
put over the yellow ground colour. The head of
Chestnut-flanked Sparrowhawk is proportionately
wider (Louette & Herroelen 2007; Plate 1: 1).
An Accipiter photographed by M. Wilson,
at Bwindi, Uganda (Figs. 2-3), provoked a
discussion. Chestnut-flanked Sparrowhawk is not
yet known for Uganda, but its occurrence in this
border area with DRC is plausible. Obviously,
it is in adult plumage. However, the bird does
not show the decidedly black dorsal plumage
colour, or the dark cast to the yellow legs and
feet, which are so obvious in Chestnut-flanked
Sparrowhawk. Other features of the Bwindi
bird are the barred flanks and thighs; these are
plain chestnut in Chestnut-flanked Sparrowhawk
but barred in sparsimfasciatus , the subspecies of
African Goshawk in this area. Additionally, the
white tail spots are indistinct; the bars on the
vent are single-coloured reddish and lack the
black component typical of Chestnut-flanked
Sparrowhawk. A female sparsimfasciatus is large
and much paler than the bird in the photograph,
and the relative length of the tail and the size of
the person’s hand both indicate that the bird’s size
was approximately correct for a male. The bars on
the breast are bicoloured, which is not the rule for
a male, but not impossible.
2. Separating African Goshawk from larger
Accipiter species
The peculiar immature female of African Goshawk
in west-central Africa, between Cameroon and
DRC ( canescens and toussenelii) , which sometimes
lacks ventral spots, could be confused with adult
male Black Sparrowhawk (Plate 3: 5 and 8).
Superficially, the latter differs only in that it has
more extensive black patches on the flanks and
even more on the thighs (it also has the typical
adult red irides, whereas the immature female
African Goshawk still has brown or pale yellow
eyes).
3. Separating African Goshawk from smaller
Accipiter species
When size is difficult to appreciate in the field,
confusion of the small toussenelii males is also
possible with the generally smaller Red-thighed
Sparrowhawk; in fact, the largest females of Red-
thighed Sparrowhawk attain just about the same
size as the smallest males of Chestnut-flanked
Sparrowhawk (Plate 1: 3-4). Adults of these two
species have decidedly blackish upperparts (grey
in toussenelii) and red eyes (orange or yellow in
toussenelii ). Male Red-thighed Sparrowhawk is
noticeably smaller. Just as in African Goshawk,
the western nominate subspecies of Red-thighed
Sparrowhawk is smaller than the eastern subspecies
A. e. zenkeri, but to a lesser extent (c.5% difference
in wing-chord: Louette 2002), and it is usually less
saturated with rufous on the ventral side than the
eastern one (see Borrow & Demey 2001). The
ventral colour of female A. e. zenkeri is usually, but
not always, overlain with silvery grey, as is the case
with most toussenelii.
In woodland, where an appreciable size
difference separates male sparsimfasciatus from
female African Little Sparrowhawk, confusion is
less likely, although the identification of a lone
bird can prove difficult, even from a photograph,
see e.g. www.birdquest.net/afbid/birdspecies.
php?func=view&slideno=3&af_bs_id=276.
4. Separating African Goshawk from other
similar raptors
Shikra is also a common woodland Accipiter, its
iris is orange to red in the adult and its central pair
of tail-feathers is plain (compared to other species
discussed here, on Plate 2). Immature Shikra has a
dark mesial throat stripe and contrasting blotches
on the breast, which are lacking, indistinct or
narrow in African Goshawk.
It is less likely that African Goshawk will
be confused with Rufous-breasted Sparrowhawk
A. rufwentris or Ovambo Sparrowhawk A.
ovampensis ; these species exhibit several features
that distinguish them from the former and are
well depicted in several handbooks (although
a photograph of Ovambo Sparrowhawk is
misidentified as A. tachiro in del Hoyo et al. 1994:
79). Long-tailed Hawk Urotriorchis macrourus has
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -29
Figures 2-3. African Goshawk / Autour tachiro Accipiter tachiro sparsimfasciatus, Bwindi,
Uganda, 26 October 2000 (M. Wilson)
a much longer, graduated tail with a conspicuous
white bar at its base. Gabar Goshawk Micronisus
gabar has, among other differences, prominent
white uppertail-coverts, even when immature.
Key features to check
1. Iris and cere colour. This is often a useful
character for species recognition. The iris is red
in most adult Chestnut-flanked and Red-thighed
Sparrowhawks, but mostly yellow (occasionally
orange) in African Goshawk. The cere is bright
orangey-yellow in most Chestnut-flanked and
Red-thighed Sparrowhawks but rarely so bright
in the toussenelii paraspecies of African Goshawk.
In sparsimfasciatus it is yellow or (more often)
greenish-yellow (Chapin 1932, Zimmerman et al.
199 6; specimens in RMCA); in southern Africa
(nominate tachiro ) it is grey or greenish-grey
(Allan 2003, Kemp & Kemp 1998).
2. Leg and foot colour. Chestnut-flanked
Sparrowhawk is peculiar among African Accipiter
in having a blackish cast overlaying the yellow
ground colour. Ail RMCA specimens show this
feature, and this must be visible in live birds too.
All adult African Goshawks have bright yellow
legs and feet (although dark legs appear also
on a macroscelides specimen from The Gambia,
photographed by C. Barlow after it was kept in a
fridge for ten years).
3. Tail spots in adults. A. t. toussenelii, canescens
and macroscelides have three relatively large
white spots on the uppertail. While these spots
are largest in the toussenelii paraspecies, they
also occur in some individuals of the tachiro
paraspecies: in sparsimfasciatus some males have
them, but others do not and some females also
have spots, although these are less distinct. (In
southern Africa’s nominate tachiro only the male
has uppertail spots: Allan 1997).
Conclusion
It is important to realise that in such a variable
species as the African Goshawk, many characteristics
should be taken into account before a definite
identification can be made in those areas where it
occurs alongside other Accipiter species. Whilst it
cannot be excluded that individuals occasionally
occur outside their normal range, this must be
rare, because African Goshawks are sedentary.
Therefore, the locality is an important clue to the I
taxon concerned and possible contusion species.
Acknowledgements
Ron Demey initiated this project by suggesting an
overview paper for the information published up to
now in technical papers. Alain Reygel examined all the
specimens with me, photographed many of them for
Nik Borrow and proffered useful comments. Malcolm
Wilson sent the photograph of the Bwindi bird. Clive
Barlow sent photographs of birds from The Gambia.
Mary Hennen sent photographs of specimens in The I
30 -Bull ABC Vol 17 No 1 (2010)
Plumage variation in African Goshawk: Louette
Field Museum of Natural History, Chicago, USA. Bill
Claik and Emmanuel Cilissen provided other useful
advice.
References
Allan, D. G. 1997. Field identification of African
Accipiter species and similar-looking hawks. Bull.
ABC A: 74-82.
Allan, D. G. 2005. African Goshawk Accipiter tachiro.
In Hockey, P. A. R„ Dean, W. R. J. & Ryan, P.
G. (eds.) Roberts’ Birds of Southern Africa. Seventh
edn. Cape Town: Trustees of the John Voelcker
Bird Book Fund.
BirdLife International. 2009. IBA factsheet. Senkele
Sanctuary. www.birdlife.org/datazone/sites
(accessed 16 June 2009).
Borrow, N. & Demey, R. 2001. Birds of Western Africa.
Fondon, UK: Christopher Helm.
Borrow, N. & Demey, R. 2004. Field Guide to the
Birds of Western Africa. Fondon, UK: Christopher
Helm.
Brown, L. H., Urban, E. K. & Newman, K. 1982. The
Birds of Africa. Vol. 1. Fondon, UK: Academic
Press.
Chapin, J. P. 1932. The birds of the Belgian Congo.
Part 1 . Bull. Amer. Mus. Nat. Hist. 65.
Clark, W. S. & Davies, R. A. G. 2000. Taxonomic
problems in African diurnal raptors. In Chancellor,
R. D. & Meyburg, B.-U. (eds.) Raptors at Risk.
Proceedings of the 5th World Conference on Birds of
Prey and Owls, Midrand, Johannesburg, South Africa,
4-11 August 1998. Berlin: World Working Group
on Birds of Prey and Owls & Blaine, Washington
DC: Hancock House Publishers.
Dowsett, R. J. & Dowsett-Femaire, F. 1993. Comments
on the taxonomy of some Afrotropical bird species.
Tauraco Res. Rep. 5: 323-389.
Ferguson-Lees, J. & Christie, D. A. 2001 . Raptors of the
World. London, UK: Christopher Helm.
Helbig, A. J., Knox, A. G., Parkin, D. T., Sangster, G.
& Collinson, M. 2002. Guidelines for assigning
species rank. Ibis 144: 518-525.
del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1994.
Handbook of the Birds of the World. Vol. 2.
Barcelona: Lynx Edicions.
Kemp, A. C. 1994. Afrotropical Accipitridae. In del
Hoyo, J., Elliott, A. & Sargatal, J. (eds.) Handbook
of the Birds of the World. Vol. 2. Barcelona: Lynx
Edicions.
Kemp, A. &c Kemp, M. 1998. Birds of Prey of Africa and
its Islands. London, UK: New Holland.
Louette, M. 1992. The identification of forest Accipiters
in central Africa. Bull. Br. Ornithol. Club 112:
50-53.
Louette, M. 1995. A catalogued immature specimen
of the Pemba African Goshawk in the National
Museums of Kenya. J. East Afr. Nat. Hist. 84:
35-37.
Louette, M. 2000. Evolutionary exposition from
plumage pattern in African Accipiter. Proc. Ninth
Pan-Afr. Ornithol. Congr. Ostrich 7 1 : 45-50.
Louette, M. 2001. Redescription of African Goshawks
Accipiter tachiro on Bioko Island and the adjacent
mainland. Ostrich 72: 24-27.
Louette, M. 2002. Relationship of the Red-thighed
Sparrowhawk Accipiter erythropus and the African
Little Sparrowhawk A. minullus. Bull. Br. Ornithol.
Club 122: 218-222.
Louette, M. 2003. Size, plumage, moult and supposed
hybrids of African Goshawks (. Accipiter tachiro
/ toussenelii group) in DR Congo. Ostrich 74:
18-29.
Louette, M. 2007. The variable morphology of the
African Goshawk (. Accipiter tachiro). Ostrich 78:
387-393.
Louette, M. & Herroelen, P. 2007. Comparative
biology of the forest inhabiting hawks Accipiter
spp. in the Democratic Republic of Congo. Ostrich
78: 21-29.
Sinclair, I. & Ryan, P. 2003. Birds of Africa South of the
Sahara. Cape Town: Struik.
Snow, D. W. 1978. An Atlas of Speciation in African
Non-passerine Birds. London, UK: Br. Mus. (Nat.
Hist.).
van Someren, V. G. L. 1956. Days with birds. Fieldiana,
Zool. 38: 1-520.
Stresemann, E. 1923. Ueber einige Accipiter-Aiten. J.
Ornithol. 71: 517-525.
Thomsett, S. 2007. A record of a first year dark
plumage Augur Buzzard moulting into normal
plumage. Gabar 18: 25-30.
Zimmerman, D. A., Turner, D. A. & Pearson, D.
J. 1996. Birds of Kenya and Northern Tanzania.
London, UK: Christopher Helm.
"Royal Museum for Central Africa, B-3080 Tervuren,
Belgium. E-mail: michel.louette@africamuseum.be.
h Flat 5, 63-67 St George’s Drive, Pimlico, London SW1V
4DD, UK. E-mail: n.borrow@btinternet.com
Received 3 June 2006; final version accepted 26
October 2009.
Plumage variation in African Goshawk: Louette
Bull ABC Vol 17 No 1 (2010) -31
Status of Short-clawed Lark Certhilauda chuana
in south-eastern Botswana
Chris A. Brewstef, Keddy Mooketsa b and Marc Her remans
Le statut de l’AIouette a ongles courts Certhilauda chuana au sud-est du Botswana. La grande majorite
de la population de I’Alouette a ongles courts Certhilauda chuana , une espece endemique a I’Afrique
australe, se trouve au sud-est du Botswana. Des recensements par transect ont ete effectues en novembre
2007-janvier 2008 afin d’etablir son statut dans cette region et de comparer les resultats avec ceux d un
recensement effectue en 1992-93. En janvier 2008 des observations ont egalement ete faites pour etablir
les limites de son aire de repartition. Les resultats indiquent une modeste augmentation des effectifs et une
legere diminution de la superficie d’habitat approprie, tandis que l’aire de repartition a peu change. On n’a
pas trouve de correlation entre les changements de la superficie de l’habitat approprie et les changements des
effectifs, ce qui indique qu’a present il y a suffisamment d’habitat qui convient. Au sud-est du Botswana,
l’Alouette a ongles courts est presque entierement confinee a des terrains en jachere ou la cultivation est avec
des methodes agricoles traditionnelles. Les dernieres annees on a enregistre une diminution substantielle de
la surface plantee avec du sorgho et du mat's selon des methodes traditionnelles. Si cette tendance continue,
cela pourrait avoir un effet defavorable sur l’Alouette a ongles courts. L’espece beneficierait probablement
beaucoup de l’instauration d une prime gouvernementale pour stimuler [’utilisation de methodes agricoles
traditionnelles.
Summary. The large majority of the population of Short-clawed Lark Certhilauda chuana , a southern
African endemic, is found in south-eastern Botswana. A series of transect surveys was undertaken in
November 2007-January 2008 in order to establish its status in this region and to compare the results
with those obtained during a 1992-93 survey. In January 2008 observations were made to establish the
limits of its range. Results suggest a modest increase in numbers and a small decline in the area of suitable
habitat, whilst there has been little change to the range. No correlation between changes to the area of
suitable habitat and changes in numbers was found, indicating that currently there is no shortage of suitable
habitat. In south-east Botswana, Short-clawed Lark is almost completely confined to fallow land that has
been cultivated for field crops using traditional agricultural practices. In recent years there has been a large
decrease in the area of land cultivated with sorghum and maize using traditional practices. If this trend
continues, this could have an adverse impact on Short-clawed Lark. The most beneficial support for the
species is probably a government incentive to farmers to cultivate field crops using traditional practices.
S hort-clawed Lark Certhilauda chuana (Fig. 1)
is endemic to southern Africa. There are
two discrete populations: a large one in south-
eastern Botswana and the North West Province
of South Africa, extending marginally into the
Northern Cape and Free State Provinces, and a
smaller, isolated, population largely restricted to
the Pietersburg Plateau in Limpopo Province,
South Africa. A survey conducted in the 2004-05
breeding season in the North West, Northern Cape
and Free State Provinces indicated an apparent
range reduction and possible decrease of Short-
clawed Lark in South Africa (Engelbrecht et al.
2007). This prompted CAB and KM to undertake
a survey in south-eastern Botswana in November
2007-January 2008, in order to establish the
species’ current status in the country and make a
comparison with an earlier, unpublished survey
undertaken by MH in November-December
1992 and November-December 1993.
Short-clawed Lark is found territorially in pairs
for most of the year (Herremans & Herremans
1992). Only the male sings the territorial song
(Herremans & Herremans 1992). The male
usually sings from a bush, fence-post or small tree
up to cA m tall, occasionally from a clod of earth
in a ploughed field. In south-east Botswana the
intensity of its song increases dramatically from
October to December (Herremans & Herremans
1992). There is a spectacular aerial display,
which reaches its peak in October-November.
Territorial activity is much reduced in the latter
part of the rainy season, when birds are moulting,
and in the dry season (Herremans & Herremans
22 -Bull ABC Vol 17 No 1 (2010)
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
1992). In a study of the eastern population in
the Polokwane Game Reserve on the Petersburg
Plateau, Engelbrecht (2005) found that territorial
activity commenced in early August, reached
its peak towards mid and late September, then
continued at a low frequency throughout the
summer before reaching a second peak at the end
of the breeding season in March-April.
Farmers are often familiar with the species
and call it sebota , the Setswana word for lark.
Possibly because it is accustomed to the presence
of farmers it is a confiding species, showing little
fear of people. The first indication of its presence
is often of a male singing, just a few metres away.
It appears to have the tendency to move towards
an intruder, such as a person or vehicle, venturing
into its territory and then announce its presence
by singing at close range. Occasionally it follows
the intruder at close quarters, right through its
territory until the intruder has left. Due to its
confiding nature and its obtrusive habits, the
male is often easy to observe, particularly in early
summer.
Study area
Location
The study area was located in the core range of
Short-clawed Lark in south-eastern Botswana.
1 his is an area of c. 16,000 knr extending west
to c.24°59’E, north to c.24°00’S and east to
c.26°30’E. The international boundary with
South Africa represents the southern limit. There
are also a few records outside of this core range,
particularly north of 24°00’S (Herremans 1997).
i Climate
The climate is characterised by long hot summers,
with summer rainfall, and short, cool, dry winters.
Annual rainfall around Gaborone averages 450-
500 mm, with most rain falling in October-April
(Campbell & Main 2003). Rainfall varies greatly
from year to year. Annual rainfall data at Gaborone
since 1980 indicate that the summers with the
lowest rainfall were 1984-85, with 243 mm,
1991-92, with 2 44 mm, and 2006-07 with only
1 45 mm (Department of Meteorolgical Services,
Gaborone, in litt. 2008). For the same period
the summer with the highest annual rainfall was
1999-2000, with 886 mm; 2007-08 was also
particularly wet, with 713 mm. The study period
was thus preceded by a particularly dry summer.
Habitat
The natural vegetation of south-east Botswana
is predominantly Acacia savanna, though habitat
dominated by broad-leaved tree species is also
widespread, particularly on sandy soils and rocky
hills. Short-clawed Lark occurs primarily in areas
with Acacia savanna. Its distribution is centred
on luvisols and lixisols on granite substrate. The
species is generally absent from rocky ground
and, accordingly, avoids rocky hills (Herremans
1997). Rocky hills occupy extensive areas in south-
east Botswana, particularly between Mochudi and
Molepolole and also to the south-west of Gaborone,
and around Kanye and Lobatse. The species avoids
Kalahari sands, which are most prevalent in the
west of the study area, at the eastern edge of the
Kalahari and also avoids vertisols, though such
soils are localised and mainly confined to the area
between I lokweng and Sikwane (Ministry of
Agriculture 1990).
Most land in south-east Botswana is tribal
leasehold land. There is, however, an extensive
block of freehold farms around Lobatse, and
immediately north and south of Gaborone is also
private land. The city of Gaborone is situated
on former freehold farming land. Short-clawed
Lark is almost totally confined to areas of tribal
land that have been cultivated using traditional
dry-land farming practices (Herremans 1997,
2005). Such traditional practices involve the dry-
land planting of field crops, mainly sorghum and
maize, and the grazing of fields, after crops have
been harvested, by livestock, primarily cattle,
donkeys and goats. Short-clawed Lark prefers
fallow fields, grazed by livestock, with scattered
bushes and small trees, primarily Acacia tortilis ,
though occasionally A. mellifera and Dichrostachys
cinerea (Fig. 2). It has a preference for open
habitat. Large open fields devoid of bushes or
small trees, characteristic of commercial farms,
are also unsuitable. However, the great majority
of arable land in south-east Botswana is cultivated
using traditional practices. According to data for
2002, 42.8% of the 16,000 km 2 core range of
Short-clawed Lark is considered to be land either
cultivated, or previously cultivated, for crops
using dry-land farming practices (Department of
Surveys and Mapping, Gaborone, in litt. 2008).
However, this figure is likely to include some land
subsequently encroached by Acacia and no longer
suitable for Short-clawed Larks.
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Bull ABC Vol 17 No 1 (2010) -33
Figure 1 . Short-clawed Lark / Alouette a ongles courts Certhilauda chuana, Ntlhantlhe, south-eastern Botswana, August
2008 (Eugenie Skelton)
Methods
Both in 1992-93 and in 2007 a series of transect
surveys was undertaken along a representative
selection of routes in order to estimate the number
of territories of Short-clawed Larks and to assess
the area of habitat suitable for the species. The
same methods were used for both sets of surveys so
the results are directly comparable. Most transects
were undertaken along gazetted roads but a few
went along un-gazetted tracks. All transects had a
width of 400 m — 200 m on either side of the road
or track. Hence for every 1 km of road or track, 40
ha were surveyed.
A Short-clawed Lark was usually first
located when a singing bird was heard, although
occasionally one was first located by the sound of
its alarm or contact call. Only veiy seldom was
a bird initially located by sight. The presence of
a singing bird or of a bird in display flight was
considered to be evidence of a territorial pair.
Habitat was considered to be suitable for Short-
clawed Larks if it was open land or fallow land
with or without scattered trees or bushes, and
unsuitable if it was thick, closed bush, woodland,
habitation or had a rocky substrate. Occasionally
birds were found in unsuitable habitat, such as
closed bush or the vicinity of habitation, but
always there was suitable habitat nearby, within
100 m from the bird. Fallow land that had been
largely encroached by Acacia was considered to
be no longer suitable. For each transect habitat
was recorded at 100-m intervals for the entire
transect, so that the area of habitat and proportion
of the land suitable for Short-clawed Lark could
be calculated. Habitat was recorded separately
on each side of the road, as quite often there was
suitable habitat only on one side of the road.
Along each transect, on both sides of the road, the
start and finish of suitable habitat, to the nearest
100 m, was recorded.
All transects were undertaken by vehicle.
Wherever habitat was considered to be suitable,
the vehicle was driven slowly and stopped at
100-m intervals to listen for Short-clawed Larks
within 200 m of the road or track. If, following a
wait of five minutes, no Short-clawed Larks were
recorded, a tape-recording of the song (recorded
by MH in 1992-93) was played, using the sound
system of the vehicle. For all singing birds, the
perpendicular distance of the bird to the road and
coordinates of the point on the road closest to the
bird, were recorded. Coordinates were recorded
34 -Bull ABC Vol 17 No 1 (2010)
Status of Shot t-clawed Lark in south-eastern Botswana: Brewster et al.
Figure 2. Short-clawed Lark Certhilauda chuana habitat,
Ntlhantlhe, south-eastern Botswana, August 2008
(Eugenie Skelton)
Habitat de l’Alouette a ongles courts Certhilauda chuana,
Ntlhantlhe, Botswana du sud-est, aout 2008 (Eugenie
Skelton)
correct to the nearest hundredth of a minute,
using a Garmin GPS, model MAPbOCx. If birds
were recorded at successive stops, 100 m apart,
then an effort was made to hear all birds recorded
at both stops at the same time, to avoid recording
the same bird or birds twice. When they could not
be heard at the same time they were not recorded
as birds had the tendency to follow the vehicle
while it remained in their territories.
Most field work was undertaken in the
morning, starting as early as possible after sunrise
(05.30 hrs); it was seldom continued after 14.00
hrs. Territorial males are most vocal early in the
morning, and till c. 10.00 hrs it was generally
possible to locate them without playing the tape-
recording. From c. 10.00 hrs to c. 14.00 hrs males
were less vocal, although they would often still
sing. To locate males at this time it was often
necessary to play the tape recordings of the song
and wait for a response; these tape recordings
included both dialects. After c. 14.00 hrs rerritorial
males became much more difficult to locate, even
using playback. Evidence of this was obtained for
the transect survey undertaken along the Kanye-
Mmathethe road. When this transect was surveyed
in the mid-afternoon, no birds were recorded
despite the habitat being suitable, but when the
transect was re-surveyed in the early morning, two
weeks later, seven pairs were located.
The efficiency with which birds were located
was probably also influenced by the weather
conditions. It was generally easier to locate birds
on windless days than on windy days. It was also
easier to locate birds on cool days, following a
period of rain rather than during hot and/or dry
periods. Fortunately, during the 2007 surveys the
weather was relatively cool and cloudy with well
above average rainfall, with nearly all transects
being undertaken in favourable conditions.
In 1992-93 a total of 1,350 km were surveyed.
To allow direct comparison, the large majority of
transects in 2007 were exactly the same as in 1 992-
93. However, transects in which no Short-clawed
Larks were recorded in 1992-93, such as from
Mochudi and from Sikwane to Olifants Drift, were
not repeated in 2007 (see Appendix 1 for all place
names mentioned). Transects on which Short-
clawed Larks were recorded only at low density in
1992—93, were not deemed to be a priority, so the
majority of such transects were not surveyed again
in 2007. Un-gazetted tracks in rural Botswana tend
to vary their route over time, due to allocation of
fields and plots, fallen trees and erosion. Attempts
to follow the exact routes of three transect surveys,
from Oodi ro Mochudi, from Mogoditshane to
the eastern corner of rhe international airport and
from Makgomane to Tswaaneng, which were
undertaken on un-gazetted tracks in 1992-93,
were unsuccessful as the exact route followed
could not be re-located. Accordingly the data for
these three transects are not directly comparable
(although they are certainly in the same area).
One transect, from Pitsane via Tlharaseleele to
Rakhuna, adjacent to the area where Engelbrecht et
al. (2007) searched unsuccessfully for Short-clawed
Larks in South Africa, was surveyed in 2007,
though it had not been surveyed in 1992-93.
In January 2008 S. & L. Tyler, using the same
methods, surveyed an additional transect from
Botlhapatlou via Hatslatladi to Lentsweletau that
was also not surveyed in 1992-93; the results of
this transect are included in the data. In 2007-08
transects surveyed had a total length of 990 km,
which represents r.2.5% of the core range of
Short-clawed Lark; 841 km of these are directly
comparable with data for 1992-93.
In January 2008, an effort was made, with
the assistance of S. & L. Tyler, to visit areas at
the edge of the range that had not been covered
in transect surveys, in order to establish the range
limits. Locations where the species occurred 15
years previously were revisited to ascertain if there
had been any range changes.
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Bull ABC Vol 17 No 1 (2010) -35
Results
Survey efficiency
The estimated perpendicular distances of territorial
birds from the road or track (the centre of the
transect) are grouped into 10-m class intervals and
are presented in Fig. 3.
The estimated perpendicular distances show a
bias to more ‘convenient' distances from the road,
particularly for greater distances. Class intervals,
such as 100 < d < 110, 150 < d < 160 and
200 < d < 210 (d = perpendicular distance, in
metres, from road) are represented in the data
more frequently than other class intervals, because
ol rounding-off of estimates.
The data clearly indicate that a greater
proportion of territorial birds were recorded closer
to the road than further away. Indeed, 77% of
territorial birds were recorded at <110 m from
the roads, while only 23% were found in the
peripheral 48% of the transects.
It is reasonable to assume that the data do
not include all the territorial males present within
the transects. To estimate the proportion of
birds present that were detected in a survey is
not straightforward. Assuming the drop-off in
numbers recorded with distance (Fig. 3) represents
the probability of being detected as a function
of distance, we can fit a polynomial curve and
estimate the efficiency of the surveys. Accepting
the curve as a probability density function, it can
be estimated that only 46% of the birds present
were actually recorded during the surveys (though
see also Discussion).
Numbers and population density
The 30 transects that were surveyed both in
1992-93 and in 2007, for which the results are
directly comparable, are listed in Table 1.
For comparable transects a total of 396 pairs
were recorded in 1992-93 and 447 in 2007,
representing a 12.9% increase. While the results
suggest that the numbers ol pairs increased between
the two surveys, the area of habitat considered
suitable for Short-clawed Larks decreased slightly,
from 11,410 to 10,810 ha, i.e., for comparable
transects, a 5.3% reduction. Accordingly, there
was also an increase in density in suitable habitat,
from 3.57 pairs / 100 ha in 1992-93 to 4.14 pairs
/ 100 ha in 2007, an increase of 19.2%.
Short-clawed Lark is clearly more common
in some parts of its range than in other areas. In
20 40 60 80 100 120 |40 160 180 200
20 40 fit) 80 100 120 140 160 180 200
Figure 3. Perpendicular distance of pairs of Short-clawed
Larks Certbilauda chuana from line of transect.
Distance perpendiculaire des couples de l'Alouette a
ongles courts Certbilauda cbuana par rapport au transect.
2007 the highest densities were around Mosopa,
Kubung and Thamaga; >10 pairs / 100 ha of
suitable habitat were recorded for several transects
in this area. Relatively high densities of >6 pairs /
1 00 ha of suitable habitat were also found around
Ntlantlhe and north of Gaborone. Densities in the
southern part of the range, south of the Lobatse-
Kanye main road, were noticeably lower: south of
25°10’S densities for all transects were < 4 pairs /
100 ha of suitable habitat. The pattern of densities
is illustrated in a 15-minute grid (Fig. 4).
For most transects more pairs were recorded
in 2007 than in 1992-93. Those for which fewer
were recorded are Bokaa-Kopong (from 12 pairs
to nine pairs), Lentsweletau-Kopong (ten pairs
to five pairs), Letlhakeng-Gasese (24 pairs to
three pairs), Mmangodi-Moshupa (26 pairs to
22 pairs), Boatle-Mmankgodi (11 pairs to eight
pairs), Mmathethe-Metlojane (11 pairs to two
pairs), Good Hope-Mmathethe (nine pairs to six
pairs) and Metlojane— Good Hope (two pairs to
one pair). For the Mmankgodi-Mosopa transect,
the reduction in numbers was due to a large
decrease in pairs recorded around Mmankgodi,
whereas near Mosopa a small increase was actually
recorded.
36 -Bull ABC Vol 17 No 1 (2010)
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Table 1 . Summary of results of transect surveys (from north to south)
Tableau 1 . Apergu des resultats des recensements par transect (du nord au sud)
TRANSECT
Total ha
% suitable habitat
Pairs
Density, pairs/100 ha
in suitable habitat
2007
1992-93
2007
1992-93
2007
1992-93
Molepolole-N of Hatsalatladi
2,180
34.4
25.7
19
13
2.54
2.32
Molepolole — Lentsweletau
1,400
22.8
23.6
5
3
1.57
0.91
Lentsweletau — Rasesa — Pilane
1,334
19.7
12.9
4
1
1.52
0.58
Lentsweletau— Kopong
1,020
9
15.4
5
10
5.42
6.37
Bokaa— Kopong
572
34.8
38.5
9
12
4.52
5.45
Mabalane — Mochudi
1,682
7.3
14.2
2
1
1.62
0.42
Mmamashia turn-off — Modipane — Mabalane
1,664
20.8
16.9
9
2
2.6
0.71
Letlhakeng— Gasese
1,994
19.8
29.6
3
24
0.76
4.06
Gasese— Pitseng
844
41
52.3
16
11
4.62
2.49
Molepolole — Thamaga
1,398
27.7
20.8
18
10
4.65
3.44
Thamaga— west along power-line
1,360
15.9
36
23
14
10.63
2.86
Kubung— north to power-line— N of Losilokgokong
924
20.5
24.5
25
19
13.17
8.4
Mosopa — Kubung
644
25.2
20.9
19
6
11.72
4.46
Mosopa— edge of sandveld (Ralekgetho road)
792
31.1
27.5
17
15
6.9
6.89
Mosopa— Thamaga
624
21.1
51.3
14
11
10.66
3.44
Mmankgodi— Mosopa
948
24.3
36.3
22
26
9.58
7.55
Boatle (Ramotswa turn-off)— Mogonye— Mmankgodi
1,060
18.8
28.2
8
11
4.01
3.68
Mogobane turn-off — Borotsi — Ntlhantlhe — Ranaka
1,396
38.8
36.1
40
37
7.38
7.34
Ranaka— south through fields— Ntlhantlhe
778
62.8
47.4
43
41
8.8
11.13
Ntlhantlhe — Gamoswane (Kanye — Lobatse road)
858
57.8
62.6
38
36
7.67
6.71
8 km along Mmathethe — Kanye road
326
79.1
70.2
7
5
2.71
2.18
Pelotshetlha turn-off— Dipotsana
748
52.8
75.5
10
8
2.6
1.42
Lobatse road turn-off— Mmathethe
1,548
55.7
56.8
17
16
2.07
1.82
Mmathethe— Metlojane
1,084
28.1
21.3
2
11
0.66
4.77
Mmathethe— Good Hope
1,100
39.4
30.6
6
9
1.38
2.67
Mmathethe— Metlobo
1,470
43.2
45.3
14
10
2.21
1.5
Good Hope— Lorwana
944
57
75
18
17
3.34
2.4
Metlojane— Good Hope
372
60.1
43.5
1
2
0.45
1.24
Metlojane— Makgomane
630
79.2
60.9
15
7
3,01
1.83
Borobodilepe — Hebron — Phitsane Molopo
1,946
28.2
27.2
18
8
3.27
1.51
TOTAL OF 30 TRANSECTS SURVEYED IN BOTH 1992-93 AND 2007
33,640
32.1
33.9
447
396
4.14
3.47
Oodi— Mochudi
1,282
14.1
11
6.08
Oodi— Mochudi
1,580
18.9
3
1.05
Mogoditshane— Mmopane— E corner of airport
896
28.4
18
7.08
Mogoditshane— Mmopane— E corner of airport
1,092
30.9
14
4.14
Makgomane— Tswaaneng
1,132
48
4
0.74
Makgomane— Tswaaneng
1,256
47.1
4
0.68
TOTAL OF 33 TRANSECTS (2007 data)
36,950
31.9
33.6
480
417
4.07
3.3
Lentsweletau— Botlhapatlou (January 2008)
1,962
29.3
37
6.25
Pitsane — Tlharaseleele — Rakhuna
692
54.5
4
1.06
TOTAL OF ALL DATA
39,604
32.2
521
4.09
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Bull ABC Vol 17 No 1 (2010) -37
There is no correlation between change in
area ot suitable habitat and change in numbers,
indicating that there is currently no shortage of
suitable habitat. While near Mmankgodi and
Kopong a decline in numbers appears to be
related to bush encroachment, there are other
transects where numbers have increased despite
a large decrease of suitable habitat between
the two surveys. For example, for the transect
from immediately north of Thamaga westwards
along the power-line, the area of suitable habitat
decreased from 490 ha to 216 ha, whilst the
number of pairs recorded increased from 14 to
23 pairs.
In 2007 the highest densities of Short-clawed
Larks were recorded for the transect northwards
from Kubung to north of Losilokgokong, with 25
pairs in 189.86 ha, i.e. 1 pair / 7.6 ha. Noticeably
high densities were also recorded locally around
Gathwane, on a section of the transect from
Good Hope to Lorwana. Around Gathwane ten
pairs were recorded in 78 ha of suitable habitat,
a density of 1 pair / 7.8 ha. In 1992, between
Ranaka and Ntlhantlhe, 30 pairs were recorded in
234 ha ol suitable habitat, i.e. 1 pair / 7.8 ha.
Continued occupation by territorial males
In both surveys, coordinates (correct to the nearest
hundredth of a minute) were recorded for the
point on the road closest to each territorial male.
The perpendicular distance from the road was also
recorded. With these data the localities of territories
could be compared between the two surveys.
For all birds recorded less than 110 m from
the road in 2007, 38% (127 out of 334) were in
the same localities (±100 m) as a territorial male
in 1992-93. For birds <60 m from the road, 39%
(93 of 237) were at the same location (±100 m) as
a territorial bird in 1992-93. However, continued
occupation of localities by territorial males was in
general lower, or even non-existent, for transects
where Short-clawed Lark occurs at lower densities
and higher for transects with higher densities.
Such a relationship is perhaps not unexpected
as where Short-clawed Larks occur at highest
densities, the great majority of suitable habitat
is likely to be occupied. The highest continued
occupation of localities by territorial males was
for all three transects near Ntlhantlhe where 63%
of the territories <1 10 m from the road remained
occupied and 68% of those <60 m from the road.
Range limits
The 1992-93 survey found that the core range
of Short-clawed Lark extended westwards to
Phitsane Molopo, Tswaaneng, Metlobo, Pitseng
and Gasese. Field work in January 2008, in areas
not visited in 1992-93, established that it extends
slightly further west along the Molopo Valley,
west of Phitsane Molopo. The westernmost record
in this area is of a bird seen west of Leporung
at 25°47.50’S 24°52.27’E. In January 2008 the
species was also found commonly to the south of
Sesung. These records extend its known range but
it seems likely that it had simply been overlooked
in 1992-93, due to lack of visits, rather than the
species has expanded its range.
Between Gasese and Letlhakeng, along the
Moshaweng Valley, there was a drastic reduction
in numbers at the edge of the range between the
two surveys: from 24 territorial males in 1992 to
only three in 2007. In 2007, the most northerly
record was in the Moshaweng Valley at 24°22.97’S
25°01.04’E, exactly where there was also a record
in 1992, whereas in 1992 the northernmost record
was at 24°14.82’S 24°59.84’E, 16 km further
north. The apparent contraction of range from the
northern Moshaweng Valley is the only indication
of any change in the core range between the two
surveys.
The northern limit of the core range of Short-
clawed Lark is c.24°00’S. North this there are
only scattered records. There were rwo isolated
records in 1993, north-west of the core range,
one c. 14 km north-northwest of Letlhakeng and
the other c. 17 km north-west of Botlhapatlou.
These two locations were not visited in 2007-08;
both are situated in valleys, which provide some
localised suitable habitat, in areas that are largely
unsuitable for Short-clawed Larks, due to the
predominant Kalahari sands.
In 1992 two birds were found near Lephephe,
well to the north of the core range of the species,
and birds were also recorded at two other different
locations to the east-northeast of Lephephe. There
was also, in 1992, an isolated record east of
Shoshong at 23°15.01’S 26°34.85’E, which is the
most northerly location at which Short-clawed
Lark has been reported in Botswana. In 2007-08
the Lephephe area was searched, without success,
for Short-clawed Lark. Attention was then focused
on the Sojwe area, west of Lephephe, where a
territorial bird was eventually located 1 1 km
38 -Bull ABC Vol 17 No 1 (2010)
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
25°E
26°E
27°E
Shoshong
x
Mahalapye
■ X X
Sojwe
BOTSWANA
N
i
Botlhapatlou
X Letlhakeng
■ ■
Lentsweletau
s'
Molepolole
Mochudi
Mogoditshane Gaborone
Moshupa
Thamaga
Tlokwang
f
SOUTH
AFRICA
Ramotswa
■
Kanye
Lobatse
t
Goodhope
Pairs (d)/ lOOha
Relative
of suitable habitat
abundance
d < 2
■
uncommon
2<d<6
■
fairly
common
6 <d < 10
■
common
d > 10
■
very
common
X
recorded
in 1992-93
Okm
50km
Figure 4. Distribution of Short- clawed Lark Certhilauda chuana in
south-eastern Botswana 2007-08.
Repartition de l’Alouette a ongles courts Certhilauda chuana au sud-
est du Botswana 2007-08.
north of Sojwe. The continued presence of Short-
clawed Lark in the Lephephe area was therefore
confirmed, though it certainly must occur only
sparsely in this area
In the east, in 1992-93, transect surveys from
Sikwane and from Mochudi to Olifants Drift
failed to produce any records of Short-clawed Lark
and, apart from one record c.20 km south-east of
Mochudi, on the road to Mabalane, it was not
found to the east of Mochudi. In January 2008
territorial birds were seen about 22 and 28 km
east north-east of Mochudi. These records extend
the known limits of its range in the east; it is
likely, however, that Short-clawed Lark had been
overlooked in this area, due to lack of visits, rather
than the species had extended its range.
Short-clawed Lark was searched for, without
success, between Tlokweng, a large urbanised
village immediately to the east of Gaborone, and the
South African border; the predominantly
black cotton soils in this area appear to
provide unsuitable habitat. It was neither
recorded in the city of Gaborone, nor on
freehold land immediately to the south
of Gaborone, where suitable habitat is
lacking. On most freehold land to the
north and south of Lobatse it is likely to
be absent due to lack of suitable habitat
(rocky hills and wooded savannas). It
does, however, occur commonly close to
the South African border in the Ramotswa
area.
Population estimate
An estimate of the population of Short-
clawed Lark in south-eastern Botswana
involves the consideration of several
parameters. These include the range, the
proportion of the range that is suitable,
the representativeness of the transects,
the density in suitable habitat and the
proportion of the territories that were
detected in surveys.
Lhe total range, excluding the
outlying Lephephe area, where it occurs
only sparsely, is estimated at 16,000 km 2 .
For the calculations, we use 2007 and
January 2008 transects except for parts of
three transects (Mmamashia-Mabalane,
Mabalane-Mochudi and Letlhakeng-
Gasese) that are not considered to be
within the range. 2002 data (Department
of Surveys and Mapping, Gaborone, in litt. 2008)
indicate that 42.8% of the range of Short-clawed
Lark has a land-use which could make it suitable
for the species. From our transect surveys 31.7% is
suitable habitat and the average density of Short-
clawed Lark here was 3.9 pairs / 100 ha; we use
these figures in the calculation.
The proportion of occupied territories that
were detected during transect surveys is more
debatable than the other variables. We use the
figure of an efficiency of 46% as indicated by
the curve in Fig. 3, which could represent a
probability-density function.
Based on the above figures, we estimate the
total population of Short-clawed Larks at 43,000
pairs. If the efficiency of the data is assumed to
be higher (e.g. 60%, see discussion for particular
reasons affecting the probability of recording),
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Bull ABC Vol 17 No 1 (2010)- 39
the population could be 33,000 pairs. Both these
figures contain a wide margin of error. While
it is difficult to make a more accurate estimate,
it seems reasonable to assume that the total
population in 2007 was in excess of 20,000 pairs.
This is an improvement on the previous estimate
(‘over 10,000 pairs’) made by Herremans (2003),
which even referring to data of 1992-93 may have
been too prudent.
Discussion
For comparable transects a 12.9% increase in
numbers and a 19.2% increase in density was
recorded between the two surveys. The methods
used for the two surveys were the same. However,
some of the differences in numbers could possibly
be accounted by factors other than an increase
in numbers. For example, comparable transect
surveys could have possibly been undertaken at
different times of day, when detection rates are not
necessarily the same. Secondly, weather conditions
might not have been the same for comparable
transects; surveys undertaken in good conditions
are likely to be more comprehensive than surveys
undertaken in unfavourable conditions, such as
windy or hot days. There might too have been
differences in the approaches of the observers.
Due to these factors it likely, as stated above,
that the data contain a wide margin of error.
Nevertheless, the results of the two surveys suggest
that there has been a modest increase in numbers
between the two surveys.
There appear to be three possible reasons for a
greater proportion of birds being recorded closer
to roads. Firstly, detection probability decreases
with distance: birds that are at greater distance
from the road are more likely to be overlooked as
their vocalisations are less likely to be heard than
those that are closer to the road, particularly on
windy days. Secondly, as already indicated, Short-
clawed Larks tend to move towards an intruder,
which makes them more likely to be encountered
nearby than further away. Birds at greater distances
are, however, expected to be less likely to move to
an intruder as their territories would be less likely
to include the road. Thirdly, the use of a tape-
recording to locate territorial birds is more likely
to be effective for birds nearby than for distant
birds, particularly because the vehicle’s sound
system was not powerful (50 watt). However, these
factors could be partially offset by the tendency of
all males to commence singing when they hear one
male start to sing. These reasons indicate that the
probability-density function as presented in Fig. 4
might underestimate the efficiency of the surveys,
because there are genuine reasons for birds to be
detected closer to the roads.
The decline in numbers recorded around
Kopong and Mmankgodi is likely to be related
to a relatively large reduction in suitable habitat:
in 2007, bush encroachment on land that had
previously been cultivated was particularly
noticeable. When fields are not cultivated any
longer and become steadily encroached by bushes
and trees, primarily acacias, they become unsuitable.
For the three transects between Mmathethe, Good
Hope and Metlojane, however, the decrease in the
number of pairs recorded between the two surveys
is not obviously related to a change in habitat;
there was actually a large increase in suitable
habitat for these transects. The factors that might
have caused this apparent reduction in numbers
are unclear.
Engelbrecht (2005) states that males defended
approximately 6- 10-ha territories in a study of
the eastern population in the Polokwane Game
Reserve. The size of these territories is remarkably
similar to the highest densities recorded in the
two surveys in Botswana. This suggests that
when Short-clawed Lark was recorded at its
highest densities in south-east Botswana, almost
all available suitable habitat was occupied by
territorial males.
Considering, firstly, that not all territorial
birds were recorded and, secondly, that 12.9%
more territories were located in 2007 compared to
1992-93, the degree of continued occupation of
localities by territorial birds is probably considerably
higher than the above figures suggest. If all
territories <60 m from the road were detected in
2007 and 60% of the territories, irrespective of the
distance from the road, were detected in 1992-93,
then an estimated 65% of the localities recorded as
occupied in 2007 were also occupied in 1992-93.
Given the higher number of territories recorded
in 2007, the degree of continued occupation of
localities over the period between the two surveys
is likely to be slightly higher, possibly over 70%.
These figures suggest that localities have ceased to
be occupied at an estimated average rate of c.3%
per annum between the two surveys.
40 -Bull ABC Vol 17 No 1 (2010)
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Threats
The data from 2007 support Herremans’ (1997,
2005) contention that Short-clawed Lark in
south-east Botswana is almost totally restricted
to tribal land that is cultivated using traditional
agricultural practices. Any changes to agricultural
practices are therefore likely to have an impact on
the species.
Although there is an extensive block of freehold
farms to the north and south of Lobatse, the great
majority of agricultural land is tribal land under
traditional farming practices. While there have
been no major changes in either land ownership
patterns or farming practices in recent years, and
none seem likely in the near future, there has been
a steady decrease in the area of tribal land that
has been cultivated for field crops (Ministry of
Agriculture, Gaborone, in lift. 2008). Botswana is
prone to a great variation in rainfall from year to
year. In drought years the area planted with field
crops is very small, while in years of good rainfall a
much greater area is planted. For the ten years from
1981-82 to 1990-91, mean annual area planted
for field crops in the traditional sector was 227,890
ha. For the ten years from 1996-97 to 2005-06
(the last year for which figures are available) this
area decreased by 53% to 106,260 ha. In 1988-89,
a year of good rainfall, 237,100 ha of sorghum
and 76,000 ha of maize were planted in the
traditional sector, while in 2005-06, another year
with good rainfall, the totals were only 38,700 and
45,900 ha. These figures illustrate the precipitous
decline of the area planted with sorghum in the
traditional sector in recent years. The area planted
with maize has also decreased, but less markedly.
Though there are no supporting data, the reasons
for these decreases are likely to be primarily socio-
economic. With increasing prosperity and a higher
standard of education young people tend to lose
interest in farming. Older people also appear to
have lost some of the enthusiasm to farm, either
due to increasing age or due to the opportunity
now to be able to rely financially on their relatives
working in the urban areas. Whereas previously,
young people would help their older relatives
with cultivation of their fields, now they are more
likely to be gainfully employed in urban areas and
unable to assist their relatives in cultivation of the
land. In 2008 the government introduced a new
scheme, ISPAAD (Integrated Support Programme
for Arable Agricultural Development), to support
the traditional sector, in a bid to reverse the decline
in crop production.
The result of declining cultivation of field crops
is a decline in the availability of suitable habitat
for Short-clawed Larks. As less land is cultivated,
fields are encroached by bushes, rendering them
unsuitable. It is unclear how long it takes for a
fallow field to become bush encroached, but it
is likely to be more rapid in years of high rainfall
than in dry years and when there is no grazing by
livestock. 1 hough there are no supporting data, it
seems possible that it can take ten years or more
for a fallow field to be encroached by Acacia to
the extent that it becomes unsuitable for Short-
clawed Lark. For several years, when bushes are
coppicing, the land can still be suitable.
The other main threat to Short-clawed Larks
is likely to be the expansion of settlements,
particularly the city of Gaborone and the villages
nearby. While currently Gaborone is situated
on land that in recent years has never provided
suitable habitat for Short-clawed Larks, the rapid
expansion of the city and of nearby villages, such
as Mogoditshane, Mmopane and Metsimotlhaba,
is taking place where Short-clawed Larks occur at
relatively high density. Inevitably there will be a
localised decline in the numbers of Short-clawed
Larks, particularly to the north of Gaborone.
The expansion of settlements is also taking place
elsewhere in south-east Botswana, albeit to not
such a great extent. It is possible, too, that the
large numbers of small stock discourage farmers to
cultivate fields close to the settlements due to the
high risk of goats destroying their crops. Therefore
bush encroachment of fields is likely to be greater
close to settlements than elsewhere. This was
noted particularly around Kopong, Mmankgodi
and Lorwana.
The current favourable status of Short-clawed
Lark in south-east Botswana is in sharp contrast
with that in the adjacent parts of its range in
South Africa, where the species has experienced
an apparent range contraction and a possible
decline in numbers (Engelbrecht et al. 2007). The
factors that Engelbrecht et al. (2007) consider
to be inimical to Short-clawed Lark in South
Africa include commercial agriculture, cultivation
of pasture grass, insufficient grazing pressure
resulting in excessively lush vegetation, bush
encroachment in areas with traditional agricultural
practices and, lastly, development. In contrast to
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Bull ABC Vol 17 No 1 (2010) -41
its status on agricultural land there, where very few
birds were found, it was common in the Botsolano
Game Reserve, a protected area in Botswana close
to the South African border, near Pitsane, where
commercial agriculture, cultivation of pasture
grasses and insufficient grazing pressure do not
occur, or only marginally so. Bush encroachment
and development have, as yet, only a localised
effect on numbers in south-eastern Botswana.
In conclusion, Short-clawed Lark is currently
still doing well in south-eastern Botswana. Results
suggest that numbers have shown a small increase
since an earlier survey was undertaken in 1992-
93. Its conservation status is favourable, and, due
to a possible decline in numbers in South Africa
(Engelbrecht et al. 2007), its population probably
constitutes an increasingly large proportion of the
world population of this species. However, the
continued decline in the cultivation of field crops
using traditional practices presents a potential
threat. The most beneficial support for the
species would appear to be an incentive, by the
government of Botswana, to farmers to cultivate
sorghum and maize using traditional practices.
This would not only support the Short-clawed
Lark but also improve farmers’ livelihoods and
Botswana’s food security.
Acknowledgements
We thank BirdLife Botswana for providing a
Garrnin GPS, logistical support and much positive
encouragement, the African Bird Club Conservation
Fund and the Royal Society for Protection of Birds
for providing financial support, Stephanie and Lindsay
Tyler for assisting with fieldwork, the Department of
Surveys and Mapping in Gaborone for compiling maps,
the Ministry of Agriculture of Botswana for providing
agricultural data, the Department of Meteorological
Services in Gaborone for providing rainfall data, and
Stephanie Tyler and Derek Engelbrecht for commenting
on this report.
References
Campbell, A & Main, M. 2003. Guide to Greater
Gaborone. Gaborone: The Botswana Society,
Engelbrecht, D. 2005. Breeding biology of the eastern
population of the Short-clawed Lark in South
Africa. Ostrich 76: 1 54-1 61.
Engelbrecht, D., Grosel, J. & Dippenaar, S. 2007.
The western population of Short-clawed Lark
Certhilauda chuana in South Africa revisited. Bull.
ABC 14: 58-61.
Herremans, M. 1997. Shortclawed Lark Certhilauda
chuana. In Harrison, J. A., Allan, D. G., Underhill,
L. G., Herremans, M., Tree, A. J., Parker, V. &
Brown, C. J. (eds.) The Atlas of Southern African
Birds. Johannesburg: Birdlife South Africa.
Herremans, M. 2005. Shortclawed Lark Certhilauda
chuana. In Hockey, P. A. R., Dean, W. R. J. &
Ryan, P. G. (eds.) Roberts' Birds of Southern Africa.
Seventh edn. Cape Town: The Trustees of the John
Voelcker Bird Book Fund.
Herremans, M. & Herremans, D. 1992. Breeding of
the Shortclawed Lark Mirafra chuana in Botswana.
Babbler 23: 6-17.
Ministry of Agriculture. 1990. Soil Map of the Republic
of Botswana. Gaborone: Ministry of Agriculture.
“PO Box 26292, Gaborone, Botswana. E-mail: cbrewster@
botsnet. bw
h BirdLife Botswana, Private Bag 003, Suite 348,
Mogoditshane, Botswana. E-mail: keddii@webmail.
co.za
Mead of Research, Natuurpunt (BirdLife partner,
Flanders), Coxiestraat 1 1 , B-2800, Mechelen, Belgium.
E-mail: marc.herremans@natuurpunt. be
Received 20 January 2009; revision accepted 5 October
2009.
Appendix 1 . Gazetteer of localities
Annexe 1 . Liste des localites citees
Boatle
24°50'S 25°49’E
Mmopane
24°44’S 25°52’E
Borobodilepe
25°37’S 25°29’E
Mochudi
24°23’S 26°08’E
Borotsi
24°57'S 25°43’E
Modipane
24°37’S 26°07’E
Bokaa
24°26'S 26°01’E
Mogobane
24°58’S 25°42’E
Botlhapatlou
24°02'S 25°30'E
Mogoditshane
24°37’S 25°52’E
Dipotsana
25°14'S 25°25’E
Mogonye
24°49’S 25°42’E
Gaborone
24°40'S 25°55’E
Molepolole
24°24'S 25°31’E
Gamoswane
25°07'S 25°29'E
Mosopa
24°47’S 25°25’E
Gasese
24°31’S 25°03'E
Ntlantlhe
24°58'S 25°35’E
Good Hope
25°28’S 25°26'E
Olifant's Drift
24 0 11’S 26°51'E
Hatsalatladi'
24°08'S 25°35'E
Oodi
24°34’S 26°02’E
Hebron
25°40’S 25°24'E
Pelotshetlha
25°12’S 25°22'E
Kanye
24°58’S 25°20'E
Pilane
24°24’S 26°05’E
Kopong
24°28’S 25°54'E
Pitsane
25°28’S 25°36’E
Kubung
24°37'S 25°20'E
Phitshane Molopo
25°45’S 25°13'E
Lephephe
23°21’S 25°51'E
Pitseng
24°41'S 25°02'E
Leporung
25°46’S 24°58'E
Rakhuna
25°34'S 25°34'E
Letlhakeng
24°06'S,25°02'E
Ralekgetho
24°41'S 25°11’E
Lentsweletau
24°15’S 25°51'E
Ramotswa
24°52'S 25°53'E
Lobatse
25°13'S 25°40’E
Ranaka
24°55'S 25°28'E
Lorwana
25°19'S 25°32’E
Rasesa
24°22’S 26°05’E
Losilokgokong
24°33’S 25°22'E
Sesung
24°53’S 25°00’E
Mabalane
24°38’S 26°22'E
Shoshong
23°02'S 26°30'E
Makgomane
25°33'S 25°14'E
Sikwane
24°38’S 26°24’E
Metlobo
25°26'S 24°58’E
Sojwe
23°26'S 25°45’E
Metlojane
25°32'S 25°22’E
Thamaga
24°40’S 25°32’E
Mmamashia
24°32'S 26°00'E
Tlharaseleele
25°29'S 25°37’E
Mmankgodi
24°44'S 25°39'E
Tlokweng
24°40’S 25°57’E
Mmathethe
25°19’S 25°16’E
Tswaaneng
25°31’S 24°59’E
42 -Bull ABC Vol 17 No 1 (2010)
Status of Short-clawed Lark in south-eastern Botswana: Brewster et al.
Cataloguing the Lubango Bird Skin Collection: towards an
atlas of Angolan bird distributions
Michael S. L. Mills' 1 ', Ursula Frank?, Grant Joseph', Francisco Miato' 1 , Suzanne Milton 1 ’,
Ara Monadjerri, Dieter OschadleuJ and W. Richard J. Dean b
Cataloguer la collection de peaux d oiseaux de Lubango : vers un atlas des repartitions des oiseaux
angolais. La collection de peaux d oiseaux logee a Lubango, Angola, comprend plus de 40.000 specimens,
lepiesentant plus de 850 taxons. En juin 2008, nous avons travaille sur la collection pendant deux semaines,
a de collecter des donnees concernant la distribution des especes. Ces travaux font partie d un projet atlas
pour les oiseaux de 1 Angola. La collection est toujours en bon etat et le «Instituto Superior da Ciencias e
Educaqao)) (ISCED), qui abrite la collection, doit en etre felicite. Les donnees mentionnees sur les etiquettes
de 1 5.000 peaux, dont celles de tous les specimens des especes moins connues, ont ete saisies dans une base
de donnees informatisee. Les 25.000 enregistrements restants sont faits sur la base de photos des «fiches de
catalogue». Les specimens les plus interessants sont ceux de quatre Aigrettes vineuses Egretta vinaceigula — les
premieres donnees pour 1 Angola de cette espece cataloguee mondialement «Vulnerable». D’autres exemples
de peaux interessantes sont illustres par des photos et attirent l’attention sur l’importance de la collection
pour des etudes systematiques. La collection de mammiferes est aussi mentionnee brievement. Enfin, des
recommandations sont faites pour la gestion future de la collection.
Summary. The bird collection housed in Lubango, Angola, contains more than 40,000 skins, representing
more than 850 taxa. As part of an atlas project for Angolan birds, we visited rhe skin collection for two
weeks in June 2008, to extract distributional information from the specimens. The skin collection is still in
good condition, and the Instituto Superior da Ciencias e Educa^ao (ISCED), which houses the collection,
is to be commended for this. Data from labels of 15,000 skins were entered into an electronic database,
including all specimens of lesser known species. The remaining 25,000 entries are being made from
photographs of ‘catalogue’ cards. The most interesting specimens are four Slaty Egrets Egretta vinaceigula,
the first records of this globally Vulnerable species in Angola. Other examples of interesting skins are
illustrated in various photographs, drawing attention to the importance of the collection for systematic
studies. A brief mention is also made of the mammal collection. Finally, a list of recommendations is given
for the future management of the collection.
W ith the sixth-longest bird list of any African
country, Angola harbours an exceptionally
rich biodiversity. Add to this one of Africa’s highest
bird conservation priorities — the Western Angola
Endemic Bird Area (Stattersfield et al. 1998) and
its biologically important scarp forests — and the
biological importance of the country becomes
unquestionable. During the 1960s and 1970s the
country’s biodiversity was investigated, plant and
animal collections established, and several reserves
were appropriately managed (Huntley 1974),
but 30 years of civil unrest have left conservation
and research in Angola well behind that of other
southern African countries. Basic information on
species distributions is poor, and the network of
reserves is dysfunctional.
Recent peace and stability have provided new
opportunities for improving the situation. As a
first step, old reserves need to be re-established,
knowledge of species distributions updated and
Figure 1. The team working on the skin collection,
entering details from bird labels into a database
(Michael Mills)
L’equipe travaillant sur la collection de peaux, saisissant
par ordinateur les donnees mentionnees sur les etiquettes
(Michael Mills)
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010) -43
refined, key gaps in the conservation network
identified and remedied, and links built with
Angolan counterparts. Whilst available data
on Angolan bird distributions were recently
summarised (Dean 2000), the contents of the
largest collection of Angolan bird skins, referred
to here as the Lubango Bird Skin Collection
(LBSC), were largely unknown. Summaries based
on some information contained in the LBSC were
published by Pinto (1970, 1972, 1973, 1983),
but the collection of more than 40,000 specimens
must be considered the largest untapped source of
information on Angola bird distributions, and a
primary source for systematic research. A sizeable
collection of mammal skins and skulls is also
housed here.
The aim of our visit to Lubango was four-
fold: (1) to report on the condition ol the
LBSC and make recommendations for its future
management, (2) to garner valuable distributional
information from the LBSC on birds (and to
a lesser degree bats), (3) to draw attention to
the value of the collection for study purposes,
and (4) to build links for future research and
capacity building in Angola, centred on the
collection. Here we report on the condition of
the LBSC and make recommendations for its
future management and use, draw attention to
the importance ol the collection by highlighting
its contents, and provide a progress report on
the cataloguing of the skin collection. Links with
Angolan counterparts are being developed on
several fronts, most notably through the work of
Brian Huntley and colleagues of the South African
National Biodiversity Institute (SANBI), but are
not reported on here.
Short history of the skin collection and
collecting in Angola
The LBSC is one of the largest collections of bird
specimens in south-central Africa and contains
many well-prepared specimens, comparable in
quality to any collection in Africa. The collection
is a tribute to the late Dr Antonio da Rosa Pinto,
who, in 1958, began the nucleus of the collection
by leading a collecting trip to Moxico Province,
in the east of the country. At the time, Dr Pinto
was a teacher at Salazar High School in Lourenqo
Marques (now Maputo) in Mozambique, and
was in Angola on an official ‘temporary’ mission
with the objective of establishing an Ornithology
Department at the Instituto de Investigaqao
Cientifica de Angola (IICA). In 1963 Dr Pinto
was appointed leader of the Centre for Studies at
the IICA in Lubango. He subsequently managed
to gather a very competent group of collectors
and taxidermists, most of them Angolans, familiar
with the birds and the countryside. This group,
usually a team of six men but involving over 60
different personnel over the years, served the IICA
well by establishing a collection of over 40,000
specimens, representing almost all of the avian
taxa known to occur in Angola. The collection is
currently housed at the the Instituto Superior da
Ciencias e Educaqao (ISCED), whose staff is to
be commended for maintaining the collection in
excellent condition.
Although the collection at Lubango contains
very little ‘old’ material, there is a long history of
collecting natural history specimens in Angola.
Bird collections had commenced by the 1850s,
with visits by Dr Francisco Welwitsch, a botanist
who collected some birds between 1853 and 1860,
and Joaquim Monteiro, a mining engineer who
collected birds in 1858-67. Collecting activity at
about this time was stimulated by requests for bird
specimens from Prof. J. V. du Bocage in Portugal,
who requested that military and administrative
officers in Angola collect birds for him. Also, in
1864, Jose Alberto D’Oliviera Anchieta went to
Angola to collect birds for Prof. Bocage. His first
collection, said to be ‘rich’, was lost in a shipwreck
(Pinto 1983). Anchieta returned to Angola in
1 866, and remained in the country until his death
in 1897. He worked mostly in central and western
Angola, collecting almost 4,400 specimens of 460
species of birds, of which 46 were new species to
science.
A number of collectors of many different
nationalities followed Anchieta in the late 1800s;
O. Sala (Dutch), C. J. Andersson (Dean et al.
2006; Swedish), A. W. Eriksson (Swedish), C.
Hamilton (British), J. Falkenstein (German), L.
Petit and A. Lucan (French), O. Schiitt and F.
W. von Mechow (Steinheimer & Dean 2007;
German), P. J. van der Kellen (Dutch) and
the Valdivia Expedition. Many of these are
remembered in the names of Angolan birds.
With interest growing in the natural history
ol Angola, expeditions sponsored by museums
began to visit the country in the early 1900s: the
French mission of Rohan-Cabot (Menegaux &
44 -Bull ABC Vol 17 No 1 (2010)
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Berlioz 1923), the Swiss scientific expedition to
Angola in 1928-29 (Monard 1934), the Phipps-
Biadley expedition (with Rudyerd Boulton as
collector), the Vernay-Angola expedition and
collecting trips by Hubert Lynes and Jack Vincent
(Lynes & Sclater 1933, 1934), and the Pulitzer-
Angola expedition, again with Rudyerd Boulton
as collector. Boulton subsequently collected
and described a new endemic species, Pulitzer’s
Longbill Macrosphenus pulitzeri (Boulton 1931).
In 1929-30, the Gray African Expedition of
the Academy of Natural Sciences, Philadelphia,
collected birds and mammals in central-western
Angola (Bowen 1931, 1932), and an Italian
expedition in 1930 collected the holotype of
an endemic subspecies of Liihder’s Bushshrike
Laniarius luehderi amboinensis (Moltoni 1932).
Individuals, some sponsored by museums and
owners of private collections, were also active
in Angola during the early 1900s. Dr William
Ansorge made several trips to Angola between
1903 and 1909, collecting r.8,000 bird specimens
(and many previously undescribed freshwater
fish). The Portuguese naturalist Francisco Newton
visited Angola at about the same time (de Seabra
1903), C. H. Pemberton collected in 1901-02
and Willoughby Lowe collected some material
in the Luanda area in 1910-11 (Bannerman
1912). Important collections in the 1930s were
made by Jean Bodaly who collected birds at
Chitau, Bie, and by H. K. Prior at Dondi,
Huambo. During a similar period, Rudolf Braun,
who was resident in Angola, collected some
material, most of which is now in the Zoological
Museum in Berlin. The last collections of birds
in Angola before the Ornithology Department
of the IICA was established were made by H. A.
Beatty, who collected for the Field Museum in
Chicago. In two separate major collecting trips
in 1954-55 and 1957, Gerd Heinrich collected
birds for the Zoologisches Institut, Hamburg,
the Field Museum and the Peabody Museum
at Yale University. The Transvaal Museum and
the British Museum sponsored expeditions in
the 1950s, and both expeditions obtained very
useful study material. With the exception of some
birds donated to the IICA by Heinrich and the
British Museum, most of the specimens collected
between 1850 and 1960 in Angola are scattered in
museums in Europe, the UK and North America.
However, many of the specimens collected in
Angola and sent to Portugal in the late 1800s
and early 1900s were destroyed in a fire at the
University of Lisbon in 1978 (Mearns & Mearns
1998), and many other specimens have not been
traced. Fortunately the bird collection at Lubango
remains intact and is an extremely important
source of reference material for ongoing research
on the birds of Angola.
Methods
For two weeks in June 2008 the authors worked
at the LBSC. Bird specimens were removed
from drawers and information displayed on their
labels transcribed into an electronic database
on laptop computers (Fig. 1). The following
information was captured for each specimen:
specimen number, species name, subspecies, sex,
age, weight, collection date and locality, and
collector’s name. In addition, photographs were
taken of many skins, including representatives
of all of the rarer specimens. Lesser known
species were generally processed first. During the
available time, data from 15,000 specimens were
captured into the database, covering all of the
rarer species. Handwriting on the labels was often
hard to read, requiring substantial cleaning of the
database, to correct names of collection localities
and collectors. This work is ongoing.
In addition toentering data from labels, specimen
‘catalogue’ cards (cf Fig. 2) were photographed for
the entire collection. Each card represents a single
species and subspecies, and contains the following
information on specimens belonging to the taxon:
INSTfTUTO DE INVESTIGA^AO CIENTIFICA DE ANGOLA
S*cc*o d* Ornilologi*
ESPECIE Franco 1 i_nus . JJr-: t
|28b 0 ^/^ ^ q
12861 '• a
[ 320 1 yy q
W FT? ' , V
I
ls»*
~ , ) ( V ' ' p* 'r -’v. M?' .V, ,j 0"
235 G
6- ?. J&i, f £ o'
O 65 2.V VyxSjt',, g
Figure 2. An example of the bird ‘catalogue’ cards, for
Grey-striped Francolin Francolinus griseostriatus, giving
the specimen number, date and location of collection,
and sex (Michael Mills)
Un exemple d une «fiche de catalogue», pour le
Francolin a bandes grises Francolinus griseostriatus, avec
le numero du specimen, date et localite de collection, et
sexe (Michael Mills)
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010)- 45
46 -Bull ABC Vol 17 No 1 (2010)
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Legend to figures on opposite page
Figure 3. i wo of the four specimens of Slaty Egret
Egretta vinaceigula in the collection: (a) adult, (b)
immature. 1 hese are the first published records of the
species in Angola (Michael Mills)
Deux des quatre specimens de l’Aigrette vineuse Egretta
vinaceigula de le collection : (a) adulte, (b) immature. II
s’agit des premieres donnees publiees de l’espece pour
1’ Angola (Michael Mills)
Figure 4. A comparison of Black-chinned Quailfinch
Ortygospiza gabonensis (top) and African Quailfinch O.
fiiscocrissa (bottom), from Angola. The latter species has
a white chin and spectacles, but overall the species are
very similar and may belong to a single species (Payne &
Sorenson 2007). Skins from the Lubango museum come
from a contact zone of the two taxa and could be used
as part of a detailed phylogenetic study using multiple
representatives from each quailfinch form, required to
properly test whether the three detected genetic lineages
exhibit consistent plumage differences (Fry & Keith
2004, Payne & Sorenson 2007) (Michael Mills)
Une comparaison entre l’Astrild-caille a face noire
Ortygospiza gabonensis (en haut) et l’Astrild-caille a
lunettes O. fiiscocrissa (en bas) de 1’Angola. La derniere
espece a le menton blanc et des lunettes blanches, mais
pour le reste les deux especes sont tres semblables et
pourraient comprendre une seule espece (Payne &
Sorenson 2007). Les specimens du musee de Lubango
proviennent d une zone de contact des deux taxons et
pourraient servir pour une etude phylogenetique detaillee.
Une telle etude devrait utiliser plusieurs representants de
chaque forme d’astrild-caille pour pouvoir examiner si
les trois lignees detectees ont des differences de plumage
consistantes (Fry & Keith 2004, Payne & Sorenson
2007) (Michael Mills)
Figure 5. Male (top) and female (bottom) specimens of
Black-chinned Weaver Ploceus nigrimentus , collected in
Huambo town (previously Nova Lisboa) in March 1966
probably the most recent ot this rare species in Angola.
Only two other specimens are listed in Dean (2000), with
the only other localities being Galanga (the type locality)
and Mombolo (Michael Mills)
Specimens male (en haut) et femelle (en bas) du Tisserin
a menton noir Ploceus nigrimentus, collectes a Huambo
(auparavant Nova Lisboa) en mars 1966 probablement
les mentions les plus recentes de cette espece rare en
Angola. Seulement deux autres specimens, de Galanga
(la localite type) et Mombolo, sont mentionnes par
Dean (2000) (Michael Mills)
Figure 6. An example ol the striking endemic male
Golden-backed Bishop Euplectes aureus in breeding
plumage (top), alongside Yellow Bishop E. capensis
(bottom). A population of Golden-backed Bishop on Sao
Tome is believed to have been introduced (Fry & Keith
2004) (Michael Mills)
Un exemple du remarquable male en plumage nuptial
de l’endemique Euplecte dore Euplectes aureus (en
haut), a cote de I’Euplecte a croupion jaune E. capensis
(en bas). La population de l’Euplecte dore a Sao Tome
est supposee avoir ete introduite (Fry &c Keith 2004)
(Michael Mills)
Figure 7. The near-endemic Bocage’s Sunbird Nectarinia
bocagii (second, fourth and sixth) alongside the
distinctive, endemic gadowi subspecies of Bronzy Sunbird
N. kilimensis. Bocage’s Sunbird is dark purple and black,
whereas Bronzy Sunbird is greenish bronze and has a
longer, more curved bill (Michael Mills)
Le quasi endemique Souimanga de Bocage Nectarinia
bocagii (deuxieme, quatrieme et sixieme specimens)
a cote de la sous-espece endemique distincte gadowi
du Souimanga bronze N. kilimensis. Le Souimanga de
Bocage est violet fonce et noir, tandis que le Souimanga
bronze est bronze verdatre et a un bee plus long et plus
arque (Michael Mills)
Figure 8. The very similar Bates’s Sunbird Cinnyris
batesi (top) and Little Green Sunbird Anthreptes seimundi
(bottom). The latter is overall brighter green, with a
shorter, straighter bill; Bates’s Sunbird is greyer below,
and has a black tail, which is hard to see in the field
(Michael Mills)
Les tres semblables Souimanga de Bates Cinnyris batesi
(en haut) et Souimanga de Seimund Anthreptes seimundi
(en bas). Ce dernier a le plumage vert plus vif, avec un
bee plus court et plus droit ; le Souimanga de Bates est
plus gris dessous et a une queue noire, ce qui est difficile
a voir sur le terrain (Michael Mills)
specimen number, collection date and locality, and
sex for each example in the collection. Photographs
of these cards (4,661 in total, representing 859
species) have now been labelled and ordered
by family. Data entry is continuing using these
photographs, but is expected to take at least
another 18 months to complete.
A small amount of time was dedicated to
comparing specimens of similar species, and taking
side-by-side photographs, as well as inspecting the
mammal collection.
Findings
Broadly, the collection remains in excellent
condition, free of insect damage. Specimens are
housed in wooden drawers lined using paper,
in 28 large wooden cupboards. All specimens
are labelled and the complete collection of field
journals remains with the skins. However, the
room in which the collection is kept is incredibly
dusty, the field journals are unordered and poorly
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010) - 47
Table 1 . Details of the four specimens of Slaty Egret Egretta vinaceigula in the Lubango Bird Skin Collection.
Tableau 1 . Donnees sur quatre specimens de I’Aigrette vineuse Egretta vinaceigula loges dans la collection
de peaux d'oiseaux de Lubango.
Specimen details
Collection details
No.
Sex
Age
Mass (g)
Locality
Date
Collector
23532
F
Imm.
300
Rio Cunene (Quiteve)
27 June 68
A. R. Pereira
23257
F
Ad.
245
Luamucua (Quiteve)
19 June 68
D. Mumputu
23259
F
Ad.
175
Luamucua (Quiteve)
19 June 68
A. R. Pereira
23432
F
Imm.
300
Rio Cunene (Quiteve)
24 June 68
D. Mumputu
kept, and a large number of mounted specimens
are clumsily arranged, making for poor working
conditions. Although the collection has been kept
in good condition by Prof. Jose Luis Alexandre
and his staff at ISCED, there is no official curator
or ornithologist at the collection. The current
‘caretaker’ of the collection has no training in
biology or taxidermy, and the collection remains
largely unused. There is not yet an official
protocol for access, although permission to work
on the collection can be granted by the Dean
of ISCED, Prof. Matondo Tomalela. Francisco
Miata is employed and trained to maintain and
care for the herbarium collection housed here,
and a counterpart in the bird collection is urgently
needed.
The LBSC is significant for both the number of
specimens it contains (>40,000) and the great variety
of taxa presented (>850), including numerous rarer
species. More than 1,600 photographs of skins
were taken, representing >400 species, and have
been databased. The most interesting discovery
was the presence of four specimens of Slaty Egret
Egretta vinaceigula , erroneously labelled as Black
Herons E. ardesiaca (Fig. 3). These specimens
(Table 1; Fig. 1) were all collected during a trip
to Quiteve, Huila Province, on the banks of
the Cunene River (16°02’S 15°lTE), on 19-27
June 1968, and constitute the first records of this
Vulnerable species for Angola (Dean 2000).
Some other specimens of interest are
summarised in Table 2 and species and species
comparisons are illustrated in Figs. 4-12.
DO worked exclusively on the Ploceidae. Most
Angolan Ploceidae are represented in the collection,
notable exceptions being Orange Weaver Ploceus
aurantius and Slender-billed P. pelzelni. Pinto
(1972) listed a specimen of P. pelzelni collected
in Cabinda that should have been present in
the museum and is listed on the ‘catalogue’
cards, but it was not found. While the collection
generally contains few types, it does house the type
series of the subspecies of Scaly-fronted Weaver
Sporopipes squamifrons pallidus described by Pinto
(1967). Several rare or uncommon weavers are
represented: Black-chinned Weaver P. nigrimentus
(2), Loango Weaver P. subpersonatus (2), Brown-
capped Weaver P. insignis (5), Black Bishop
Euplectes gierowii (1 from Tanzania) and Golden-
backed Bishop E. aureus (47). Three specimens
of Southern Masked Weaver Ploceus velatus were
collected by Pinto from the isolated Lake Dilolo
during August 1958 (Pinto 1965, Dean 1996),
with further specimens from this expedition
housed at the Lisbon Museum (Louette 1984).
It has been suggested that these birds belong
to the reichardi-ruweti species complex (Dean
2000). The LBSC specimens are dull-plumaged,
but one is a male starting to moult: there are a
few orange feathers on the upper throat. Other
than this orange plumage anomaly (the throat
should be turning black), the weavers appear to
match nominate Southern Masked Weaver found
further south in Angola. The nearest locality for
Southern Masked Weaver is in north-west Zambia
(Dowsett et al. 2008).
Mammals
The mammal collection at Lubango consists
of skins and skulls of a variety of species. The
aim of this expedition was to catalogue the bird
collection, thus there was only limited time for AM
to examine the mammals, which numbered more
than 3,000 specimens of at least 123 species. The
bats were examined in greatest detail and included
211 specimens of 23 species. This represents
about one third of the 63 species known to occur
in Angola. With respect to collecting sites, there is
a geographical bias towards the south-east of the
country, which is unsurprising since that is where
Cataloguing the Lubango Bird Skin Collection: Mills et al.
48 -Bull ABC Vo! 17 No 1 (2010)
Table 2. Summary of some of the more interesting specimens contained in the Lubango Bird Skin Collection, with the
number of specimens for each species (No.).
Tableau 2. Apergu d un nombre de specimens interessants dans la collection de peaux d’oiseaux de Lubango, avec
I indication du nombre de specimens pour chaque espece (No.).
Common Name Scientific Name
Rufous-chested Sparrowhawk Accipiter rufiventris
Swierstra’s Francolin Francolinus swierstrai
Grey-striped Francolin Francolinus griseostriatus
White-throated Francolin Francolinus albogularis
Horus Swift Apus horus
Bradfield's Hornbill Tockus bradfieldi
White-headed Barbet Lybius leucocephalus
Benguela Long-billed Lark Cedhilauda benguelensis
Grimwood’s Longclaw Macronyx g rimwoodi
Angola Cave Chat Xenocopsychus ansorgei
Black-necked Eremomela Eremomela atricollis
Congo Moor Chat M yrmecocichla tholloni
Gabela Akalat Sheppardia g abela
Pulitzer's Longbill Macrosphenus pulitzeri
Laura's Woodland Warbler Phylloscopus laurae
Rock-loving Cisticola Cisticola aberrans
Angola Slaty Flycatcher Melaenornis brunneus
Margaret’s Batis Batis margaritae
White-fronted Wattle-eye Platysteira albifrons
Bare-cheeked Babbler Turdoides gymnogenys
Black-faced Babbler Turdoides melanops
Rockrunner Chaetops pycnopygius
Bannerman's Sunbird Cyanomitra bannermani
Bocage’s Sunbird Nectarinia bocagii
Ludwig’s Double-collared Sunbird Cinnyris ludovicensis
Oustalet’s Sunbird Cinnyris oustaleti
Gabela Helmetshrike Prionops gabela
Chestnut-backed Sparrow Weaver Plocepasser rufoscapulatus
Bar-winged Weaver Ploceus angolensis
: Black-chinned Weaver Ploceus nigrimentus
. Golden-backed Bishop Euplectes aureus
Dusky Twinspot Euschistospiza cinereovinacea
No. Notes
3 Rare in Angola
6 Vulnerable endemic
12 Near-Threatened endemic
6 Rare in Angola
12 Form toulsoni, often treated specifically as Loanda Swift
16 Scarce species
37 Endemic and distinctive ssp. leucogaster
55 Near-endemic
38 Data Deficient
31 Endemic
65 Localised species
29 Near-endemic
7 Endangered endemic
4 Endangered endemic
1 Endemic ssp. laurae ; rare in Angola
6 Endemic ssp. bailunduensis
32 Endemic
1 Rare in Angola; endemic ssp. margaritae
4 Near-Threatened near-endemic
15 Near-endemic
21 Near-endemic
22 Near-endemic
13 Near-endemic
11 Near-endemic
76 Endemic
31 Localised species
3 Endangered endemic
82 Near-endemic
11 Near-endemic
2 Near-endemic
47 Endemic
29 Endemic ssp. cinereovinacea
Lubango is situated. The collection includes a
number of interesting bat specimens such as two
D’Anchieta’s Fruit Bat Plerotes anchietae, a species
known from just 11 specimens (Bergmans 1989,
Kock et al. 1998); 21 specimens of Angolan
Epauletted Fruit Bat Epomophorus angolensis, an
Angolan near-endemic; and African Sheath-tailed
Bat Coleura afra, a widespread species but in
southern Africa known from just three specimens
(Monadjem et al. in press). Non-chiropteran
mammals well represented in the collection
include genets ( Genetta ), hares ( Lepus ), hyraxes
(dassies) ( Heterohyrax and Procavia ) and at least
33 genera of rodents. Primates are particularly
poorly represented with skins of just six species.
Habitats: erosion of biodiversity in the
environs of Lubango
The habitats in which birds were collected
between 1958 and 1974 ranged from coastal desert
through palm and baobab savanna on lowland
alluvium along the Cunene River, to grassland
and sclerophyllous shrubland on the sandstones
of the high-altitude tableland that surrounds
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010) -49
Lubango, to escarpment forest along the ‘Scarp’
and equatorial gallery forest along various rivers.
Travelling from northern Namibia to Lubango
we passed successively through palm savanna and
mopaneveld, baobab savanna, Baikiaea (teak)
woodland on yellow sand, mixed woodland
with Combretum , Terminalia, Commiphora and
Albizia set among spectacular granite hills, and
then, at higher altitudes on red sands, miombo
woodland. The sandstone plateau above the town
of Lubango supports stunted miombo and a high
diversity of shrubs including Protea welwitschi and
grass trees Xeris sp. Closed Afromontane forest
patches occurred in deep, well-watered gorges on
the escarpment. When the bird collection was
constituted, in 1958-74, the human population of
Angola was sparse and most of the woodland in the
southern part of Angola was intact. Tall woodland
that included large specimens ol such hardwoods
as Pterocarpus angolensis (kiaat), Combretum (bush
willow) and Baikiaea plurijuga (teak) extended
from the Namibian border to Lubango.
Human population growth over the past four
decades has changed the face(s) of the landscape.
Within a 50-km radius of Lubango miombo
woodlands have been cleared and replaced with
subsistence agriculture based on grain crops, goats
and cattle, with charcoal made from large miombo
trees as a cash supplement. Further from the city
of Lubango bags of charcoal and honey for sale
at roadside markets are witness to the continued
erosion of the woodland, as trees make way for
more subsistence crops, cut to raid bee hives,
ringbarked for materials used in medicine or to
construct bark hives, and converted to charcoal
50 -Bull ABC Vol 17 No 1 (2010)
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Legend to figures on opposite page
Figure 9. I he endemic Monteiro’s Bushshrike
Malaconotus monteiri (second and fourth) alongside its
closest relative, Grey-headed Bushshrike M. blanchoti,
which differs in lacking the pale ring around the eye, in
having a yellowish, not greyish eye, and a less robust bill.
Monteiro s Bushshrike is supposedly less orange below
(Fry & Keith 2000, Sinclair & Ryan 2003), but these
two specimens contradict this (Michael Mills)
L endemique Gladiateur de Monteiro Malaconotus
monteiri (deuxieme et quatrieme specimens) a cote de
son parent le plus proche, le Gladiateur de Blanchot
M. blanchoti , qui differe par l’absence du cercle oculaire
pale et par son oeil jaunatre, non pas grisatre, et son
bee moins fort. Le Gladiateur de Monteiro est suppose
etre moins orange dessous (Fry & Keith 2000, Sinclair
& Ryan 2003), mais ceci est contredit par ces deux
specimens (Michael Mills)
Figure 10. Rosy-throated Longclaw Macronyx ameliae
(second and fourth) alongside examples of the Data
Deficient Grimwood’s Longclaw, well represented in the
collection by 38 specimens of two subspecies, grimwoodi
and cuandocubangensis , the latter not mentioned in Keith
et al. (1992) (Michael Mills)
La Sentinelle a gorge rose Macronyx ameliae (deuxieme
et quatrieme specimens) a cote d’exemplaires de la
Sentinelle de Grimwood, espece «Insuffisamment
documente» bien representee dans la collection par
38 specimens de deux sous-especes, grimwoodi et
cuandocubangensis. Cette derniere n’est pas mentionnee
par Keith et al. (1992) (Michael Mills)
Figure 11 . The Endangered, endemic Gabela
Helmetshrike Prionops gabela (first and third) alongside
its closest relative, the widespread Retz’s Helmetshrike P.
retzii, illustrating the latter species’ larger size and darker
plumage (Michael Mills)
Le Bagadais de Gabela Prionops gabela (premier et
troisieme specimens), espece endemique «Menacee
d’extinction», et son parent le plus proche a large
distribution, le Bagadais de Retz P. retzii, illustrant la
taille plus grande et le plumage plus fonce de ce dernier
(Michael Mills)
Figure 12. Two subspecies of Meves’s Starling
Lamprotornis mevesii found in Angola; the more glossy
mevesii (top and third) alongside the duller benguelensis,
endemic to the southern escarpment zone, that may
deserve specific status (Hall I960). Specimens from the
Lubango Bird Skin Collection could help unravel the
'systematics of this species (Michael Mills)
Deux sous-especes du Choucador de Meves Lamprotornis
mevesii representees en Angola; mevesii, plus brillant (en
haut et troisieme), et benguelensis, endemique de la zone
australe de fescarpement, plus terne. Les deux formes
pourraient etre des especes a part entiere (Hall 1960);
des specimens de la collection de Lubango pourraient
■servir a elucider leur taxonomie (Michael Mills)
for hearing and cooking in the ever-growing
urban centres. Large trees are disappearing in even
quite remote areas such as the slopes above the
precipitous cliffs of the escarpment at Leba. Smoke
rising from the woodland, cut stumps, charcoal
pits, paths made by ox-drawn sleds, and feathers
of wild birds used to sustain the woodcutters bear
silent witness to the ongoing erosion of the natural
capital of this beautiful land.
Towards an atlas
One of the objectives of compiling a catalogue and
database of the bird specimens in the Lubango
collection is to build a georeferenced database of
bird specimen records for Angola. These data will
be merged with another database, containing data
on distributions taken from Traylor (1963), Pinto
(1983), Dean (2000) and Mills & Dean (2007),
data on bird specimens in other collections and sight
records of birds contributed by visitors to Angola.
These data will then be mapped, probably at a 15’
x 1 5’ scale. The maps will provide guidelines for the
recommendation of protected areas and will also
provide some basic distribution patterns, useful for
modelling effects of climate change and potential
environmental disasters (e.g. oil spills from offshore
wells along the northern coast). Gap analyses
using these data will establish priorities for future
ornithological field work in Angola.
Bird atlas studies not only show bird distribution
patterns, but more importantly also identify areas
for which there are no data. Globally, bird atlases
have made a key contribution to conservation,
through highlighting the conservation priorities
of species (providing fundamental data for Red
Data listing) and habitats (e.g. Fishpool & Evans
2001). Angola, emerging from decades of political
instability, is a country where knowledge of bird
distributions is particularly poor, although the
avifauna is diverse. Most surveys and collecting
have been conducted in western and north-central
Angola, and along the coastal areas and parts
of the Mayombe in Cabinda. We do not know
whether gaps in the distribution of certain species
are ’real’ or artefacts of surveys. An atlas will help
close these gaps or show whether they are real.
This has important implications for conservation
in Angola in that attention will then be drawn to
areas of high avian species richness, which might
also prove to be areas of high species richness
amongst other taxa. Identifying focal areas will
Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010) -51
also lead to an evaluation of land use practices in
these areas and an assessment of their impacts; for
example, charcoal burning using native woodland
(miombo species complex) trees.
Recommendations for the collection
Although the collection is being kept in reasonable
condition, conditions can be greatly improved and
the collection should be put to practical use. We
recommend that the following steps be taken:
• Produce an electronic database of the bird
skin collection, which work is in progress,
and once the ciatabase is complete, copies
will be provided to colleagues in Angola and
worldwide, to promote work using the skins.
Data will start to be made available online
via the website of Natural World (www.nat-
world.org) within the next 12 months.
• Training of (a) young Angolan ornithologist(s),
to act as curator for the collection.
• Possible 'adoption’ of the collection by a foreign
museum to assist with training and to improve
the conditions in which skins are kept.
• Cleaning of the entire room in which the skins
are housed.
• Properly organising all documents pertaining
to the collection.
• Cleaning and cataloguing the valuable collec-
tion of books associated with the collection.
• Encouraging collaboration between Angolan
and foreign researchers, using the skin collec-
tion as a point of contact.
• Stimulate interest in Angolan birds by incor-
porating informative visits to the collection
in standard biology courses at the institute
and making use of the specimens for student
projects.
Conclusions
Given the threats to biodiversity in Angola,
it is important that some of the plant and
animal collections from the 1970s remain in the
country to guide and inspire a new generation
of Angolan scientists. With the help of SANBI,
other biodiversity experts in the South African
Development Community and assistance from
outside the region there may still be time to
plan a protected area network for Angola that
will retain all vegetation types and the associated
fauna. Without planning, active protection and
initiatives to provide alternative sources of income
for the local inhabitants, it is unlikely that the next
generation of Angolans will be able to enjoy the
beauty of the country and the biological diversity
experienced by their grandparents, to taste wild
honey, see Giant Sable Hippotragus niger variani
in the wild, or even to simply find sufficient wood
or charcoal for their daily needs.
Acknowledgements
Funding for this research came from the generous
contributions of Ursula Franke, the African Bird Club
Conservation Fund, Tony Dowd and Robert Angiers.
Brian Huntley assisted tremendously with organising
access to the collection, and with logistical support.
Many thanks to Yudo Borges and especially Eduardo &
Tanya Traguedo for their help during our visit, and for
being such hospitable hosts. Prof. Matondo Tomalela,
Dr Fernanda Lages, Prof. Jose Luis Mateus Alexandre
and other staff at ISCED were incredibly supportive of
our work, and this project would have been impossible
without them. Dr Michel Louette, Robert J. Dowsett,
Ron Demey and Guy Kirwan commented on an earlier
version of this paper.
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Cataloguing the Lubango Bird Skin Collection: Mills et al.
Bull ABC Vol 17 No 1 (2010) -53
Bird observations from Sao Tome:
Monte Carmo as a priority conservation site
Fdbio Olmof and Longtong G. Turshak b
Observations d’oiseaux de Sao Tome : Monte Carmo comme site de priorite pour la conservation.
A l’occasion d’inventaires effectues sur l’ile de Sao Tome, dans le Golfe de Guinee, en juillet-aout 2007,
46 especes one ete trouvees, y compris tous les taxons endemiques. L’abondance avienne, basee sur le
taux de rencontre, est plus elevee dans les forets montagnardes que dans les forets a plus basse altitude,
mais ces dernieres abritent plus d’especes. Les zones agricoles supportent une avifaune mixte d’especes
endemiques et introduites. Les especes les plus abondantes dans les deux habitats forestiers sont quatre
especes endemiques : le Souimanga de Newton Anabathmis newtoni, la Prinia de Sao Tome Prinia molleri ,
le Tisserin de Sao Tome Ploceus sanctithomae et le Serin roux Serinus rufrobrunneus. Les forets de basse
altitude de Monte Carmo (Ribeira Peixe) abritent plusieurs Ibis de Bocage Bostrychia bocagei dans une zone
relativement limitee, ainsi que le Neospize de Sao Tome Serinus ( Neospiza ) concolor et la Pie-grieche de Sao
Tome Lanius newtoni. Le Nasique de Bocage Amaurocichla bocagii et la pie-grieche ont aussi ete observes
au dessus de 1.000 m dans la zone d’Ana Chaves. Les forets de Monte Carmo sont considerees comme
une priorite pour des projets de conservation, qui pourraient inclure du tourisme base sur l’observation des
oiseaux, mais leur avenir est incertain a cause des developpements recents dans les plantations d’huile de
pal me avo is in antes.
Summary. Surveys carried out on the Gulf of Guinea island of Sao Tome in July-August 2007 found
46 species, including all of the endemic taxa. Bird abundance was higher in montane forests, based
on encounter rates, than in forests at lower elevations, but the latter held more species. Agricultural
areas supported a mixed avifauna of endemic and introduced species. Numerically dominant species in
both forest habitats were the endemic Newton’s Sunbird Anabathmis newtoni, Sao Tome Prinia Prinia
molleri, Sao Tome Weaver Ploceus sanctithomae and Principe Seedeater Serinus rufrobrunneus. The low-
elevation forests of Monte Carmo (Ribeira Peixe) held several Dwarf Olive Ibises Bostrychia bocagei in a
comparatively small area, as well as Sao Tome Grosbeak Serinus ( Neospiza ) concolor and Sao Tome Fiscal
Lanius newtoni. Sao Tome Short-tail Amaurocichla bocagii and the fiscal were also recorded above 1,000 m
in the Ana Chaves area. The forests of Monte Carmo are considered a priority for conservation projects,
which might include birding-based tourism, but their future is uncertain because of recent developments
in nearby oil-palm plantations.
T he islands of Sao Tome (857 km : ) and
Principe (139 km 2 ) in the Gulf of Guinea
hold at least 17 and eight single-island endemics,
respectively, probably representing the largest
number of endemic birds per land area for any
island group (Melo 2007, Melo & Jones in
press). Several of the endemics are of conservation
concern, mostly due to habitat loss, including the
Vulnerable Sao Tome Short-tail Amaurocichla
bocagii and the Critically Endangered Newton’s
Fiscal Lanius newtoni, Sao Tome Grosbeak Serinus
{Neospiza) concolor and Dwarf Olive Ibis Bostrychia
bocagei (BirdLife International 2008).
These volcanic islands possess a rugged
topography with limited level ground along the
coast and in some valleys. Sao Tome reaches
2,024 m, whilst on Principe the highest elevations
peak at 945 m. Fast-running streams radiate down
the mountains through lush forest and cropland to
the sea on both islands (Christy & Clarke 1998,
Jones & Tye 2006). The islands are covered in
lush montane and low-elevation forest, shade
forests (cocoa and coffee plantations), derelict
plantations ( capoeiras ) and some open savannah
(on Sao Tome).
The islands were first occupied by humans after
their discovery by the Portuguese in the 1470s,
and their economy became dependent on cash
crops, especially cocoa and coffee, both cultivated
under shade trees in large plantations {rogas or
shade forest) (Seibert 2002). The result was that
most forest below 1,000-1,200 m was drastically
modified, if not destroyed; the least disturbed
forest areas at lower elevations are concentrated in
the wettest south-western part of Sao Tome, and
in southern Principe. On the other hand, one of
54 -Bull ABC Vol 17 No 1 (2010)
Bird observations from Sao Tome: Olmos & Turshak
the key habitats on both Sao Tome and Principe
is the shade forest or capoeira resulting from the
abandonment of former plantations of cocoa,
coffee, coconut and oil-palm after independence
in 1975 (Christy & Clarke 1998, Jones & Tye
2006).
Data on the local avifauna appeared only after
the mid- 19th century. Due to the country being
closed to most foreigners until the recent past
(Seibert 2002), updated information on some of
the rarest endemics became available only after
the 1980s (Sargeant 1994, Jones & Tye 2006).
More recent research has addressed the taxonomy
and biogeography of the endemics (Melo 2007,
Melo & Jones in press), compared the densities of
endemic species in different habitats and human
impacts (Dallimer et al. 2009) and the distribution
and basic ecology of the threatened species (ABS
2007, Maia & Alberto 2009).
Sao Tome possesses three Important Birds
Areas (IBAs) that encompass the main habitat
types (lower elevation and montane forests, and
savannahs (Christy 1998). Some sites within the
IBAs have been well explored by ornithologists,
such as the montane forests of Lagoa Amelia and
the nearby capoeiras and agricultural mosaic of
Bom Sucesso (Rocha 2008, Dallimer et al. 2009).
However, areas such as the lower elevation forests
of Monte Carmo, above Ribeira Peixe, although
well known to birders and visited by researchers
(Melo 2007, Leventis & Olmos 2009), lacked
descriptions of their bird communities.
Here we report the findings of a bird survey on
Sao Tome during a fact-finding visit to the islands
sponsored by BirdLife International and the A. P.
Leventis Ornithological Research Institute carried
out between 13 July and 12 August 2007, with
further on visits in January and July-August
2008.
Study sites and Methods
Observations were made along existing paths in
selected localities according to access and bird
species expected to be found. Characterisation of
the different vegetation types follows Jones & Tye
(2006).
Bom Sucesso (00°17’20”N 06°36’45”E; 1,148
m): visited on 19, 23-28 July and 9 August.
The site of the national botanical garden and a
gateway to the trails leading to Pico de Sao Tome,
Lagoa Amelia and other locations in the central
massif. A nearby elevation (Macrambala) is also
accessible by vehicle, with a trail starting along
the ridge overlooking the Nova Ceilao Valley
(walked on 28 July). I he gardens cover a small
area, with both native and introduced trees, and
flowering plants. This area is surrounded by farms
cultivating bananas, plantains, carrots and yams,
with isolated clumps ol trees. Large areas are
occupied by invasive grasses and herbs. This part
of the island is much cooler and more subject to
mist than lower elevations.
Lagoa Amelia (00°16’50”N 06°35’36”E; 1,385
m): visited on 23—24 and 26—27 July. Covering
montane forest inside Parque Natural Obo this
well-known birding spot is accessed via a track
from Bom Sucesso. Within the park’s boundary,
which is already encroached by farmland, the
forest becomes continuous as the track ascends
the mountain. Trees may reach over 30-35 m,
with a heavy cover of moss and epiphytic plants.
Exotic bamboos along the track mark old roads
between now derelict rogas. Lagoa Amelia is an
old volcanic crater, now filled by grassy vegetation
(no standing water during our visit), surrounded
by montane forest.
Monte Carmo (campsite at 00°09’06”N
06°33’60”E; 363 m): visited on 1-4 August.
Situated in the south-west of the island near
Ribeira Peixe, this is a well-known site for the
rarest species on Sao Tome (Leventis & Olmos
2009), and is reached after a rwo-hour walk from
the nearby oil-palm plantation of Emolve. Above
the plantation the vegetation gradually changes
Rom capoeira and shade forest to mature low
forest (with many Symphonia globulifera ) and
the trail follows a fairly gentle slope bordered by
deep valleys. The ground is commonly strewn
with rocks, which probably precluded cultivation.
There are many level areas along the slope and
water collects in some places. Signs of foraging
feral pigs were plentiful. This is one of the wettest
parts of the island and it rained throughout our
stay, despite this being the ‘dry’ season.
Sites in Sao Tome where only qualitative
observations were carried were Ro 9 a Binda
(00°13T0”N 06°27’57”E; 30 m) and Ro ? a Juliana
de Sousa (00 o 12’01”N 06°28’20”E; 214 m), both
visited on 15 July; Roqa Bombaim and Formoso
Grande (campsite at 00°13’5T’N 06°37’42”E;
631 m), visited on 29-30 July; the well-known
trail between Bom Sucesso and Pico de Sao Tome,
Bird observations from Sao Tome: Olmos & Turshak
Bull ABC Vol 17 No 1 (2010) -55
and from there down to Ponta Figo (see Christy
& Clarke 1998), walked on 16-17 July; and the
headwaters of the rio Ana Chaves (00°15’45”N
06°34’23”E, 1,182 m), visited on 9 August.
Birds seen or heard were recorded along
the trails, including species with far-carrying
vocalisations such as orioles and pigeons.
Quantitative data were recorded only when it
was not raining, accounting for the seemingly low
effort at Monte Carmo. Some species were sound-
recorded, the relevant files being available at
Xeno-canto (XC; www.xeno-canto.org/africa). As
a measure of relative abundance we used encounter
rates (Bibby et al. 1998) expressed by the number
of individuals recorded per ten hours (see Table 1
for sampling effort). This index and its variations
give a less subjective idea of the relative abundance
and detectability of birds present in a given area
(Pacheco & Olmos 2003).
We took GPS coordinates of all individual
Dwarf Olive Ibises, Sao Tome Fiscals, Sao Tome
Grosbeaks and Sao Tome Short-tails detected.
As reliable altitude readings could not always be
made due to the dense tree cover we use values
obtained from GoogleEarth throughout this
paper. Nomenclature principally follows Jones &
Tye (2006) with the modifications suggested by
Melo (2007) and Melo & Jones (in press).
Results and Discussion
All endemic birds known on Sao Tome were
recorded (Table 1). Overall, 45 species were
observed, including one seabird nesting in tree
hollows in the forest and one shorebird on the
beach. Twenty-five species were found in the
agricultural mosaic of Bom Sucesso and the
capoeiras between Binda and Juliana de Sousa,
both sharing 16 species, whilst 20 were found in
the shade plantations and capoeiras of Bombaim.
The environs of Sao Tome town harboured 22
species, including most of the introductions,
many of which also occur at Born Sucesso, but
montane and lowland forests support only native
species. None of the introduced birds has, to
date, colonised the latter habitats despite the
long history of European colonisation and trade
with mainland Africa (Seibert 2002, Jones & Tye
2006).
Montane forests at Lagoa Amelia, where survey
effort was greatest, held 1 5 species compared to 20
at the lower elevation Monte Carmo, with 12 of
these shared. Species found only in mature or old
secondary forest included Dwarf Olive Ibis, Sao
Tome Short-tail, Sao Tome Fiscal and Sao Tome
Grosbeak, all found at Monte Carmo.
We found no evidence of any endemic species
breeding during our survey, and only two (Sao
Tome Oriole Oriolus crassirostris and Newton’s
Sunbird Anabatbmis newtoni ) consistently
responded to playback. Sao Tome Prinia Prinia
molleri was commonly seen performing aerial
displays, but these appear to occur year-round
(Christy & Clarke 1998, Jones & Tye 2006).
Only Vitelline Masked Weavers Ploceus velatus
were observed nest building and displaying, but
several Sao Tome Weavers were observed nest
building in the Bom Sucesso area during the July
2008 visit.
A greater richness at Monte Carmo agrees
with the findings of Dallimer et al. (2009),
who compared Lagoa Amelia with another lower
elevation site, rio Sao Miguel, in western Sao
Tome. The main difference between forest types
uncovered by their study and ours was the lack
of endemics such as the ibis, fiscal, grosbeak,
short-tail and Giant Weaver Ploceus giganteus
in montane forest. On the other hand, that the
ibis, fiscal and short-tail do occur in montane
forest some distance from Lagoa Amelia (Rocha
2008; see below) lends credence to the theory that
human activities like hunting and gathering of
forest products result in lower densities of those
species (Dallimer et al. 2009).
The point counts undertaken by Rocha (2008)
found 15 species in montane forest in the Bom
Sucesso / Lagoa Amelia area, although his sampling
in less-disturbed areas further from Lagoa Amelia
resulted in the addition of Dwarf Olive Ibis and
Sao Tome Short- tail. The agricultural mosaic of
Bom Sucesso yielded only 17 species, compared
to 25 in our list, a difference probably the result
of recce walks being a more effective method of
recording uncommon species.
As noted by other observers (Christy & Clarke
1998, Jones & Tye 2006) most endemic birds
utilise shade plantations and agricultural areas
with a mosaic of cultivation, sparse trees and
hedges, which finding has since been corroborated
by more detailed research (Rocha 2008). These
habitats possess abundant introduced plants
providing nectar (the shade tree Erythrina
poeppigiana and the shrub Tithonia diversifolia )
56 -Bull ABC Vol 17 No 1 (2010)
Bird observations from Sao Tome: Olmos & Turshak
and fruit (the trees Cecropia peltata and Musanga
cecropioides plus several cultivated species; the
shrub Cestrum levigatum ) consumed by many
endemics (Leventis & Olmos 2009). Species
such as Principe Seedeater Serinus rufobrunneus ,
Sao Tome Flycatcher Tcrsiphone atrochalybeia,
Sao dome Thrush Turdiis olivaceus , Sao Tome
Chestnut-winged Starling Onychognathusf.fidgidus,
Newton s Sunbird and the globally threatened Sao
Tome White-eye Zoster ops ( ficedulinus ) feae had
their highest encounter rates in the Bom Sucesso
mosaic compared to nearby forest, although this
result masks differences among discreet habitats
(annual cultivation, tree clumps, banana groves,
etc.) comprising the mosaic.
Birds, as a whole, were commonest in Lagoa
Amelia compared to Monte Carmo, with encounter
rates of 540 birds / 10 hours at the first compared
to 170 at the latter. Limited sampling effort and
almost constant rain during our stay at Monte
Carmo were factors, but the lower abundance of
birds observed was striking, especially of common
species such as prinias, speirops and Newton’s
Sunbird (Table 1).
The commonest endemics (Principe Seedeater,
Newton’s Sunbird, Sao Tome Speirops Zosterops
lugnbris and Sao Tome Weaver) were also the
most abundant species in both montane and lower
elevation forest, but with striking differences in
relative abundances. Overall, Monte Carmo had
lower encounter rates for most endemics, and the
white-eye was absent. Only the flycatcher, starling
and speirops had encounter rates that could be
considered similar.
King & Dallimer (2003) and Dallimer et al.
(2009), using mist-netting and point counts, also
found striking differences between montane and
lowland forests in the relative abundances of Sao
Tomean endemics, with montane forest holding
greater numbers of seedeaters, prinias, speirops,
Sao Tome Weaver and Newton’s Sunbird. In
contrast, orioles, paradise flycatchers, thrushes and
Giant Sunbird are commonest at lower elevations.
Data from encounter rates broadly agree with this
pattern.
Significant records
Dwarf Olive Ibis Bostrychia bocagei This species
was recorded only at Monte Carmo, a known site
for the species together with the 16 Grande River
and hillsides in the Formoso Grande area (ABS
2007, Leventis & Olmos 2009). What sounded
like a call was heard briefly at a distance in Formoso
Grande. Although considered silent compared to
other Bostiychia ibises (Christy & Clarke 1998,
Jones & Tye 2006), on 1 August three birds were
heard calling from different perches at dusk and
one called at dawn on 2 August. The voice (XC
18130) is, however, similar to related species.
Despite being used by hunters, Monte Carmo
harbours an important ibis population. On 1
August we recorded the first ibis near the campsite,
perched c.8 m above ground. On 2 August, at
06.18 hrs, one was seen perched in the lower
canopy at 00°09’02.8”N 06°34’05.1”E (321 m),
with another nearby at 10.00 hrs. On 3 August
we found eight birds during the morning (07.10-
11.20 hrs) while walking from 00°08’52.1”N
06°34T4.7”E (303 m) to 00°09’13.2”N
06°33’52.9”E (386 m). These included four lone
birds and two ‘pairs’, one of the latter comprising
an adult and a juvenile (which had a shorter bill
and drabber plumage). All of these birds, except
one of the lone individuals, were foraging on the
ground when first seen, with one bird perched on
a tree. Additionally, on 4 August another pair was
found at 00°08’55.6”N 06°34’32.6”E (c.284 m)
in a tree-fall gap in second-growth forest with little
leaf litter and much exposed soil.
Sightings were at least 150 m apart (the
latter much further), but we can not discount
the possibility of double-counting, although we
tried to track the direction birds flew or if they
remained perched when we lost contact with
them. The clumped records show an extraordinary
gathering of those rare, apparently solitary birds,
in a small area.
The ibises foraged alone or in loose family
groups, and were quite silent by day, calling only
at dusk and dawn, if at all. All were in mature or
old second-growth forest at 150-400 m with well-
spaced large trees, very Open undergrowth and
large patches of exposed soil resulting from feral
pig activity or rainwater. In some areas, the soil
was largely covered by irregularly shaped rocks,
which also results in an open understorey. The
association between ibises and disturbed soil or
open understorey has been mentioned previously
(Jones & Tye 2006).
Bird observations from Sao Tome: Olmos & Turshak
Bull ABC Vol 17 No 1 (2010) -57
58 -Bull ABC Vol 17 No 1 (2010)
Bird observations from Sdo Tome: Olmos & Turshak
Sao Tome Maroon Pigeon Columba thomensis
Two adults perched on a jackfruit tree at Juliana
de Sousa, with another in montane forest at
Pico Carvalho (00°16T2”N 06°34’35”E; 1,393
m) on 18 July, and one in the same spot on 9
August feeding on the fruit of Schefflera manii.
Another adult seen at 00°17’04”N 06°33’25”E
(1,165 m) on 20 July completes our records of
this uncommon species. The record at Juliana de
Sousa (214 m) reveals that the species is not strictly
associated with montane lorest and can utilise
capoeira at low elevations, at least seasonally.
Dallimer et al. (2009) found this species is
not a montane specialist as has sometimes been
suggested (Jones & Tye 2006), with significant
populations present in the lowlands of western
Sao Tome, where Juliana de Sousa is sited. On
the other hand, it was not found at Monte Carmo
during our survey (although one was seen in
January 2008), suggesting its occurrence in the
lowlands might be patchy or seasonal.
Sao Tome Short-tail Amaurocichla bocagii
Although Jones & Tye (2006) set the altitudinal
limit for this species at 500 m, Dallimer et al.
(2003) found one at 1,100 m in the island’s
central massif, the same general area where the
species was found breeding by Rocha (2008).
Maia & Alberto (2009) found short-tails to be
regular dwellers in montane forests above 1,300
m, and fairly common in some areas.
Our records support those findings. We located
the species near Formoso Grande, where a pair was
seen repeatedly on 29-30 July at 00°13’50.6”N
06°37’44.4”E (622 m) in a gully cut by a stream
running among boulders in low forest. More
interestingly, on 9 August we also found short-tails
along the slope of the Ana Chaves Valley, where
Legend to figure on opposite page
Figure 1. (a) Sao Tome Scops Owl / Petit-due de Sao
Tome Otus hartlaubr, (b) Sao Tome Green Pigeon /
Colombar de Sao Tome Treron sanctithomae\ (c) Sao
Tome Short-tail / Nasique de Bocage Amaurocichla
bocager, (d) Sao Tome Thrush / Merle de Sao Tome
Turdus olivaceofuscus ; (e) Juvenile Sao Tome Oriole /
Loriot de Sao Tome Oriolus crassirostris; (f) Male Sao
Tome Oriole / Loriot de Sao Tome Oriolus crassirostris ;
(g) Male Sao Tome Paradise Flycatcher / Tchitrec de Sao
Tome Tersiphone atrochalybeia\ (h) Sao Tome Prinia /
Prinia de Sao Tome Prinia molleri (Fabio Olmos, except
(c) A. P. Leventis)
a pair was seen at 00°15’45.4”N 06°34’23.7”E
(1,174 m), and a lone individual at 00°15’36”N
06°34’25”E (1,162 m), all in steep terrain covered
by transitional montane-low forest, and away
from water. As noted by Maia & Alberto (2009),
this suggests that potential habitat for the species
is more extensive than had been assumed.
The species was also found at the well-
known area of Monte Carmo. A pair was seen at
00°09’09”N 06°34T4.8”E, c.230 m, and a lone
bird at the campsite, both on 1 August. Next
day, a trio, a pair and a single individual were
recorded while walking the area of more level
ground between the campsite and 00°09 14.4”N
06°32’04.3”E, a transect of cA km. On 3 August
a pair was seen on the ground at 00 o 09’13.2”N
06°33’52.9”E in an area where the undergrowth
was open with many rocks on the forest floor,
which appears washed by rain, with little litter.
Another bird was observed in the lower strata (3-4
m high) on more level ground at 00°09T3.2”N
06°33’52.9”E (386 m), at least 100 m from a wet
gully. One bird was also seen nearby the following
morning.
In the very humid forests of Monte Carmo
only one pair was closely associated with water,
foraging near the ground by a drainage line with a
trickle of water. The others were seen on the forest
floor and lower strata of the forest. In montane
forests, Maia & Alberto (2009) also found short-
tails were not particularly associated with water,
unlike as previously suggested (Atkinson et al.
1991), and this finding was corroborated for lower
elevation forest by Dallimer et al. (2009).
Sao Tome Fiscal Lanius newtoni Restricted to
few sites in the south-east and south-west of Sao
Tome (those areas of highest rainfall), from the
Bombaim / Formoso area south-west through the
16 Grande Valley (Schollaert & Willem 2001),
the Martim Mendes basin above Ribeira Peixe
and west to the Xufexufe basin (King & Dallimer
2003) to c. 1 ,300 m (Maia & Alberto 2009). On 3
August, one was observed low down in a narrow
forested gully at Monte Carmo (00°09T2.7”N
06°33’48.9”E; 400 m).
Our excursion to Ana Chaves, south-west
of the Bombaim / Formoso area and within the
headwaters of the 16 Grande, had the specific
goal of finding this species. The site lies in a deep
valley with steep slopes. As we descended we heard
Bird observations from Sao Tome: Olmos & Turshak
Bull ABC Vol 17 No 1 (2010) -59
Table 1. Bird species recorded during this survey. Numbers indicate the number of individuals detected per ten hours of all-
records censuses, whilst x indicates species recorded outside census periods.
Tableau 1 . Especes d’oiseaux observees pendant I’inventaire. Les chiffres indiquent le nombre d’individus detecte par dix
heures de recensement, tandis que x indique les especes observees en dehors des periodes de recensement.
A: Farms around Bom Sucesso, including tree clumps and small remnant forest patches amid cultivated areas. Census effort: 5.5 hours.
B: Montane forest near Bom Sucesso, mostly along the trail to Lagoa Amelia and to Novo Ceilao. Census effort: 14.15 hours.
C: Low forest around the Monte Carmo campsite. Census effort: 7.8 hours.
D: Trail through shade forest and capoeira (old coconut and cocoa plantations) between rogas Binda and Juliana de Souza. Census effort: only qualitative observations.
E: Trek through montane forest from Bom Sucesso up Pico de Sao Tome and down to shade forest above Ponta Figo. Census effort: only qualitative observations.
F: Tall shade forest near Roga Bombaim. Census effort: qualitative observations.
G: Gardens, orchards, vacant lots, urban areas and the airport environs around Sao Tome town. Census effort: only qualitative observations.
A : Zones cultivees autour de Bom Sucesso, y compris des fourres et des lambeaux de foret au milieu de cultivations. Effort de recensement : 5,5 heures.
B : Foret montagnarde pres de Bom Sucesso, principalement le long du sentier vers Lagoa Amelia et Novo Ceilao. Effort de recensement : 14,15 heures.
C : Foret de basse altitude autour du camp a Monte Carmo. Effort de recensement : 7,8 heures.
D : Sentier a travers de la foret ombrophile et de capoeira (vieilles plantations de cocotiers et de cacao) entre ropas Binda et Juliana de Souza. Effort de recensement :
uniquement des observations non systematiques.
E : Trajet a travers de la foret montagnarde de Bom Sucesso a Pico de Sao Tome et, a la descente, traversal la foret ombrophile au dessus de Ponta Figo. Effort de
recensement : observations non systematiques.
F : Foret ombrophile pres de Ropa Bombaim. Effort de recensement : observations non systematiques.
G : Jardins, vergers, terrains vagues, zones urbaines et environs de I'aeroport autour de la ville de Sao Tome. Effort de recensement : observations non systematiques.
Common name
Scientific name
A
B
C
D
E
F
G
White-tailed Tropicbird
Phaethon lepturus
X
X
Cattle Egret
Bubulcus ibis
12.5
X
X
Green-backed Heron
Butorides striata
X
X
Western Reef Heron
Egretta gularis
X
Dwarf Olive Ibis
Bostrychia bocagei
11.5
Yellow-billed Kite
Milvus ( migrans ) parasitus
X
X
Red-necked Spurfowl
Francolinus afer
X
Common Sandpiper
Actitis hypoleucos
X
Sao Tome Green Pigeon
Treron sanctithomae
1.8
10.6
2.6
X
X
X
Sao Tome Bronze-naped Pigeon
Columba matherbii
3.6
2.1
Sao Tome Lemon Dove
Cotumba larvata simplex
16.1
26.1
2.6
X
X
X
Sao Tome Maroon Pigeon
Columba thomensis
X
X
Feral Pigeon
Columba livia
X
X
Laughing Dove
Streptopelia senegalensis
1.8
X
X
X
Red-headed Lovebird
Agapornis pullarius
X
X
Emerald Cuckoo
Chrysococcyx cupreus insularum
1,8
X
X
Barn Owl
Tyto alba thomensis
X
X
Sao Tome Scops Owl
Otus hartiaubi
X
X
X
Sao Tome Spinetail
loonavena thomensis
69.6
4.9
X
X
X
Palm Swift
Cypsiurus parvus
12.5
X
X
X
Common Swift
Apus cf. apus
X
Little Swift
Apus affinis bannermani
8.9
X
X
X
Sao Tome Kingfisher
Alcedo ( cristata ) thomensis
X
X
Sao Tome Thrush
Turdus olivaceofuscus
16.1
9.2
1.3
X
X
X
X
Sao Tome Prinia
Prinia molleri
35.7
42.4
12.8
X
X
X
X
Sao Tome Short-tail
Amaurocichla bocagii
7.7
Sao Tome Paradise Flycatcher
Tersiphone atrochalybeia
26.8
14.1
15.3
X
X
Newton's Sunbird
Anabathmis newtoni
128.6
84.1
20.4
X
X
X
X
60 -Bull ABC Vol 17 No 1 (2010)
Bird observations from Sao Tome: Olmos & Turshak
Common name
Scientific name
A
B
C
D
E
F
G
Giani Sunbird
Dreptes thomensis
3.5
1.3
X
X
Sao Tome White-eye
Zosterops (ficedulinus) feae
50.0
17.0
X
Sao Tome Speirops
Zosterops lugubris
117.9
114.5
17.9
X
X
X
Sao Tome Fiscal
Lanius newtoni
X
Sao Tome Oriole
Oriolus crassirostris
12.5
21.2
14.0
X
Sao Tome Chestnut-winged Starling
Onychognathus f. fulgidus
17.9
2.8
2.6
X
X
X
X
Vitelline Masked Weaver
Ploceus velatus peixotoi
35.7
1.3
X
X
Giant Weaver
Ploceus grandis
X
X
X
Sao Tome Weaver
Ploceus sanctithomae
30.4
84.8
25.5
X
X
X
Fire-crowned Bishop
Euplectes hordeaceus
X
Common Waxbill
Estrilda astrild
282.1
X
X
Southern Cordon-bleu
Uraeginthus angolensis
X
Bronze Mannikin
Lonchura cucullata
50.0
X
Pin-tailed Whydah
Vidua macroura
X
Yellow-fronted Canary
Serinus mozambicus
X
Principe Seedeater
Serinus rufobrunneus thomensis
123.2
102.5
33.2
X
X
X
Sao Tome Grosbeak
Serinus ( Neospiza ) concolor
X
a bird calling at 00°15’45.4”N 06°34’23.7”E
(1,174 m). More were heard when we reached the
bottom at 00°15’39.4”N 06°34’33.9”E (1,065 m)
and playback during the next three hours elicited
vocal response, although no birds approached the
source. At least three were heard together along
the creek running along the valley, one of them
<20 m away.
Together with information in the literature
our records suggest an association between this
species and watercourses, or at least to more open
areas in forest, like gullies and riversides, created
by water. That could mean that fiscal habitat is
more linear, or patchy, than currently believed.
Sao Tome Grosbeak Serinus ( Neospiza ) concolor
Positively recorded only from lower altitude forest
in the south-west of the island (Jones & Tye
2006), although there is one record from the
Monte Cafe area, near Bom Sucesso (Simpson
2002). In the Monte Carmo area (at 00 o 09’12.4”N
06°33’55.3”E; 370 m), we heard a song identified
as a grosbeak (XC17889) on 4 August at 07.50
hrs. The bird responded but did not approach
after playback, moving to a nearby gully, where
two individuals were seen in the canopy and lower
understorey. The same recording was successfully
used to attract a pair in the Monte Carmo area in
January 2008.
Conservation issues
Recent conservation initiatives in the country
have been linked mostly to ECOFAC (Central
Africa Forest Ecosystem Programme), the largely
French-funded project that aims to conserve West
African forests. Starting in 1992, this resulted in
the establishment of the 295 km 2 Obo Natural
Park, covering the most mountainous and least
accessible parts of both Sao Tome and Principe
(c.30% of the country), and other related initiatives.
Although all land belongs to the government (a
legacy of the previous socialist regime), the park’s
status is still fragile, the law creating it being issued
only in 2006. The zoning and management plan
of the park were being prepared in 2008, when the
first directors were appointed, but the park still
lacks sufficient personnel and means to enforce
the law. Agricultural encroachment is evident in
more accessible parts of the park such as Bom
Sucesso, whilst hunting is widespread.
With an only recent opening for free enterprises
(Seibert 2002), cocoa, coffee and oil palm exports
from Sao Tome are to date limited. Much of the
economy is at subsistence level; small-scale farming
is widespread and extractive activities such as the
harvesting of palm-wine and hunting of pigeons,
introduced monkeys and pigs are locally important
(Carvalho 2008). These occur wherever forest can
be accessed. During our stay, large numbers of
Bird observations from Sao Tome: Olmos & Turshak
Bull ABC Vol 17 No 1 (2010) -61
62 -Bull ABC Vol 17 No 1 (2010)
Bird observations from Sao Tome: Olmos & Tursbak
people were harvesting palm-wine and hunting
in the Formoso Grande / Bombaim area, which
was crisscrossed by heavily used trails (some to
the point of eroding) and some shelters had been
built even inside the park. The same was true of
the Brune area, adjacent to Juliana de Sousa and
also part of the Obo park.
Hunting is a widespread, unregulated and
socially accepted activity (Carvalho 2008), and
hunters were met frequently in the Obo park,
including within the environs of Lagoa Amelia
and the trail to Pico de Sao Lome. Although
subsistence hunters prefer feral pigs and Mona
Monkeys Cercopithecus mona , larger birds like
Dwarf Olive Ibises and pigeons are also taken.
Also, several commercial hunters harvest pigeons
using airguns to supply urban consumers. On
most ol the trails small piles of feathers (mostly
from Sao Tome Green and Bronze-naped Pigeons
but, at Juliana de Sousa, also Sao Tome Pigeons)
and spent shotgun cartridges were easily found.
1 he abundance of harvested and threatened
species on both Principe and Sao Tome is
negatively correlated with distance from roads
and trails (Dallimer & King 2007, Dallimer et al.
2009). The effect of hunting on species such as
the ibis is obvious and might explain the species’
absence from Lagoa Amelia, but more subtle
effects from the presence of people must affect
species that are not directly exploited, for example
the fiscal, short-tail and grosbeak.
Monte Carmo harbours all of the threatened
endemics, including surprising numbers of ibises.
The area (sometimes called Ribeira Peixe) has
been considered a priority site for conservation
action by the BirdLife International partnership.
BirdLife has supported the establishment and staff
Legend to figure on opposite page
Figure 2. (a) Newton’s Sunbird / Souimanga de Newton
Anabathmis newtoni; (b) Giant Sunbird / Souimanga
de Sao Tome Dreptes thomensis\ (c) Sao Tome White-
eye / Zosterops beefigue Zosterops ( ficedulinus ) fear, (d)
Sao Tome Speirops / Zosterops de Sao Tome Zosterops
lugubris-, (e) Sao Tome Chestnut-winged Starling /
Rufipenne de foret Onychognathus fulgidus fulgidus ; (f)
Sao Tome Seedeater / Serin roux Serinus rufobrunneus
thomensis ; (g) Sao Tome Weaver / Tisserin de Sao Tome
Ploceus sanctithomae ; (h) Male Giant Weaver / Tisserin
geant Ploceus grandis (Fabio Olmos)
training of a local NGO, Associa^ao dos Biologos
Saotomenses (ABS) as a country partner, whilst
ABS has already undertaken a broad survey of
ibis distribution (ABS 2007) and has commenced
monitoring all of the Critically Endangered species
at Monte Carmo by employing field assistants
from the local community. Further activities are
planned to promote the conservation of the area,
part of the buffer zone of the Obo park, including
awareness campaigns targeting local people.
Monte Carmo is probably the most accessible
site where all of the threatened endemics can be
found and is already a well-known destination for
birders. An international workshop to promote
ecotourism in Sao Tome and Principe held in
February 2008 listed birding as an activity to be
encouraged and specifically mentioned Monte
Carmo as a site for a pilot project. In July 2009
ABS promoted a short course for training bird
guides to work in Monte Carmo and it is hoped
that this initiative will bear fruit and be supported
by the birdwatching community.
However, Monte Carmo faces pressure
from neighbouring communities. The lowlands
adjoining the forested slopes are occupied by the
old oil-palm plantations of EMOLVE. Once the
main supplier of cooking oil for the country prior
to independence, the plantations subsequently
entered a period of decline, with only limited
renovation since. The plantations are home to
some 500 people, who lack access to electricity or
treated water. The oil-processing plant currently
employs just 30 persons, half of them on a part-
time basis, down from some 400 a few decades
ago. The result is that large numbers of people
are engaged in palm-wine harvesting, hunting
and other extractive activities, signs of which are
evident in the core of Monte Carmo.
Sao Tome and Principe faces daunting
problems associated with poverty and an increasing
population, now estimated at c. 156,000 people,
etching a living in a very limited land area (Leventis
& Olmos 2009, Dallimer et al. 2009). The post-
independence regime oversaw the collapse of most
of the commercial plantations that the economy
was reliant upon, and a move to food crops for
the local market and extractive activities. This is
now changing as the current government seeks to
restore the country’s agricultural potential, with
direct impacts at Monte Carmo.
Bird observations from Sao Tome: Olmos & Tursbak
Bull ABC Vol 17 No 1 (2010) -63
In June 2009 the plantations were ceded by the
government (which owns all land in the country)
to the French-Belgian-Luxembourg Socfinal
company, which owns oil-palm plantations in
Africa and Indonesia. According to the local press,
Socfinal plans to restore c.2,000 ha of plantations
on the south coast ol Sao Tome, which could
either result in greater local employment and fewer
people engaged in hunting and other damaging
activities, or more people moving to the area being
attracted by possible jobs, with more substantial
impacts on the forest and its threatened birds. The
outcome will largely depend on policies adopted
by the plantation’s managers.
Also in mid 2009, a similar concession to
a Libyan group was announced for the Monte
Cafe plantation, near Bom Sucesso and site of
an undocumented grosbeak sighting (Simpson
2002). As the business environment in the country
improves and investors’ interest increases, it is
probable that more initiatives of this nature will
appear, almost certainly resulting in capoeiras
being turned into plantations and potentially
resulting in increasing pressure on natural areas
if expansion is deemed profitable. A real threat is
that small-scale producers of food crops will be
dislodged, with further encroachment into the
park resulting, as is already occurring in the Bom
Sucesso area.
The sustainability of conservation initiatives in
Sao Tome and Principe is a real issue. The country
still lacks a critical mass of trained conservation
professionals and NGOs rely entirely on external
support. Furthermore, it is uncertain if projects
such as ECO FAC will leave an enduring legacy
when funding is removed. On the other hand, new
actors are forcing changes that, for good or worse,
will affect the country’s endemic and threatened
species. The outcome remains uncertain.
Acknowledgements
Peter Jones and Will Cresswell made important
suggestions on an earlier draft of his paper. Our work
would have been impossible without the support of
the A. P. Leventis Conservation Foundation. Nigel
Collar proffered continuous encouragement and helped
unravel many problems. Bastien Loloum ‘navigated’ us
through many local issues in Sao Tome and Principe.
We also acknowledge with gratitude the assistance
of Faustino Oliveira, Alzira Rodriques, Luiz Mario
Almeida, Antonio Alberto, Pedro Leitao and all those
who contributed in one way or the other to our survey.
Finally, we thank Rita Souza and Ruth Ndam for their
understanding while we were away.
References
ABS (Associa^ao de Biologos Saotomenses) 2007.
Status and distribution of the Dwarf Ibis Bostrychia
bocagei in Sao Tome. Unpubl. report to BirdLife
International.
Atkinson, P., Peet, N. & Alexander, J. 1991. The status
and conservation of the endemic bird species of
Sao Tome and Principe, West Africa. Bird Conserv.
Intern. 1: 255-282.
Bibby, C., Jones, M. & Marsden, S. 1998. Expedition
Field Techniques: Bird Surveys. London, UK:
Expedition Advisory Centre, Royal Geographical
Society.
BirdLife International. 2008. Species factsheets. www.
birdlife.org (accessed 10 December 2008).
Carvalho, M. B. 2008. Utilizacpto de recursos
animais, desenvolvimento rural e conserva^ao
da biodiversidade em Sao Tome, Repiiblica
Democratica de Sao Tome e Principe. Relatorio de
Progresso, Projeto SFRH/ BD/ 30171 / 2006.
Christy, P. 2001. Sao Tome and Principe. In Fishpool,
L. D. C. & Evans, M. I. (eds.) Important Bird
Areas in Africa and Associated Islands: Priorities for
Biodiversity Conservation. Cambridge, UK: BirdLife
International.
Christy, P. & Clarke, W. P. 1998. Guide des oiseaux de
Sao Tome e Principe. Sao Tome: ECOFAC.
Dallimer, M. & King, T. 2007. Habitat preferences of
the forest birds on the island of Principe, Gulf of
Guinea. Af. J. Ecol. 46: 258-266.
Dallimer, M., King, T. & Atkinson, R. 2003. A
high altitude sighting of the Sao Tome Short-tail
Amaurocichla bocagei. Malimbus 25: 101-103.
Dallimer, M., King, T. & Leitao, P. 2003. New records
of the Sao Tome Grosbeak Neospiza concolor. Bull.
ABC 10: 23-25.
Jones, P. & Tye, A. 1988. A Survey of the Avifauna
of Sao Tome and Principe. ICBP Study Rep. 24.
Cambridge, UK: International Council for Bird
Preservation.
Jones, P. & Tye, A. 2006. The Birds of Sao Tome
& Principe with Annobon: Islands of the Gulf of
Guinea. An Annotated Checklist. BOU Checklist
No. 22. Oxford: British Ornithologists’ Union &
British Ornithologists’ Club.
King, T. & Dallimer, M. 2003. Daily activities, moult
and morphometries of the birds of Sao Tome and
Principe. Bull. ABC 10: 84-93.
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Leventis, A. P. & Olmos, F. 2009. As Aves de Sao Tome
e Principe: Um Guia Fotografico / The Birds of Sao
Tome e Principe: A Photoguide. Sao Paulo: Aves e
Fotos.
Maia, H. A. & Alberto, A. C. 2009. The occurrence
ol Sao 9 ome Short-tail Amaurocichla bocagii and
Newton’s Fiscal Lanius newtoni in the montane
forests of Sao Tome. Bull. Brit. Orn. Club 129:
213-216.
Melo, M. 2007. Bird speciation in the Gulf of Guinea.
Ph.D. thesis. Institute of Evolutionary Biology,
University of Edinburgh.
Melo, M. & Jones, P. J. (in press) Bird speciation in
the Gulf ol Guinea island system. In Harebottle,
D. M., Craig, A. J. F. K., Anderson, M. D.,
Rakotomanana H. & Muchai, M. (eds.) Proc. 12th
Pan-Afr. Orn. Congr., 2008, Cape Town: Animal
Demography Unit.
Pacheco, J. F. & Olmos, F. 2005. Birds of a latitudinal
transect in the Tapajos-Xingu interfluvium, eastern
Brazilian Amazonia. Ararajuba 13: 27-44.
Rocha, J. R. T. 2008. Birds in humanized landscapes:
Sao Tome endemic birds' response to agricultural
intensification. M.Sc. thesis. Imperial College,
London, UK.
Sargeant, D. 1994. Recent ornithological observations
from Sao Tome and Principe Islands. Bull. ABC
1: 96-102.
Seibert, G. 2002. Camaradas, Clientes e Compadres:
Colonialismo, Socialismo e Democratiza^do em Sao
Tome e Principe. Lisbon: Ed. Veja.
Schollaert, V. & Willem, G. 2001. A new site for
Newton’s Fiscal Lanius newtoni. Bull. ABC 8:
21 - 22 .
Simpson, N. 2002. New observations of Sao Tome
Grosbeak. Bull. ABC 9: 90.
'Largo do Paissandu 10014c, 01034-010, Sao Paido, SP,
Brazil. E-mail: f-olmosdPuol. com. br
'A. P. Leventis Ornithological Research Institute, University
of Jos, PO Box 13404, Plateau State, Jos, Nigeria. E-mail:
longtongturshak@yahoo. com
Received 5 December 2007; revision accepted 18
November 2009.
Corrigenda
Bull. ABC 16 ( 1 )
In the report of the Moroccan Rare Birds Committee,
the captions for Figs. 6 and 7 on p. 34 should be
reversed.
In Salewski et all s paper on the search for the winter
quarters of the Aquatic Warbler Acrocephalus paludicola ,
the person holding the Aquatic Warbler in Fig. 3 on
p. 63 is Indega Bindia, not Ibrahima Gueye.
Bull. ABC 16 ( 2 )
In the reportage concerning the Djibouti Francolin
Francolinus ochropectus survey, on p. 138, the area of
potentially suitable habitat in the Mabla Mts. should
have read 4.3 km 2 .
In Louette & Hasson’s paper on the rediscovery of the
Lake Lufira Weaver Ploceus ruweti , the reference ‘Craig
2004’ on p. 169 should be replaced by ‘Oschadleus
2004a’, and on p. 172 by 'Oschadleus 2004b’. In the
reference list, the entry ‘Craig, A. J. F. K. 2004. Ploceus
ruweti. In Fry, C. H. & Keith, S. (eds.) The Birds of
Africa. Vol. 7. London, UK: Christopher Helm’ should
thus be replaced by:
Oschadleus, D. 2004a. Ploceus ruweti. In Fry, C. H. &
Keith, S. (eds.) The Birds of Africa. Vol. 7. London,
UK: Christopher Helm.
Oschadleus, D. 2004b. Ploceus velatus. In Fry, C. H. &
Keith, S. (eds.) The Birds of Africa. Vol. 7. London,
UK: Christopher Helm.
The lark shown in Recent Reports on p. 234, Fig. 2, is
not Friedmann’s Lark Mirafra pulpa, but Foxy Lark M.
alopex. The Kenya record of Friedmann’s Lark of 17
May 2009, mentioned on p. 232, is thus also erroneous
See the Photospot in this issue for a discussion of the
identification features of both species.
Bird observations from Sao Tome: Olmos & Turshak
Bull ABC Vol 17 No 1 (2010) -65
First records of eight bird species for Eritrea
Jason Anderson
Premiere mention de huit especes d’oiseaux pour l’Eritree. Huit additions a l avifaune de l’Eritree,
observees en octobre 2007— avril 2009, sont documentees. II s’agit des especes suivantes : 1 Erismature
maccoa Oxyura maccoa , le Courvite somalien Cursorius somalensis , le Pigeon rameron Columba arquatrix,
le Grand-due du Cap Bubo capensis, l’Engoulevent d’Abyssinie Caprimulgus poliocepbalus, la Bergeronnette
a longue queue Motacilla clara, le Traquet familier Cercomela familuzris et la Locustelle tachetee Locustella
naevia. Quatre d’entre elles sont presumees etre des residents, deux sont vraisemblablement des migrateurs
locaux, une est probablement occasionnelle, tandis que la derniere est un migrateur palearctique. Trois
especes ont ete vues a deux occasions separees et une, 1’Erismature maccoa, a ete notee sept fois en quatre
localites differences, indiquant qu’il s’agit probablement d un colonisateur recent, qui a etendu son aire de
distribution vers le nord a partir de l’Ethiopie.
Summary. Eight additions to Eritrea’s bird list, recorded in the period October 2007-April 2009, are
documented: Maccoa Duck Oxyura maccoa, Somali Courser Cursorius somalensis, African Olive Pigeon
Columba arquatrix, Cape Eagle Owl Bubo capensis, Montane Nightjar Caprimulgus poliocepbalus, Mountain
Wagtail Motacilla clara, Familiar Chat Cercomela familiaris and Grasshopper Warbler Locustella naevia. Ot
these, four are presumed residents, two are likely to be local migrants, one is probably a vagrant and one is a
Palearctic migrant. Three species were seen on two separate occasions and one, Maccoa Duck, was recorded
seven times at four different localities, indicating that it is probably a recent colonist, having expanded its
range north from Ethiopia.
F rom September 2007 to June 2009 I lived in
Adi Keyih, a town in the south of the Eritrean
highlands. During this time I recorded eight new
species for the country, which are documented
here. Some of these have already been included in
Ash & Atkins (2009) and Redman etal. (2009). As
I spent most of my time in and around Adi Keyih,
unsurprisingly six of these species were recorded in
the vicinity of the town, which lies c. 35 km north
of the Ethiopian border. The other two were
found in Eritrea’s only remaining extensive forest
area, Filfil, in the centre of the country.
Maccoa Duck Oxyura maccoa
On 25 April 2008 at c. 16.00 hrs, on a small
reservoir near the village of Hawatsu (14°53’48”N
39°20’55”E) at 2,300 m, c. 10 km from Adi
Keyih, I observed four unusual ducks, c . 50 m
distant. Given their close proximity and the lack
of confusion species, it was easy to identify them
as Maccoa Ducks, despite the absence of males in
breeding plumage. They had a pale stripe below
the eye, which contrasted with the overall dark
brown plumage, and a stiff tail, diagnostic in sub-
Saharan Africa of this species. The bill was dark.
I took several photos, in which the key features
can be seen.
Subsequently, I recorded the species on six
other occasions (Table 1; Fig. 1). These records
indicate that Maccoa Duck is widespread in
the Eritrean highlands and present year-round,
although I did not observe evidence of breeding.
It is probable that, with the increasing number
of reservoirs, Maccoa Duck has extended its
range north from Ethiopia, colonising Eritrea in
recent years. As other reservoirs are planned, other
waterbirds might also extend their range north
into Eritrea in the near future.
Table 1. Records of Maccoa Duck Oxyura maccoa in Eritrea, 2008-09
Tableau 1. Mentions de I'Erismature maccoa Oxyura maccoa
en Eritree, 2008-09
Date
Locality / Localite
Number / Nombre
25 Apr 2008
Small reservoir near Hawatsu
4
10 May 2008
Afoma Reservoir, near Senate
2; 1 d breeding
plumage (br.)
2 Jul 2008
Tseaziga Reservoir, near Tsada Christian
IT br.
21 Jul 2008
Adi Nfas Reservoir, near Asmara
8-9; at least 4 d br.
1 Sep 2008
Acria Reservoir, near Asmara
2; Id br.
25 Jan 2009
Adi Nfas Reservoir, near Asmara
1 non-br.
14 Feb 2009
Afoma Reservoir, near Senate
5; 2d coming into br.
66 -Bull ABC Vol 17 No 1 (2010)
First records of eight bird species for Eritrea: Anderson
Figure 1 . Male Maccoa Duck / Erismature maccoa Oxyura maccoa , Acria Reservoir, near Asmara, 1 September 2008 (J.
Anderson)
Figure 2. African Olive Pigeon / Pigeon rameron Columba arquatrix , Karibosa (S. Ferwerda)
Figure 3. Cape Eagle Owl / Grand-due du Cap Bubo capensis dillonii, Adi Keyih, Eritrea, April 2008 (J. Anderson)
Figure 4. Montane Nightjar / Engoulevent dAbyssinie Caprimulgus poliocephalus (sex unconfirmed), Abi Girat, Eritrea,
25 February 2009 (J. Anderson)
Figure 5. Adult Mountain Wagtail / Bergeronnette a longue queue Motacilla clara, Adi Keyih, Eritrea, 21 October
2007 (J. Anderson)
Figure 6. Juvenile Mountain Wagtail / Bergeronnette a longue queue Motacilla clara , Adi Keyih, Eritrea, 21 October
2007 (J- Anderson)
Figure 7. Grasshopper Warbler / Locustelle tachetee Locustella naevia, Sabur, near Filfil, Eritrea, 26 January 2009 (J.
Anderson)
First records of eight bird species for Eritrea: Anderson
Bull ABC Vol 17 No 1 (2010)- 67
Somali Courser Cursorius somalensis
On 6 March 2008, at 07.10 hrs 1 was passing
on my motorbike near the village of Mealewia
(14°49’13”N 39°2f50”E), c. 3 km south-west of
Adi Keyih, at 2,400 m. Approximately 20 m from
the road, on some ploughed but barren land I
noticed a courser. I observed it through binoculars
from a distance of c. 20 nr and made field notes.
The bird’s overall coloration was beige, and it
had a clear black eye-stripe, a white supercilium, a
dark grey crown and a white belly/vent, obviously
paler than the breast. The bill was black and the
legs pale grey. I twice flushed the bird and on
both occasions clearly saw its pale inner wing,
which is diagnostic of Somali Courser, Cream-
coloured Courser C. cursor having an all-dark
underwing. Subsequent visits to the same spot did
not produce any more sightings, either that day,
or on the following two days.
This is the first documented record of Somali
Courser for Eritrea. An unpublished trip list by
K. Harte and D. Berhane from December 2004
mentions a record of four Somali Coursers in the
Eritrean coastal lowlands near Foro, c.50 km from
Adi Keyih at sea level. D. Berhane (pers. comm.)
informed me that he was unaware at the time that
the species had not previously been recorded in
Eritrea, and that he did not possess any field notes
to confirm the identification.
The nearest confirmed sightings are from the
north-eastern lowlands of Ethiopia and just across
the border in Djibouti, c.400 km south-east of
my sighting (Ash & Atkins 2009). The Eritrean
records indicate that the species occasionally
occurs significantly further north of its usual range
and could conceivably occur alongside Cream-
coloured Courser. However, the high altitude of
my bird is atypical, suggesting a vagrant.
African Olive Pigeon Columba arquatrix
On 26 January 2008 at 09.20 hrs, I was
birdwatching near Filfil Solomuna, in the vicinity
of the Medhanit Recreation Centre (15°37’0T’N
38°56’07”E) at 1,000 m, in the middle of Eritrea’s
largest remaining tract of tropical forest. In a
mature broad-leaved tree I observed a large pigeon
with a dark head, yellow eye-ring, yellow bill,
purple-grey on the wing and mantle, pale spots
/ mottling on the breast, and yellow feet. These
features are diagnostic of African Olive Pigeon.
The bird was only visible for c.30 seconds before
it disappeared into denser forest. I remained in the
area for another three days, frequently returning
to the same spot, but did not see the bird again.
On 14 February 2008 at 11.35 hrs, I was
walking with two colleagues through riparian
woodland at Karibosa, near Adi Keyih (14°54’42 N
39°25T2”E; c.100 km south of the first sighting)
at 2,500 m, when I observed another African
Olive Pigeon in a broad-leaved tree, c. 5 m above
me. We watched the bird for 5-7 minutes in
excellent conditions and one of my colleagues
took several photographs (Fig. 2).
These two sightings extend this pigeon’s range
north significantly, the nearest confirmed records
being from 500 km further south, in Ethiopia
(Ash & Atkins 2009), although the species has
recently also been discovered slightly nearer, in
Djibouti (Redman et al. 2009). The species is
probably resident in small numbers in isolated
patches of mature woodland in Eritrea.
Cape Eagle Owl Bubo capensis
On 1 April 2008, when I was visiting a school in
Adi Keyih (14 0 51’14”N 39°22’07”E), at 2,400 m,
I noticed a group of children surrounding a boy
who was carrying a large owl. It transpired that he
had bought the bird from a person who had found
it injured on the ground close to a nearby village.
I took the owl home and kept it alive for several
days. The humerus of the left wing was completely
broken close to the body.
The bright yellow-orange eyes separated it
from all other large owls except Desert Eagle
Owl B. ascalaphus. The overall darkness of the
plumage, very heavy mottling on the upper breast
and strong mottling on the belly identified it as
Cape Eagle Owl (Fig. 3). Its length was 50 cm.
The race present in Ethiopia (and presumably
that involved here) is dillonii, which is sometimes
treated with B. c. mackinderi (of Mozambique
to Kenya) as a separate species, Mackinder’s
Eagle Owl Bubo mackinderi. The Natural History
Museum at I ring possesses a specimen of Cape
Eagle Owl collected in Senafe, Abyssinia, in 1868
(BMNH 1887.11.11.24), which is erroneously
mentioned as a Desert Eagle Owl in Ash & Atkins
(2009), leaving just one confirmed record for the
latter species in Eritrea. As Senafe is in present-day
Eritrea, the specimen becomes the first confirmed
record of Cape Eagle Owl for the country,
the record documented here being the second.
68 -Bull ABC Vol 17 No 1 (2010)
First records of eight bird species for Eritrea: Anderson
Although the nearest confirmed records are from
central Ethiopia, 600 km to the south, there
are also lour uncertain records from northern
Ethiopia (Ash & Atkins 2009). It seems likely
that the species is a rare resident in Eritrea, and
possibly also in northern Ethiopia.
Montane Nightjar Caprimulgus poliocephalus
On 25 February 2009, at c. 13.00 hrs, I flushed a
nightjar from the ground near the village of Abi
Girat, near Adi Keyih (14°53’33”N 39°22’00”E)
at 2,200 m, along a lightly wooded stream in
a small, quite barren valley with some small
Acacia abyssinica and Prickly Pear Opuntia ficus-
indica. 1 he bird settled c. 7 m away, and I took
several photographs (Fig. 4). The only features I
noticed were the rather dark overall coloration,
a prominent chestnut collar, and several cream
spots on the wing-coverts. It seemed similar in
size to Dusky Nightjar C. frenatus , a species I
had positively identified nearby, and I initially
suspected that it was that species. When the bird
flew off, it showed clear white wing spots, but I
did not notice the tail pattern. When I tried to
relocate the bird, I was only successful in flushing
it again, whereupon it emitted a monosyllabic call
twice in quick succession, kwa-kwa. It flew a little
further away and, despite extensive searching, I
was unable to find the bird again. Subsequent
analysis of the photographs revealed the bird to be
a Montane Nightjar.
Two months later, on 25 April 2009 at
c. 11.30hrs, 1 was birdwatching with D. Berhane
at Karibosa, near Adi Keyih (14°54’49”N
39°25’18”E) at 2,500 m, when he flushed another
Montane Nightjar from dense cover close to a dry
riverbed. The bird settled on a branch, where we
could take good-quality photographs. Comparison
of these with two specimens at the Natural History
Museum, Tring, collected near Fake Tana, in
north-west Ethiopia (one male and one female),
revealed that the plumage of the Eritrean birds was
identical to that of the specimens.
Montane Nightjar is a rather uncommon
resident in Ethiopia and the nearest confirmed
record is from the Simien Mountains (Ash &
Atkins 2009). Given the presence of suitable
habitat in the southern Eritrean highlands, the
species had long been suspected to occur. It is
probably resident there, extending the species'
range c.200 km northwards.
Mountain Wagtail Motacilla clara
On 21 October 2007 ar 14.30 hrs, I was
birdwatching in the Maka stream gorge near Adi
Keyih (14°51’52”N 39°23’13”E) at 2,300 m.
Following heavy rains, the stream was flowing
well and I came across three wagtails that seemed
quite different to White Wagtail M. alba, which
is a common Palearctic migrant in the area. All
three had a plain grey head and mantle, and dark
wing feathers narrowly edged white. Two birds
had a slim, dark ‘V’-shaped breast-band, but this
was absent on the third, which followed the other
rwo. All three birds frequently uttered short sharp
contact calls. I watched them for c. 20 minutes,
following them downstream, and took several
poor-quality photographs, which confirm their
identity as Mountain Wagtails (Figs. 5-6). The
third bird’s lack of breast-band indicates it was
a juvenile. Whilst confusion with juvenile White
Wagtail is possible, I observed the key features of
Mountain Wagtail (narrow white supercilium, no
black moustachial stripe, no white on the median
coverts, very long tail).
This is the first record of Mountain Wagtail
for Eritrea. 1 he species is common in northern
Ethiopia (Ash & Atkins 2009), making it
unsurprising that it ranges slightly into Eritrea.
However, despite checking the same stream
regularly during the next two years, I did not
see the species there again. In 2008 the rains
were not as heavy and the water level was much
lower. Mountain Wagtail may be a local migrant,
appearing, and possibly breeding, in Eritrea only
after heavy rains.
Familiar Chat Cercomela familiaris
On 12 October 2007 at 16.00 hrs, close to the
village of Safira, near Adi Keyih (14°51T8”N
39°24’19”E) at 2,550 m, in an area of open scrub
with large boulders, I spotted a small passerine
pursuing insects 10-15 m away. The bird, which
was constantly flicking its wings and bobbing its
tail, was drab brown overall and had a brownish-
rufous rump and outer tail with a ‘T-shaped dark
central band and tail end. The slender, horizontal
jizz did not match Common Redstart Phoenicurus
phoenicurus or Black Redstart P. ochruros, both
of which I know well, and the underparts were
also too pale for either. I observed the bird for
c. 5 minutes before it flew off and identified it as
a Familiar Chat. Despite extensive observation,
First records of eight bird species for Eritrea: Anderson
Bull ABC Vol 17 No 1 (2010) -69
I did not notice the rufous mask described and
illustrated in Sinclair & Ryan (2003); instead, the
head appeared uniformly brown.
Exactly one year later, on 12 October 2008,
I encountered the species again, feeding in a dry
streambed in a rocky valley several kilometres
south of the original sighting. I attempted to take
a photograph, but the bird flew off and I failed to
relocate it.
These are the first records for Eritrea of
Familiar Chat, whose Ethiopian range extends
right up to the Eritrean border. My sightings thus
extend the species’ range only slightly but they
are from a higher altitude than those in Ethiopia
(1,090-2,000 m: Ash & Atkins 2009). I visited
both sites regularly thereafter, but did not find
the species again. Possibly Familiar Chat is a local
migrant, with some birds moving north after the
rainy season: both sightings were made in mid
October, following the rains, when insects are
most plentiful.
Grasshopper Warbler Locustella naevia
On 26 January 2009 at 11.30 hrs, near Sabur
Recreation Centre, Filfil Solomuna (c. 1 5°36’N
38°35’E), at c. 1,300—1,400 m, in an area of open,
ungrazed meadows on a steep hillside with small
bushes, surrounded by broadleaf woodland, I
separately flushed two small brown birds from
the 20-80 cm high grass. Both dived into small
bushes nearby. I was unable to relocate the first
bird, but the second remained for 20 minutes in
a very small bush, which I approached to within
10 m. Immediately, I noticed diagnostic dark
markings on the pale undertail-coverts, as the bird
cocked its tail and turned away. I also noted the
generally brown upperparts with black streaking
on the mantle, crown and wings, slight streaking
on the breast below a pale throat, and dark face
with no clear supercilium. These features are
consistent with Grasshopper Warbler. I obtained
several reasonable photographs, which confirm
the bird’s identity (Fig. 7).
I suspect that the other bird I flushed, as
well as a third I briefly saw the same day, were
also Grasshopper Warblers. Possibly the area is
a wintering ground for this Palearctic migrant.
(See also Anderson & Berhane (submitted) for
more about the importance of this site.) There
are no previous records in Eritrea of Grasshopper
Warbler, which is an uncommon winter visitor to
Ethiopia, with only 13 records mentioned by Ash
& Atkins (2009).
Note
This paper originally also included a record
of Great Cormorant Phalacrocorax carbo from
Mai Nefe Reservoir, near Asmara (15°15’34”N
38°47’47”E) on 3 February 2009. Recently,
however, two records of Great Cormorant have
been published, albeit undated (De Marchi et
al. 2009). Giuseppe De Marchi (pers. comm.)
informed me that these concerned a dead bird on
NN045 Island in Howakil Bay on 30 December
2002 and a live bird in shallow water in the Gulf
of Zula on 7 January 2006. My record from Mai
Nefe thus becomes the third confirmed record of
Great Cormorant in Eritrea.
Acknowledgements
Thanks to John Ash, John Atkins, Nigel Redman,
Nigel Cleere, Nik Borrow and John Caddick for their
assistance in identifying some of the above species
from photographs and field notes, to Dawit Berhane
and Giuseppe De Marchi for details of their Great
Cormorant records, and to Steve Smith for his support
and advice concerning the Cape Eagle Owl. Nigel
Redman commented on a draft of this paper.
References
Anderson, J. & Berhane, D. (submitted) Recent
observations on the Abyssinian endemic species in
Eritrea. Bull. ABC.
Ash, J. & Atkins, J. 2009. Birds of Ethiopia and Eritrea:
An Atlas of Distribution. London, UK: Christopher
Helm.
De Marchi, G., Chiozzi, G. & Semere, D. 2009. Wings
over the Red Sea — the birds of the Eritrean Islands.
Natura, Riv. Sci. Natur. 99(2) Suppl.: 1-128.
Redman, N., Stevenson, T. & Fanshawe, J. 2009. Birds
of the Horn of Africa. London, UK: Christopher
Helm.
Sinclair, I. & Ryan, P. 2003. Birds of Africa South of the
Sahara. Cape Town: Struik.
c/o 5 Wilton House , St. Paul’s Cray Road, Chislehurst,
Kent BR7 6QG, UK. E-mail: jasonandersonl@gmail.
com
Received 19 August 2009; revision accepted 9 January
2010 .
70 -Bull ABC Vol 17 No 1 (2010)
First records of eight bird species for Eritrea: Anderson
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Bull ABC Vol 17 No 1 (2010) -71
Recent bird records from Fogo, Cape Verde Islands
Ruben Barone' and Jens Herinfr
Observations recentes de Fogo, lies du Cap-Vert. Des donnees sont presentees concernant 12 especes
d’oiseaux observees a Fogo, lies du Cap-Vert, parmi lesquelles deux premieres mentions pour 1 ile
(Chevalier gambette Tringa totanus et Hirondelle de fenetre Delichon urbicum ), les premieres donnees de
nidification du Martinet du Cap-Vert Apus alexandri et les premieres observations babies du Phaeton a bee
rouge Phaethon aethereus indiquant la nidification probable de celui-ci. Des informations sont egalement
presentees sur d’autres taxons mal connus a Fogo, tels que certaines especes pelagiques et l’Effraie des
clochers Tyto alba detorta.
Summary. We present data on 12 bird species observed on Fogo, Cape Verde Islands, among them two
first records for the island (Common Redshank Tringa totanus and Common House Martin Delichon
urbicum ), the first breeding records of Cape Verde Swift Apus alexandri and the first reliable observations
of Red-billed Tropicbird Phaethon aethereus indicating probable breeding. Information on other taxa poorly
known on Fogo, such as some pelagic seabirds and Barn Owl Tyto alba detorta, is also given.
F ogo, one of the Cape Verde Islands, is situated
in the leeward group (‘Ilhas do Sotavento’),
c.724 km from the African continent. With
a surface area of 478 km 2 , the highest peak
(Pico Novo) reaches 2,829 m (Michell-Thome
1976). Its landscape is characterised by an active
volcano (which last erupted in April 1995) and an
impressive caldera rim c. 1,000-m high, a rugged
coast with vertical cliffs that rise up to 200 m,
many small and medium-sized volcanoes, lava
plains and a few steep gorges. Large areas are
cultivated and/or used as pasture. The remaining
original vegetation is mainly confined to the
Bordeira’ and ‘Cha das Caldeiras’ areas, in cliffs
and gorges and in volcanic badlands (see Ribeiro
1954, Mitchell-Thome 1976, Diniz & Matos
1987, Correia 1996, Day et al. 1999, Leyens
2002, Olehowski et al. 2008 and Foeken et al.
2009 for more information on the geology,
geography, climate and vegetation).
Few ornithologists have studied the avifauna
of this island. Among them are Leonardo Fea
{in Salvadori 1899), Jose G. Correia {in Murphy
1924), de Naurois (1969, 1987, 1994), Jaime
Vieira dos Santos {in Frade 1976), Norrevang
& Hartog (1984), de Bruyn & Koedijk (1990),
Flazevoet (1995, 1998, 2003), Barone (1997),
Geniez & Lopez-Jurado (1998), Ratcliffe et al.
(2000), Jens Hering (Hering & Hering 2005,
Hering 2008, Hering & Fuchs 2008, 2009) and
Jesus et al. (2009).
During five ornithological trips to Fogo in
2004-06, we observed several bird species not
reported previously, and some others for which
there are only a limited number of observations.
Local information on breeding birds was mainly
collected by RB. Dates of our visits are as follows:
18-21 October 2004 (JH & H. Hering), 5-10
February 2005 (RB), 18-29 September 2005
(RB), 28-30 December 2005 and 4-5 January
2006 (JH & H. Hering) and 19 October-1
November 2006 (JH & E. Fuchs). Information
on the Cape Verde Cane Warbler Acrocephalus
brevipennis (Hering & Hering 2005, Hering
2008, Hering & Fuchs 2008, 2009) and the diet
of the Barn Owl Tyto alba (Siverio et al. 2008) has
been published elsewhere.
Methods
RB carried out a total of 24 diurnal point counts
of 20-60 minutes (both visual and aural, three of
them repeated 2-4 times), in different habitats
across the island (sea cliffs, lowland xerophytic
vegetation, cultivation, inland cliffs, gorges and
high-mountain vegetation), largely following
the recommendations of Bibby et al. (1992).
Observations focused on seabirds, herons, raptors,
swifts and some passerines, using both binoculars
and a telescope. In addition, 14 gorges and inland
cliffs, suitable as habitat for diurnal raptors and
Barn Owl, were explored, and random walks in
the lower, middle and higher parts of the island
were performed. These were complemented by
five nocturnal listening stations of 20 minutes
(one of them repeated four times) in the Mosteiros
area, Bangaeira (Cha das Caldeiras) and the main
72 -Bull ABC Vol 17 No 1 (2010)
Recent bird records from Fogo, Cape Verde Islands: Barone & Hering
town, Sao Filipe, aimed at detecting pelagic
seabirds approaching land and Barn Owls. JH
iocused his attention mainly on the Cape Verde
Cane Warbler, conducting listening point counts
and line transects to detect the species during
its breeding season (see Hering & Hering 2005,
Hering 2008, Hering & Fuchs 2008, 2009).
Results and Discussion
We have selected data on 12 species observed
on Fogo, including two new island records of
migrants (Common Redshank Tringa totanus and
Common House Martin Delichon urbicum) and
observations concerning breeding taxa, namely
Cape Verde Swift Apus alexandri (first breeding
records for the island), Red-billed Tropicbird
Phaetbon aethereus (first reliable observations),
several pelagic seabirds and Barn Owl Tyto alba
detort a.
Fea’s Petrel Pterodroma feae
At least one was seen flying over open sea, more
than 500 m otf Mosteiros, in the north of the
island, by RB on 6 February 2005, at 16. 20-
lb. 25 hrs. Two were seen from the same site, at
17.20-17.55 hrs the next day.
This species breeds at several localities on
Fogo, mainly in the Cha das Caldeiras area above
1,600 m (Hazevoet 1995, Ratcliffe et al. 2000,
Jesus et al. 2009), but there are few published
sightings from adjacent seas. We were informed
of a previously unknown colony on Monte Vaca,
on the west side of the island, but it was not
possible to verify this. Following recent genetic
and morphometric studies, the nominate Cape
Verdes’ population has been proposed as a species
different from the birds of Bugio, in the Desertas
Islands, Madeira, which are now referred to as P.
deserta in some literature (Jesus et al. 2009).
Cape Verde Shearwater Calonectris edwardsii
Six were observed flying at sea late in the evening
of 18 September 2005 from Porto de Vale dos
Cavaleiros, in the west of the island. In the
afternoon of 20 September 2005, two were seen
flying c.500 m off Mosteiros, with at least three
on 21 September. We obtained reliable local
information about the breeding of this species
on the marine cliffs below Corvo, in the north-
east. At Alcatraz, in the south-east, we saw some
possible breeding sites, indicated by droppings at
the entrance of several crevices in the marine cliffs,
on 24 September 2005.
Despite the fact that Fogo possesses many
seemingly suitable breeding sites, there are no
breeding records of Cape Verde Shearwater (de
Naurois 1994, Hazevoet 1995). This is likely due
to the lack of a detailed inspection of its sea cliffs.
Bourne (1955) included this species in his list of
birds of the islands as it had been ‘reported by a
reliable inhabitant’.
Cape Verde Little Shearwater Puffinus
(, assimilis ) boydi
On several occasions on 5-8 February and 20-23
September 2005, we heard birds calling at night
while approaching the cliffs behind Mosteiros,
where there seems to be a breeding colony.
Maximum number of contacts included ten heard
between 19.45-22.15 hrs on 21 September, and
13 between 21.30-22.00 hrs on 22 September.
At times, two birds were heard simultaneously,
and sometimes males and females could be
distinguished due to their different vocalisations,
as pointed out by James & Robertson (1985)
for Puffinus ( assimilis ) baroli and by Robb et al.
(2008) for the Cape Verdean endemic. Calls were
clearly different from those of P. (a.) baroli (, cf
Robb et al. 2008). During the late afternoon of 21
September 2005, one or two birds were observed
at sea off Mosteiros.
The same locality is mentioned by Hazevoet
(1995), who heard several birds there in April
1990. The only known breeding records are
from Ilheu de Cima, Branco, Raso, Santiago and
Boavista islands (Hazevoet 1995).
Red-billed Tropicbird Phaetbon aethereus
Three, all apparently adults, were seen approaching
the coastal cliffs of Ponta Lenha-Baia da
Reconhigao, in the south-west (near ‘Santuario de
Nossa Senhora do Socorro’), in the afternoon of
19 September 2005 by RB. One entered a hole in
the basaltic cliffs, but left after four minutes; later
the same or another individual visited a different
cavity and stayed longer. These observations may
indicate breeding at this locality.
To date, Red-billed Tropicbird had not been
definitely reported on Fogo, although it had
occasionally been observed close to the coast
Recent bird records from Fogo, Cape Verde Islands: Barone & Hering
Bull ABC Vol 17 No 1 (2010) -73
(T. Leyens pers. comm.) and Bourne (1955)
mentioned it for the island based on information
by a ‘reliable inhabitant’. Breeding has been
confirmed on Sal, Boavista, Santiago and Brava,
and on Raso and Rombos islets (Hazevoet 1995,
1998), and it probably breeds on Santo Antao as
well (Palacios & Barone 2001, Hazevoet 2003). It
has been observed recently on Ilheu dos Passaros,
Sao Vicente (Hazevoet 2010).
Cattle Egret Bubulcus ibis
We found a roost of this species in a tree at
Mosteiros. On 5 February 2005 there were c.125
birds, with 152 there the next day between
17.50-18.55 hrs. In September 2005 there were
no Cattle Egrets at all on the island, and in
December 2005 and October 2006 only small
numbers were recorded, the maximum being 12,
south of Mosteiros, on 19 October.
This egret is present in the Cape Verdes
mainly in December-April (Hazevoet 1995), with
some breeding records from Santiago in the 1960s
(Bannerman & Bannerman 1968, de Naurois
1969). Our roost seems to be one of the largest in
the archipelago, although 540 birds were counted
near the sewage farm of Sao Vicente on 9-10
March 1996 (Hazevoet 1997). A roost of 1,344
birds was found on Santiago in March 2008 and
a breeding colony containing c.6 0 nests occurred
on Boavista in 2004 (Hazevoet 2010).
Grey Heron Ardea cinerea
One flew above the coastal cliffs of Fajazinha,
north-west of Mosteiros, on 7 February 2005,
an immature was seen above Mosteiros on 20
September 2005, and another bird along the shore
at Mosteiros, on 24 and 29 October 2006.
Hazevoet (1995) mentioned the existence of
<10 records from Fogo, Santo Antao and Sal, but
there has been an increase in observations on the
last two islands during the past decade and even
some breeding records on Santo Antao (Hazevoet
1997, Barone & Delgado 1999, Palacios &
Barone 2001, Hazevoet 2003). Fogo does not
offer suitable habitat for this heron, which prefers
coastal plains and lagoons.
Sanderling Calidris alba
Two were observed on a dark sandy beach close
to Porto de Vale dos Cavaleiros on 18 September
Legend to figures on opposite page
Figure 1. Satellite image of Fogo Island, Cape Verde
Islands, with the main localities cited in the text
(modified after a NASA photograph).
Image satellite de file de Fogo, lies du Cap-Vert, avec les
principals localites citees dans le texte (modifiee d apres
une photo de la NASA).
Figure 2. Fajazinha, in the north of Fogo; one of the best
places for waders on the island (R. Barone)
Fajazinha, dans le nord de Fogo ; un des meilleurs
endroits de File pour les limicoles (R. Barone)
Figure 3. Small canyon between Fajazinha and
Sambango; within its interior two nests of Cape Verde
Swift Apus alexandri were discovered (R. Barone)
Petit canyon entre Fajazinha et Sambango, ou deux
nids du Martinet du Cap-Vert Apus alexandri ont ete
decouverts (R. Barone)
Figure 4. Mosteiros: from the coast several pelagic
seabirds were seen and in the cliffs behind the town Cape
Verde Little Shearwater Pujfinus ( assimilis ) boydi and
Barn Owl Tyto alba detorta were heard (J. Hering)
Mosteiros : plusieurs especes d’oiseaux pelagiques y ont
ete vus a partir de la cote, tandis que le Puffin semblable
du Cap-Vert Pujfinus ( assimilis ) boydi et FEffraie des
clochers Tyto alba detorta ont ete entendus dans les
falaises derriere la ville (J. Hering)
Figure 5. Pai Antonio is one of the main tropical
agriculture areas in the Cape Verde Islands. Barn Owl
Tyto alba detorta was found at this site, which is one
of the most important for Cape Verde Cane Warbler
Acrocephalus brevipennis in the archipelago (J. Hering)
Pai Antonio est une des zones principales d'agriculture
tropicale dans les lies du Cap-Vert. L’Effraie des clochers
Tyto alba detorta a ete trouvee sur ce site, qui est un des
plus importants de l’archipel pour la Rousserolle du Cap-
Vert Acrocephalus brevipennis (J. Hering)
Figure 6. Partial view of the caldera rim of Cha das
Caldeiras, situated in the centre ol the island, with two
villages, Portela and Bangaeira, at its base. This is one
of the most important breeding sites of Fea’s Petrel
Pterodroma feae (J. Hering)
Vue partielle du bord de la caldera de Cha das Caldeiras,
situee au centre de File, avec deux villages, Portela et
Bangaeira, a son pied. Ceci est un des sites de nidification
les plus importants du Petrel gongon Pterodroma feae (J.
Hering)
Figure 7. Coastal cliffs close to Santuario de Nossa
Senhora do Socorro, in the south-west, where Red-billed
Tropicbird Phaethon aethereus was observed (R. Barone)
Falaises pres de Santuario de Nossa Senhora do Socorro,
dans le sud-ouest, ou le Phaeton a bee rouge Phaethon
aethereus a ete observe (R. Barone)
74 -Bull ABC Vol 1 7 No 1 (2010)
Recent bird records from Fogo, Cape Verde Islands: Barone & Hering
3 ^ Samban5&4^
• v- .. 'wtbsieiros
.Pdota da Pai Antonio
ajazinha
Salina
Corvo
Bangaeira
Mira-Mira
Portela
Sao Lourenco
P. Vale dos
Cavaleiros
ao Filipe
Nossa Sra"
do Socorro
Y
Recent bird records from Fogo, Cape Verde Islands: Barone & Hering
Bull ABC Vol 17 No 1 (2010) -75
2005. On 25 September, two, possibly the same
birds, were on a similar beach between Porto
de Vale dos Cavaleiros and Sao Filipe. Four
were on Ponta da Salina on 30 December 2005
with a maximum of three on Porto de Vale dos
Cavaleiros the same day.
This wader is more common on the eastern
islands of Sal, Boavista and Maio (Flazevoet 1995,
Barone & Delgado 1999, Barone et al. 2001),
which possess extensive flat coastal habitats and
lagoons, although it occurs locally throughout the
archipelago. Our records suggest that Sanderling
is probably a regular migrant visitor in small
numbers on Fogo.
Common Redshank Tringa totanus
An immature was observed at the shore of
Fajazinha on 21 September 2005.
This is the first record for Fogo. There are
previous observations from Sao Vicente, Sal,
Boavista, Maio and Santiago (Hazevoet 1995,
Barone et al. 2001, Hazevoet 2003).
Common Sandpiper Actitis hypoleucos
We have several records from different months,
all of them along the northern shore. One east of
Mosteiros and three at Fajazinha on 6-7 February
and 21 September 2005; three at Mosteiros on 29
December 2005, and one there next day; finally,
two at Mosteiros on 24 October 2006, with three
there five days later.
There are few published records for Fogo
(Hazevoet 1995, Barone 1997). Our observations
suggest that it is a regular migrant visitor to this
island, as well as to the rest of the archipelago
(Hazevoet 1995).
Cape Verde Barn Owl Tyto alba detorta
One was calling above Mosteiros at 23.36 hrs on
6 February 2005. The next day, we discovered
two cavities used by the species on the Sambango
volcano, in the north. The first, which contained
bones ol House Mouse Mus musculus and some
insect remains, was old, but the second (situated
at 20 m), where we collected c.20 pellets, was still
in use. On 9 February we found five pellets at
Ribeira Gomes, near Mira-Mira, on the west side
of the island, at c.700 m (see Siverio et al. 2008 for
analysis of the pellets). Other records include: a
bird calling at night above Mosteiros, at the same
place as in February, on 20 September 2005; a
new pellet, containing many insect remains, found
below the roost on Sambango on 21 September;
one soaring in a cultivated area between Cova
Lima and Cutelo Alto, in the north of the island,
on 20 October 2006; one perched in daylight in
a mango tree Mangifera indica at the outskirts
of Pai Antonio, in the north, and another on
the roofs of the southern part of Mosteiros on
28 October. The diurnal search for the species
in several gorges, small canyons and inland cliffs
in some other northern (between Mosteiros and
Fajazinha), central (Cha das Caldeiras area) and
western (Sao Filipe-Sao Louren^o) areas of the
island was unsuccessful.
These data suggest that Barn Owl is a locally
common species on Fogo, as also indicated by
information obtained from local people. The
only previous records were published by Hazevoet
(1995), who saw it several times in June 1989 and
April 1 990, indicating its probable breeding on this
island. Previously Bourne (1955) mentioned that
the species was ‘reported by a reliable inhabitant’.
Our observations, especially the finding of fresh
pellets and birds calling at night with territorial
behaviour, are proof of its establishment on Fogo.
To date, breeding of the Barn Owl has been
confirmed on Santo Antao, Santa Luzia, Branco,
Boavista, Maio, Santiago, Ilheu Grande (Rombos)
and Brava, but the species is also present on Sao
Vicente, Raso and Sao Nicolau (Siverio et al.
2007). Furthermore, there is fossil evidence for its
presence on Sal (Boessneck & Kinzelbach 1993).
Cape Verde Swift Apus alexandri
This endemic was observed in many localities,
mainly over coastal and inland cliffs and steep
gorges. It exhibited some nocturnal activity, as we
heard one or two birds at night above Mosteiros
on 6 February 2005, a behaviour also recorded in
similar species like the Plain Swift Apus unicolor
(Rodriguez 1988). The largest groups consisted
of 20-21 birds at the cliffs near Porto de Vale
dos Cavaleiros on 18 September 2005 and more
than 100 at Cha das Caldeiras on 4 January 2006.
However, the most interesting records concern the
discovery of several nests. On 7 February 2005
three were seen approaching the cliffs west of
Fajazinha, one of which tried to enter a small hole,
and a nest (probably in use, as it had droppings
at the entrance) was discovered in the same area.
76 -Bull ABC Vol 17 No 1 (2010)
Recent bird records from Fogo , Cape Verde Islands: Barone & Hering
1 he same day, two other nests were found in a
small canyon situated in the interior, at 60 m,
between Fajazinha and Sambango. One of them,
at c . 5 m height, was occupied, with another, at
3.5 m, nearby. Bones of Cape Verde Swift were
lound in Barn Owl pellets collected at Sambango
in February 2005 (Siverio et al. 2008).
These are the first breeding records of Cape
Verde Swift on Fogo. Previously, there were
nesting data only for Brava and Sao Nicolau, but
its breeding was considered likely on Santiago,
Fogo and Santo Antao as well (Hazevoet 1995).
Listed as breeding on all of the islands in the
archipelago by de Naurois (1994).
Common House Martin Delichon urbicum
One was observed near Bangaeira, in the Cha das
Caldeiras area, on 5 January 2006 by JH.
Hazevoet (1995) mentioned that this species
had not been reported from Fogo.
Acknowledgements
JH acknowledges the collaboration of Heidi Hering and
Elmar Fuchs during the field work. Dr Berthold Seibert
and his wife Rosi are thanked for their company and
friendship during some of RB’s trips. Guillermo Garcia
located some references on geology and geography
of the island, and assisted with the toponymy of the
localities, whilst Dr Peter Sziemer provided additional
literature. Dr Cornelis J. Hazevoet, Miguel Fernandez
del Castillo and Ana Monedero read and corrected the
first draft, and Ron Demey proffered editorial advice.
Leopoldo Moro scanned some original slides of bird
habitats, Miguel Angel Noriega placed the localities on
the satellite image of Fogo and finally, Dr Juan Jose
Bacallado helped RB with a small, personal fund.
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Zino, E. 2000. The status and distribution of Fea’s
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“C/. Eduardo Zamacois, 13-3°A, 38005 Santa Cruz de
Tenerife, Canary Islands, Spain. E-mail: makaronesia68@
yahoo, es.
b CI. Wolkenburger Strafe 11, D-09212 Limbach-
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Received 4 August 2009; revision accepted 29
September 2009.
78 -Bull ABC Vol 17 No 1 (2010)
Recent bird records from Fogo, Cape Verde Islands: Barone & Hering
The separate African winter quarters of Pied Flycatcher
Ficedula hypoleuca and Collared Flycatcher F. albicollis
Robert J. Dowsett
Le Gobemouche noir Ficedula hypoleuca et la Gobemouche a collier F. albicollis ont des quartiers
d hiver africains bien separes. Goodenough et al. (2009) ont ecrit que le Gobemouche noir Ficedula
hypoleuca et son proche cousin le Gobemouche a collier F. albicollis hivernent en sympatrie dans des pays
comme le Tchad et le Nigeria, mais c est incorrect. Le Gobemouche noir hiverne principalement dans les
forets claires soudaniennes de la Sierra Leone au Cameroun, tandis que le Gobemouche a collier hiverne
dans les forets claires de la region zambezienne au sud de l’Equateur.
Summary. 1 he claim that Pied Flycatcher Ficedula hypoleuca and its close relative the Collared Flycatcher
F. albicollis winter sympatrically in countries such as Chad and Nigeria’ (Goodenough et al. 2009) is not
tiue. Pied Flycatcher winters mainly in the Sudanian woodlands from Cameroon west to Sierra Leone, but
Collared Flycatcher does so in the Zambezian woodlands south of the equator.
I n their discussion of factors relevant to the
conservation of Pied Flycatchers Ficedula
hypoleuca , Goodenough et al. (2009) claim that
this species and its close relative the Collared
Flycatcher F. albicollis ‘winter sympatrically in
countries such as Chad and Nigeria (Dowsett
1993, Elgood et al. 1994)’. This is untrue, and is
not what was shown by Dowsett (1993).
A literature search has produced many
specimen and correctly identified sight records
of Ficedula flycatchers in sub-Saharan Africa.
To these have been added my own observations
from several countries in which these two species
occur in winter or on passage, from western
Mali to northern Cameroon for Pied Flycatchers,
and north-east Nigeria to southern Zambia for
Collared Flycatchers.
Winter distribution of Pied and Collared
Flycatchers
1 Goodenough etal. (2009) were perhaps influenced
by the fact that Elgood et al. (1994) wrote of
Collared Flycatcher in Nigeria ‘uncommon...
Sep-Mar’, which implies a presence throughout
that period. This echoed Elgood et al. (1966),
who considered that it is ‘probably a regular
winter visitor’. Elowever, the few records of
Collared Flycatcher in Nigeria all fall between 13
September and 1 November, except for one bird
which spent the period 23 February-23 March at
Vom (Smith 1966). There is a handful of records
from neighbouring Chad (11 September-19
October and 1 1-13 April: Salvan 1968). For both
Nigeria and Chad, Dowsett (1993) made it clear
that the species occurs only on passage.
Pied Flycatchers too are known only on
passage through Chad (7 September to the first
half of October and 29 March-10 April: Salvan
1968, Newby 1980), which is at the eastern limit
of the species’ migration. But they do winter
in considerable numbers in Nigeria. Elgood et
al. (1994) reported them between October and
April, but extreme dates are in fact 17 September
(Malamfatori, Lake Chad: Dowsett 1969) and
23 May (Vom: Smith 1966). Pied Flycatchers
winter south in Nigeria from 11°N (Falgore,
January: Wilkinson & Beecroft 1985; Zaria, 27
February: Fry 1965), mostly between 07°N and
10°N. There are few records from the coastal
zone of Nigeria (e.g. Lagos: Forrester 1971, Gee
& Fleigham 1977). In its overall wintering area
(essentially Cameroon west to Mali, south to
Sierra Leone: Serle 1949; pers. obs.) the species
frequents especially the Sudanian woodlands, less
often clearings or the edge of forest. In the Sahel
it occurs only on passage, and then there is a
preponderance of autumn (southbound passage)
records at several localities; e.g. at Malamfatori,
at least 14 between 17 September and 9 October
(Dowsett 1969), but only three on northbound
passage (early April to 3 May: Dowsett 1968,
Sharland 1969). In contrast, with the drying out
of the Lake Chad area, Gustafsson et al. (2003) in
the period 1997-2000 had only a single autumn
record at Malamfatori (8 September), and none at
all in spring. Near Jos (2001-09), M. Stevens (in
African winter quarters Pied and Collared Flycatchers: Dowsett
Bull ABC Vol 17 No 1 (2010) -79
15W 10W 5W 0 5E 10E 15E 2 0E 2 5E 30 E 35E 40E
Figure 1. Records (mapped by degree square) of Pied Flycatchers Ficedula hypoleuca (black squares), Collared
Flycatchers F. albicollis (open squares) and Semi-collared Flycatchers F. semitorquata (black dots). Localities at which
two species occur are denoted by ‘pied’ symbols.
Distribution (par carres d un degre de latitude-longitude) des Gobemouches noirs Ficedula hypoleuca (carres noirs), a
collier F. albicollis (carres creux) et a demi-collier F. semitorquata (points noirs). Les localites oil se rencontrent deux
especes sont indiquees par un symbole noir et blanc.
lift. 2009) ringed 100 in October compared to 45
in March-April.
In contrast to Pied Flycatchers, Collared
Flycatchers winter south of the equator, in the
Zambezian woodlands, centred on Zambia and
Malawi in particular (Moreau 1972, Dowsett-
Lemaire & Dowsett 2006, Dowsett et al. 2008).
Fig. 1 shows the distribution of these two species,
and the separation of the centres of distribution is
clear, with the Central African rain forest largely
avoided. Records of Semi-collared Flycatchers
F. semitorquata are also mapped; as they are
difficult to separate, some records might have
to be reassessed, but it does seem that their
winter distribution is near the equator, centred on
Uganda and western Kenya (e.g. Pearson 1998,
and references therein).
Future workers are likely to be misled by
the published statement in such an authoritative
journal as Ibis , but the editor declined to publish
this clarification there.
Acknowledgements
I thank Peter Jones, David Pearson and Matt Stevens
for their helpful comments on the manuscript.
References
Dowsett, R. J. 1968. Migrants at Malam’fatori, Lake
Chad, spring 1968. Bull. Nigerian Orn. Soc. 5:
53-56.
Dowsett, R. J. 1969. Migrants at Malam’fatori, Lake
Chad, autumn 1968. Bull. Nigerian Orn. Soc. 6:
39-45.
Dowsett, R. J. 1993. Afrotropical avifaunas: annotated
country lists. Nigeria and Chad. Tauraco Res. Rep.
5: 69-77 & 103-108.
Dowsett, R. J., Aspinwall, D. R. & Dowsett-Lemaire,
F. 2008. The Birds of Zambia. An Atlas and
Handbook. Liege: Tauraco Press & Aves.
80 -Bull ABC Vol 17 No 1 (2010)
African winter quarters Pied and Collared Flycatchers: Doivsett
Dowsett-Lemaire, F. & Dowsett, R. J. 2006. The Birds
of Malawi. An Atlas and Handbook. Liege: Tauraco
Press & Aves.
Elgood, J. H., Sharland, R. E. & Ward, P. 1966.
Palaearctic migrants in Nigeria. Ibis 108: 84-116.
Elgood, J. H., Heigham, J. B., Moore, A. M„ Nason,
A. M., Sharland, R. E. & Skinner, N. J. 1994.
The Birds of Nigeria: An Annotated Check-list.
BOU Check-list No. 4. Second edn. Tring: British
Ornithologists' Union.
Forrester, M. F. 1971. The birds of Ikoyi, Lagos. Bull.
Nigerian Orn. Soc. 8: 13-21.
Fry, C. H. 1965. The birds of Zaria. IV — Residents,
vagrants and check-list (Passerines). Bull. Nigerian
Orn. Soc. 2: 91-102.
Gee, J. & Heigham, J. 1977. Birds of Lagos, Nigeria.
[Part 2], Bull. Nigerian Orn. Soc. 13: 103-132.
Goodenough, A. E., Elliot, S. L. & Hart, A. G.
2009. I he challenges of conservation for declining
migrants: are reserve-based initiatives during the
breeding season appropriate for the Pied Flycatcher
Ficedula hypoleuca?. Ibis 151: 429-439.
Gustafsson, R., Hjort, C., Ottosson, U. & Hall, P.
2003. Birds at Lake Chad and in the Sahel of NE
Nigeria 1997-2000. Ottenby: Lake Chad Bird
Migration Project.
Moreau, R. E. 1972. The Palaearctic-African Bird
Migration System. London, UK: Academic Press.
Newby, J. E. 1980. The birds of the Oadi Rime —
Ouadi Achim Faunal Reserve, a contribution to the
study of the Chadian avifauna. [Part 2.] Malimbus
2: 29-50.
Pearson, D. J. 1998. Pied Flycatcher Ficedula hypoleuca
at Kakamega Forest — a readmission to the East
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Salvan, J. 1968. Contribution a Fetude des oiseaux du
Tchad. [Part 4.] Oiseau & R.F.O. 38: 249-273.
Serle, W. 1949. Notes on the birds of Sierra Leone.
[Part 3]. Ostrich 20: 70-85.
Sharland, R. E. 1969. Mallam Fatori, spring 1969.
Bull. Nigerian Orn. Soc. 6: 98-101.
Smith, V. W. 1966. Autumn and spring weights of
some Palaearctic migrants in central Nigeria. Ibis
108: 492-512.
Wilkinson, R. & Beecroft, R. 1985. Birds in Falgore
Game Reserve, Nigeria. Malimbus 7: 63-72.
Le Pouget, 30440 Sumene, France. E-mail: Dowsett@
aol. com
Received 15 September 2009; revision accepted 20
October 2009.
African winter quarters Pied and Collared Flycatchers: Dowsett
Bull ABC Vol 17 No 1 (2010) -81
First breeding record and passage of
Eurasian Sparrowhawk Accipiter nisus in Libya
Jens Hering ', Elmar Fuchs b and Stefan Brehmef
Premiere mention de nidification et passage de I’Epervier d’Europe Accipiter nisus en Libye. La
decouverte est rapportee de deux nids occupes d’Eperviers d’Europe Accipiter nisus au nord-ouest de
Cyrenaica, Libye, en mai 2008. Le premier etait dans une plantation de pins au nord de Cyrene, pres du
complexe hotelier de Muntasah Shahhat, le second environ 1,2 km au sud-ouest du premier, dans une
zone cloturee ayant l’aspect d un pare. Des plumees contenaient des plumes d une Tourterelle des bois
Streptopelia turtur , d un Coucou gris Cucidus canorus et de 11 passereaux qui se trouvent dans la region
comme especes nicheuses ou de passage. Ceci constitue les premieres mentions de nidification de l’Epervier
d’Europe en Libye. Deux observations en mars 2009 a Wadi Ash Shari, les premieres pour cette espece au
Fezzan, pourraient indiquer que ce rapace est aussi un visiteur hivernal plus frequent qu’on ne le pensait
jusqu’a present.
I n North Africa, Eurasian Sparrowhawk Accipiter
nisus is known to breed in Morocco, Algeria
and Tunisia (race punicus : Orta 1994) and as
a regular passage migrant or winter visitor (the
European nominate race: Isenmann & Moali
2000, Thevenot et al. 2003, Isenmann etal. 2005).
According to Bundy (1976), it is only a winter
visitor to Libya, where it has been infrequently
and irregularly recorded from November to April
in Tripolitania, mainly in the coastal region.
Other sightings confirm the rarity of the species in
this region (Misonne 1973, Brehme et al. 2002).
The few records from Cyrenaica are from the coast
and Jebel Akhdar in November-April. However,
the species is also stated to be occasionally ‘fairly
common' (R. S. M. Green in Stanford 1953,
1954, Latham 1973). In the Libyan Desert there
have been a few spring observations in March and
April (Bundy 1976).
Table 1 . Analysis of the material found in the pluckings at Eurasian Sparrowhawk Accipiter nisus nest sites
near Cyrene, Libya, in May 2008.
Tableau 1. Analyse du materiel trouve dans les plumees aupres des nids d’Eperviers d’Europe Accipiter nisus
pres de Cyrene, Libye, in mai 2008.
Location: A = wood near the Muntasah Shahhat hotel complex, B = wood on the northern periphery of the city of Cyrene. ‘probably part(s) of a plucking.
Location: A = bois pres du complexe hotelier de Muntasah Shahhat, B = bois a la peripherie nord de la ville de Cyrene. ‘faisant probablement partie dune plumee.
Species
Number
Location
Remarks
European Turtle Dove Streptopelia turtur
1
A
Juvenile
Common Cuckoo Cuculus canorus
1
A
2 undertail-coverts, 1 tertial*
Crested Lark Galerida cristata
1
B
Adult, 1 tail feather, 1 secondary*
Tree Pipit Anthus trivialis
1
B
2 tail feathers
Eastern Olivaceous Warbler Hippolais pallida
2
A
warbler Phylloscopus sp.
1
B
1 tail feather*, probably P. collybita
Blackcap Sylvia atricapilla
1
B
Sardinian Warbler Sylvia melanocephala
1
B
Adult male, 1 primary*
Pied Flycatcher Ficedula hypoleuca
1
A
Blue Tit Parus caeruleus
1
A
Spanish Sparrow Passer hispaniolensis or House Sparrow P. domesticus
1
A
3
B
1 adult + 2 juveniles
Chaffinch Fringilla coelebs
10
A
9 juveniles + 1 adult
5
B
4 juveniles + 1 adult
Goldfinch Carduelis carduelis
1
A
Juvenile
82 -Bull ABC Vol 17 No 1 (2010)
Eurasian Sparrowhawk in Libya: Hering et al.
Figure 1 . The pine plantation near the Muntasah
Shahhat hotel complex, Cyrene, Cyrenaica, where the
first nest of Eurasian Sparrowhawk Accipiter nisus was
found, 27 May 2008 (J. Hering)
La plantation de pins pres du complexe hotelier de
Muntasah Shahhat, Cyrene, Cyrenaica, ou le premier nid
d’Epervier d’Europe Accipiter nisus a ete trouve, 27 mai
2008 (J. Hering)
Figure 2. Female Eurasian Sparrowhawk Accipiter nisus
near its nest in the pine plantation near the Muntasah
Shahhat hotel complex, Cyrene, Cyrenaica, Libya, 27
May 2008 (J. Hering)
Epervier d’Europe Accipiter nisus femelle pres de son nid
dans la plantation de pins pres du complexe hotelier de
Muntasah Shahhat, Cyrene, Cyrenaica, Libye, 27 mai
2008 (J- Hering)
Figure 3. Occupied Eurasian Sparrowhawk Accipiter nisus
nest in a pine tree, Muntasah Shahhat hotel complex,
Cyrene, Cyrenaica, Libya, 27 May 2008 (J. Hering)
Nid occupe d’Epervier d’Europe Accipiter nisus dans un
pin, complexe hotelier de Muntasah Shahhat, Cyrene,
Cyrenaica, Libya, 27 mai 2008 (J. Hering)
Figure 4. The pine plantation on the northern periphery
of the city of Cyrene, Cyrenaica, Libya, where the second
nest of Eurasian Sparrowhawk Accipiter nisus was found,
29 May 2008 (J. Hering)
La plantation de pins a la peripherie nord de la ville de
Cyrene, Cyrenaica, Libye, ou le second nid d’Epervier
d’Europe Accipiter nisus a ete trouve, 29 mai 2008 (J.
Hering)
In May 2008 we visited Cyrenaica, where we
concentrated our observations in the north-west.
In a pine plantation of several hectares, at c.600
m, near the Muntasah Shahhat hotel complex,
Cyrene (32°49’N 21°52’E; Fig. 1), on 27 May,
we discovered a Eurasian Sparrowhawk’s nest,
from which the female flushed, uttering loud
alarm calls. The bird was not particularly shy and
permitted us to approach to within 20 m (Fig.
2). The nest, which was lined with white down,
was in a fork on the trunk c. 10 m high and c. 30
m from the forest edge (Fig. 3). We also found
another nest, undoubtedly from the previous year,
in the centre of the small wood c.50 m from the
first. Several moulted feathers belonging to the
female, including four primaries, two secondaries
and a single tail feather, were found on the
Eurasian Sparrowhawk in Libya: Hering et al.
Bull ABC Vol 17 No 1 (2010) -83
forest floor, as well as the remains of 19 birds
of six species of passerines, a European Turtle
Dove Streptopelia turtur and a Common Cuckoo
Cuculus canorus (Table 1), all of which are known
breeding birds or passage migrants in Cyrenaica
(e.g. Bundy 1976).
Two days later, we found a second occupied
nest, c. 1.2 km south-west of the first, in an
enclosed park-like area on the northern periphery
of the city of Cyrene at c.615 m (32°49’N
21°52’E; Fig. 4). It was at a height of c. 13 m,
also in a fork on the trunk, within a veiy sparsely
wooded pine plantation of c . 5 ha. During our
presence the male vocalised continuously. We
found five primaries and a secondary of the female
as well as 12 pluckings of seven locally occurring
songbirds (Table 1).
These two occupied nests at the end of May
agree temporally with the findings of Isenmann &
Moali (2000) and Isenmann etal. (2005), who give
the breeding season for Eurasian Sparrowhawk in
Algeria and Tunisia as mid April to the beginning
of June. Based on habitat in the region, and
possibly also in other suitable areas of Cyrenaica
and Tripolitania, we believe that the Eurasian
Sparrowhawk breeds here, especially where pine
plantations occur.
The present status of this raptor as a rare
visitor to Libya also needs to be questioned.
During an 11 -day visit to Fezzan in March
2009, we saw Eurasian Sparrowhawks twice: on
28th an individual, probably an adult male, flew
over the administrative centre and on 30th an
immature female flew over a cultivated area of
the A1 Dabwat Agricultural Production Project
radial oasis complex, in Wadi Ash Shati (27°38’N
14°08’E) (Hering et al. in prep.). These birds were
probably returning from their winter quarters in
Niger or Chad, of which little is known at present
(cf Brown et al. 1982). These are the first records
for this part of the country.
Acknowledgements
We thank P. Becker for analysis of the pluckings and
T. Kraft and D. Saemann for other assistance. Our
thanks also go to Abdullah Zaied Agilla of the General
Management of Agricultural Production Projects,
Tripoli, who permitted us to conduct field studies in
the Wadi Ash Shati radial oasis complex. Translation of
the manuscript into English was by David Conlin.
References
Brehme, S., Thiede, W. & Borges, E. 2002. Beitrage
zur Vogelwelt Libyens, III: Accipitridae bis
Charadriidae. Ornithol. Mitt. 54: 391-399.
Brown, L. H., Urban, E. K. & Newman, K. 1982. The
Birds of Africa. Vol. 1. London, UK: Academic
Press.
Bundy, G. 1976. The Birds of Libya: An Annotated
Check-list. BOU Check-list No. 1. London, UK:
British Ornithologists’ Union.
Hering, J., Brehme, S. & Fuchs, E. in prep. Beitrag zur
Fruhjahrs-Vogelwelt in West-Libyen.
Isenmann, P. &c Moali, A. 2000. Oiseaux dAlgerie / Birds
of Algeria. Paris: Societe d’Etudes Ornithologiques
de France.
Isenmann, P., Gaultier, T., El Hili, A., Azafzaf,
H., Dlensi, H. & Smart, M. 2005. Oiseaux de
Tunisie / Birds of Tunisia. Paris: Societe d'Etudes
Ornithologiques de France.
Latham, J. J. 1973. Birds of Al Adem, Tobruk, and
adjacent desert areas of Cyrenaica. Roy. Air Force
Ornithol. Soc.J. 8: 24-44.
Misonne, X. 1973. Notes sur les oiseaux hivernant
a Nofilia, Golfe de Syrte, Libye. Gerfaut 63:
211-217.
Orta, J. 1996. Eurasian Sparrowhawk Accipiter nisus.
In del Hoyo, J., Elliott, A. & Sargatal, J. (eds.)
Handbook of the Birds of the World. Vol. 2.
Barcelona: Lynx Edicions.
Stanford, J. K. 1953. Some impressions of spring
migration in Cyrenaica March-May 1952. Ibis 95:
316-328.
Stanford, J. K. 1954. A survey of the ornithology of
northern Libya. Ibis 96: 449-473, 606-624.
Thevenot, M., Vernon, R. & Bergier, P. 2003. The
Birds of Morocco: An Annotated Checklist. BOU
Checklist No. 20. Tring: British Ornithologists’
Union & British Ornithologists’ Club.
" Wolkenburger Strafe 1 1, D-09212Limbach-Oberfrohna,
Germany. E-mail: jenshering. vso-bibliothek@t-online. de
h Hartensteiner Strafe 48a, D-09376 Oelsnitz, Germany.
E-mail: elmar.fuchs@gmx.de
l Gdrschstrafe 47, D-13187 Berlin, Germany. E-mail:
stefan. brehme@klinikum-niederlausitz. de
Received 5 July 2009; revision accepted 11 November
2009.
84 -Bull ABC Vol 17 No 1 (2010)
Eurasian Sparrowhawk in Libya: Hering et al.
Correction of three historical bird records from Libya
Adriano De Faveri" and Nicola Baccetti“
Correction de trois mentions historiques d’oiseaux en Libye. 7 rois specimens collectes par Toschi en
Libye en 1939, s averent avoir ete mal identifies : deux Pouillots fitis Phylloscopus trochilus sont en fair des
Pouillots veloces P. collybita et un traquet libelle comme Traquet motteux Oenanthe oenanthe est un Traquet
du desert O. deserti. Ces mentions constituaient les seuls donnees hivernales pour les especes en question, a
part quelques mentions plus anciennes du Pouillots fitis qui sont probablement egalement erronees. II y a
toutefois des observations hivernales recentes du Pouillot fitis et du 1 raquet motteux dans le pays.
T hree major reviews of Libyan birds have been
published: Zavattari (1934), Toschi (1969)
and Bundy (1976). They contain most details of
the original literature sources and historical skin
collections. Inevitably, they also contain a few
errors and inaccuracies. We found evidence of three
such cases while cataloguing the bird collection
at the Istituto Superiore per la Protezione e la
Ricerca Ambientale (ISPRA; formerly the Istituto
Nazionale Fauna Selvatica) in Ozzano Emilia,
Italy. Here we came across Augusto Toschi's series
of Libyan skins, originally published by Toschi
(1947). Three specimens proved to have been
misidentified by the collector, namely:
• Willow Warbler Phylloscopus trochilus no.
10150, shot February 1939 in the Fezzan.
Correct species: Common Chiffchaff P.
collybita.
• Willow Warbler Phylloscopus trochilus no.
10151, shot 5 February 1939 at Brak, Fezzan.
Correct species: Common Chiffchaff P.
collybita.
• Northern Wheatear Oenanthe oenanthe no.
9996, shot 3 1 January 1 939 at Mizdah, western
Libya. Correct species: Desert Wheatear 0.
deserti , female.
Only the latter two specimens were mentioned
by Toschi (1969) and none were included in
Bundy (1976). According to these authorities,
there are no other winter records of either species
in Libya, apart from a few of Willow Warbler from
December-January taken by previous collectors,
and retained without examination by Toschi
(1969), but these are probably erroneous too
(see, however, Brehme et al. 2002-06 for recent
winter observations of both species). The correct
species are considered to be regular winter visitors,
and are common at this season. The identity of
the remaining 151 preserved specimens (of the
original 154: Toschi 1947) appeared correct, at
least at the species level.
Acknowledgements
Thanks are due to Ron Demey for improving an
earlier draft and to Stefan Brehme for his constructive
comments.
References
Brehme, S., Thiede, W. & Borges, E. 2002-06.
Beitrage zur Vogelwelt Libyens, II— VIII. Ornithol.
Mitt. 54: 202-212, 391-399; 55: 54-66, 277-287;
56: 207-219; 57: 337-345; 58: 194-211.
Bundy, G. 1976. The Birds of Libya: An Annotated
Check-list. BOU Check-list No. 1. London, UK:
British Ornithologists’ Union.
Toschi, A. 1947. Risultati di una escursione zoologica
in Libia (dicembre 1938-febbraio 1939). Riv. Ital.
Ornitol. 17: 1-24.
Toschi, A. 1969. Introduzione alia ornitologia della
Libia. Suppl. Ric. Zool. appl. Caccia, Bologna 6:
1-381.
Zavattari, E. 1934. Prodromo della fauna della Libia.
Pavia: Tipografia gia Cooperativa.
“ISPRA, via Ca’Fornacetta 9, 40064 Ozzano Emilia
BO, Italy.
Received 26 August 2009; revision accepted 1 October
2009.
Correction of three historical bird records from Libya: De Faveri & Baccetti
Bull ABC Vol 17 No 1 (2010) -85
Rock Firefinch Lagonosticta sanguinodorsalis and its
brood parasite, Jos Plateau Indigobird Vidua maryae,
in northern Cameroon
Michael S. L. Mills
L’Amarante de roche Lagonosticta sanguinodorsalis et son parasite, le Combassou de Jos Vidua
maryae , au nord du Cameroun. L'Amarante de roche Lagonosticta sanguinodorsalis est une espece
extremement locale seulement connue avec certitude, avant 2005, des flancs de collines rocheuses et
herbeuses au nord du Nigeria. Recemment, plusieurs observations au nord du Cameroun indiquent que sa
repartition est plus etendue ; ces observations sont recapitulees ici. Le Combassou de Jos Vidua maryae est
un parasite de l’Amarante de roche et etait suppose etre endemique au Plateau de Jos du Nigeria. L auteur
rapporte une observation de mars 2009 dans le nord du Cameroun de combassous en plumage internuptial,
qui imitaient les emissions vocales de l’Amarante de roche. Des sonogrammes de leurs imitations du hote
sont presentes, ainsi que des sonogrammes de cris de P Amarante de roche. Comme il est peu probable
qu’une autre espece de combassou parasiterait un amarante aussi local, il est suppose que ces oiseaux
representent une population auparavant inconnue du Combassou de Jos dans le nord du Cameroun.
R ock Firefinch Lagonosticta sanguinodorsalis
was described only 12 years ago, from the
Jos Plateau in northern Nigeria (Payne 1998).
It belongs to the African/Jameson’s Firefinch
L. rubricata / rhodopareia clade of firefinches
(Payne 2004), and is similar to African Firefinch,
Mali Firefinch L. virata and Chad Firefinch L.
umbrino dorsalis, but differs from these species
in having a reddish back in the male. The
combination of a blue-grey bill, reddish back and
grey crown in the male is diagnostic. Uniquely,
Rock Firefinch was discovered by song mimicry
of its brood parasite, Jos Plateau Indigobird Vidua
maryae. Jos Plateau Indigobird was first found
Figure 1 . Male Rock Firefinch Lagonosticta sanguinodorsalis near Mora, northern Cameroon, on 12 March 2009. Birds
from northern Cameroon may have less extensive grey on the head than birds from the Jos Plateau (Simon Colenutt)
Amarante de roche Lagonosticta sanguinodorsalis male pres de Mora, Cameroun du nord, 12 mars 2009. Les oiseaux du
nord du Cameroun ont peut-etre moins de gris sur la tete que ceux du Plateau de Jos (Simon Colenutt)
86 -Bull ABC Vol 17 No 1 (2010)
Rock Firefinch and Jos Plateau Indigobird in Cameroon: Mills
m.
Jr
01 03 0)
&S 06 07 08 Q«
Turn (*)
11 13 1 J 14
Figure 2. Sonogram of mimicry by Jos Plateau
Indigobird Vidua maryae of the most common
vocalisation ot Rock Firefinch Lagonosticta
sanguinodorsalis , a rapid descending trill of 12-13 notes
per second, recorded near Mora, northern Cameroon, 13
March 2009.
Sonogramme de F imitation du Combassou de Jos
Vidua maryae de remission vocale la plus commune de
1 Amarante de roche Lagonosticta sanguinodorsalis, un
trille descendant rapide de 12—13 notes par seconde,
enregistree pres de Mora, Cameroun du nord, 13 mars
2009.
9 -
8 -
7 -
0 05 0.1 0.15 0 2 0.25 0.3 0 35 0 4 0 45 0 5
Time (s)
9-
8-
7-
! f ri-r t it
2 - / m
1 - *
0 05 o'l 015 02 0 25 0 3 0 35
Time (s)
Figure 3a. Sonogram of mimicry by Jos Plateau
Indigobird Vidua maryae of Rock Firefmch’s Lagonosticta
sanguinodorsalis contact trill, recorded on 12 March 2009,
near Mora, northern Cameroon.
Sonogramme de l imitation du Combassou de Jos Vidua
maryae du trille de contact de l’Amarante de roche
Lagonosticta sanguinodorsalis , enregistree pres de Mora,
Cameroun du nord, 12 mars 2009.
Figure 3b. Sonogram of the contact trill of Rock
Firefinch Lagonosticta sanguinodorsalis, recorded near
Mora, northern Cameroon, 12 March 2009.
Sonogramme du trille de contact de l’Amarante de roche
Lagonosticta sanguinodorsalis , enregistre pres de Mora,
Cameroun du nord, 12 mars 2009.
Figure 4. 1 he non-breeding (presumed) male Jos
Plateau Indigobird Vidua maryae whose mimicry of
Rock Firefinch Lagonosticta sanguinodorsalis vocalisations
are visualised in Figs. 2 and 3a. The whitish bill and
purplish-grey legs are consistent with those of Jos Plateau
Indigobird (Simon Colenutt)
Le Combassou de Jos Vidua maryae presume male
en plumage internuptial dont les imitations des
emissions vocales de l’Amarante de roche Lagonosticta
sanguinodorsalis sont representees par les Figs. 2 et
3a. Le bee blanchatre et les pattes gris pourpre sont
caracteristiques du Combassou de Jos (Simon Colenutt)
in 1968, and initially described as a subspecies
of Dusky Indigobird V. funerea because it was
thought to mimic African Firefinch calls (Payne
1982). Subsequent investigation revealed that it
mimics unique calls and differs in morphology,
although it differs only in size from Jambandu
Indigobird V. raricola , from Barka Indigobird
V. larvaticola by having a slightly darker wing,
and from Quailfinch Indigobird V. nigeriae by
its slightly brighter gloss and larger size (Payne
1996).
At the time of its description, Rock Firefinch
was known mainly from the Jos Plateau in
Nigeria (09°56’N 08°53’E), but also tentatively
from the Mandara Mountains on the border with
Cameroon (11°04’N 13°45’E) and from near
Rano, in Kano State, Nigeria (11°33’N 08°34’E).
Other records of ‘African Firefinch’ from northern
Nigeria were also suspected to belong to the
newly described species, as were records from
northern Benin and Burkina Faso (Payne 2004).
The distribution of Jos Plateau Indigobird was
confined to the Jos Plateau.
Recently, several reports of Rock Firefinch
have come from northern Cameroon, in similar
habitat — bushy and grassy rock)' outcrops (Brandt
Rock Firefinch and Jos Plateau Indigobird in Cameroon: Mills
Bull ABC Vol 17 No 1 (2010) -87
Table 1 . Records of Rock Firefinch Lagonosticta sanguinodorsalis from northern Cameroon
Tableau 1 . Mentions de I’Amarante de roche Lagonosticta sanguinodorsalis du Cameroun du nord
Date
Observer
Details
Locality
Mar 2004
C. Cohen (pers. comm.)
2 probable
20 km north of Maroua
Feb 2005
N. Borrow [in Bull. ABC 12: 179)
1 female
5 km north of Maroua
Mar 2005
A. Riley & R. White [in lift. 2005)
2 birds
north of Maroua
Mar 2005
A. Riley & R. White (in lift. 2005)
12 birds
Lagdo Lake, c.40 km south-east of Garoua
Apr 2006
D. Hoddinott (in lift. 2006)
12 birds
north of Maroua
Mar 2007
M. S. L. Mills (pers. obs.)
c.10 birds
10 km south-west of Mora
Apr 2007
K. Valentine (in lift. 2007)
2 birds
north of Maroua
Oct 2007
C. Artuso (in lift. 2007)
6 birds
north of Mora
Mar 2008
N. Borrow (pers. comm.)
several
5 km north of Maroua
Mar 2008
M. S. L. Mills (pers. obs.)
1 pair
110 south-south-west of Maroua
Mar 2009
M. S. L. Mills (pers. obs.)
20-30 birds
10 km south-west of Mora
& Cresswell 2008) — in the vicinity of Maroua
(10°36’N 14°20’E) and Mora(10°58’N 14°12’E).
The first potential record was by C. Cohen in
March 2004 (pers. comm.), although the first
published record (in Bull. ABC 12: 179) was
from 2003, a sighting by N. Borrow, who found
a single female on a rocky outcrop c . 5 km north
of Maroua. Since then, repeated sightings in the
Mora-Maroua area (Table 1) indicate that this
species is at least fairly common here during the
dry season, and almost certainly a resident breeder.
I have also once recorded birds further south,
nearer Garoua (09°44’N 13°50’E; 110 km south-
southwest of Maroua), also at a rocky outcrop,
although these birds were only seen briefly. A
better sighting would have been preferable to
be certain of their identity, although the only
other possible candidate is Chad Firefinch, which
was recently rediscovered in Cameroon (Voaden
2008). There are also unpublished records of
Rock Firefinch from Lake Lagdo (09°03’N
13°4TE), south of Garoua, <90 km from where
Chad Firefinch was found (see Table 1). These
should be treated as unconfirmed until further
data become available. Rock Firefinches from
Cameroon and the Mandara Mountains appear
to differ slightly from those from the Jos Plateau,
by having less grey on the crown in the male (see
Fig. 1), although the difference is slight and poorly
documented, and their calls are reported to be the
same (Abakala et al. submitted).
Given the relative abundance of Rock Firefinch
in northern Cameroon, and because indigobirds
often show similar distributions to their hosts,
it could be expected that Jos Plateau Indigobird
should occur in Cameroon also. However, few
ornithologists and birders visit northern Cameroon
during or shortly after the rains, when indigobirds
are in breeding plumage and on their songposts.
Indigobirds rarely sing outside the breeding season
and are generally impossible to distinguish in the
field in non-breeding plumage.
On 12 March 2009, I was searching for Rock
Firefinch and other rocky-country birds with
a group of nine other birders, on some rocky
hills just south of Mora, where I had seen Rock
Firefinch in March 2007. Shortly after sunrise I
could hear calls and song of firefinches coming
from the base of the hills, and soon we found
a loose flock of c. 20 Rock Firefinches. While
observing the firefinches, I made recordings of
their contact trills.
After c.30 minutes of observations, I heard
the distant calls of an indigobird Vidua sp. I
scanned the tops of trees in the direction of the
call, and located a non-breeding bird singing from
a Faidherbia albida tree at the base of the rocks,
in the company of at least two other indigobirds.
I quickly moved closer so I could observe their
vocalisations and plumage in more detail. I played
some generic indigobird calls to try to stimulate
singing, and fortunately the birds sang again.
Included in the generic ramble of indigobird
calls was mimicry of at least two different Rock
Firefinch vocalisations, which I recorded using an
Edirol R09 recorder with a Sennheiser MKE400
88 -Bull ABC Vol 17 No 1 (2010)
Rock Firefinch and Jos Plateau Indigobird in Cameroon: Mills
microphone. Recordings were inspected and
sonogiams produced using Raven Lite software
(Cornell Lab of Ornithology 2003-08).
The most common and distinctive call of Rock
Firehnch is described as a rapid descending trill of
12-13 notes per second (Payne 2004). This call,
visualised in a sonogram (Fig. 2), was made by
Jos Plateau Indigobird, and delivered at a rate of
13.6 notes per second (n= 1). A second call, a short
trill, was mimicked by Jos Plateau Indigobird; a
sonogram is presented in Fig. 3a. Analogous calls
by Rock Firefinch were recorded and are presented
as a sonogram in Fig. 3b. Call structure (shape of
notes), rate of delivery and frequency are nearly
identical, although the firefinch trill consisted of
more notes. Male breeding plumage gloss colour
and intensity were not observed, although bill
(whitish) and leg colour (purplish-grey; Fig. 4)
are consistent with Jos Plateau Indigobird. Given
the small range of Rock Firefinch, it is highly
unlikely that another indigobird species parasitises
the population in northern Cameroon. Hence, it
can be safely assumed that these birds represent
a previously unknown population of Jos Plateau
Indigobird in northern Cameroon. Further
investigations during the indigobirds’ breeding
season should enable a better understanding of
the distribution and abundance of Jos Plateau
Indigobird in Cameroon.
Acknowledgements
I thank Hemme Batjes, Andrew Bunting, Simon
Colenutt, Andy Deighton, Martin Kennewell, Ian
Merrill, Jonathan Newman, Volkert van der Willigen
and Barry Wright, who observed the bird with me,
for their patience while I made sound-recordings. Nik
Borrow generously shared information on his records,
and, with Ulf Ottosson, commented on the manuscript.
Bob Payne helped to improve the paper’s contents.
References
Abalaka, J. I., Ottosson, U., Tende, T. & Larson,
K. Submitted. Rock Firefinch Lagonosticta
_ sanguinodorsalis in the Mandara Mountains, north-
east Nigeria: a new subspecies? Bull. ABC.
Brandt, M. J. & Cresswell, W. 2008. Breeding
behaviour, home range and habitat selection in
Rock Firefinches Lagonosticta sanguinodorsalis in
the wet and dry season in northern Nigeria. Ibis
150: 495-507.
Cornell Lab of Ornithology. 2003-08. Raven Lite 1.0.
Ithaca, NY: Cornell Lab of Ornithology.
Payne, R. 1982. Species limits in the indigobirds
(Ploceidae, Vidua) ol West Africa: mount mimicry,
song mimicry, and description of new species. Misc.
Publ., Mus. Zool., Univ. of Michigan 162: 1-96.
Payne, R. 1998. A new species of firefinch Lagonosticta
from northern Nigeria and its association with the
Jos Plateau Indigobird Vidua maryae. Ibis 140:
368-381.
Payne, R. B. 1996. Field identification of the
indigobirds. Bull. ABC 3: 14-25.
Payne, R. B. 2004. Rock Firefinch Lagonosticta
sanguinodorsalis. In Fry, C. H. & Keith, S.
(eds.) The Birds of Africa. Vol. 7. London, UK:
Christopher Helm.
Voaden, N. 2008. Chad Firefinch Lagonosticta
umbrinodorsalis ‘rediscovered’ in northern
Cameroon. Bull. ABC 15: 238-241.
Birding Africa, PO Box 34146, Rhodesgift 7707, Cape
Town, South Africa; Percy FitzPatrick Institute of African
Ornithology, DST/NRF Centre of Excellence, University
of Cape Town, Private Bag X3, Rondebosch 7701,
South Africa; and A. P. Leventis Ornithological Research
Institute, University of Jos, PO Box 13404, Jos, Plateau
State, Nigeria. E-mail: michael@birdmgafrica.com.
Received 25 April 2009; revision accepted 3 November
2009.
Rock Firefinch and Jos Plateau Indigobird in Cameroon: Mills
Bull ABC Vol 17 No 1 (2010) -89
Rufous Fishing Owl Scotopelia ussheri camera-trapped at
midday near Tiwai Island, Sierra Leone
April Conwaf ,b , Sonia Hernandez f and John P. Carroll"
Une Chouette-pecheuse rousse Scotopelia ussheri photographiee a midi par un piege photographique
pres de File de Tiwai, Sierra Leone. Une Chouette-pecheuse rousse Scotopelia ussheri a ete photographiee
a midi par un piege photographique a infrarouges pres de file de Tiwai, Sierra Leone, le 16 juin 2009.
Ceci est apparemment la premiere fois que cette espece a ete photographiee dans la nature. Curieusement,
l’oiseau semblait etre actif pendant la journee.
A s part of a study on Pygmy Hippopotamus
Choeropsis liberiensis , near-infrared digital
camera-traps were placed on and around Tiwai
Island, Sierra Leone (07°33’N 1 1°19’W), between
November 2008 and June 2009. Cameras were set
to take a single photograph followed by another
automatically after ten seconds; the cameras could
then not be triggered for a further 60 seconds.
Cameras were moved to different locations after
each two-week sampling period. On 7 June, two
cameras were placed on Tagati Island, a small
island of <1 km 2 , west of Tiwai.
On 16 June, four photographs of an owl were
taken by a camera facing a seasonal inlet on the
west side of Tagati. The first two (one of which
is reproduced here: Fig. 1) show the owl on
the ground near the inlet, facing away from the
camera at 11.53 hrs. In the third photograph the
owl is landing on a Raffia Palm Raphia vinifera at
12.02 hrs (Fig. 2). In the last picture, the facial
disk is partially visible (Fig. 3). Although the owl
remained in the field of view of the camera for
c. 10 minutes, it may not have moved enough to
trigger the camera until it flew off.
The orange-rufous plumage and the plain
upperparts identify it as a Rufous Fishing Owl
Scotopelia ussheri\ the only confusion species, Pel’s
Fishing Owl S. peli , has barred upperparts (Borrow
& Demey 2001). Both species are known to occur
at Tiwai Island (R. Demey in Bull. ABC 15; 275
and in litt. 2009). To our knowledge Rufous
Fishing Owl has never before been photographed
in the wild. The ecology and biology of this Upper
Guinea forest endemic are largely unknown.
Although most owl species are nocturnal or
crepuscular, some are also diurnal (Marks et al.
1999). The three species of African fishing owls
Scotopelia , however, are all considered to normally
hunt at night (Konig & Weick 2008), although
Pel’s Fishing Owl is reported to be occasionally
active in daylight when stressed by food scarcity
due to rivers drying up (Kemp 1988). It is
Figures 1-2. Rufous Fishing Owl Scotopelia ussheri on the ground beside a small inlet (1) and perching on a Raffia
Palm Raphia vinifera (2), on Tagati Island, Sierra Leone, 16 June 2009 (camera-trap photos)
Chouette-pecheuse rousse Scotopelia ussheri par terre a cote d une petite crique (1) et perchee sur un palmier raffia
Raphia vinifera (2), ile de I agati, Sierra Leone, 16 juin 2009 (photos prises par un piege photographique a infrarouges)
90 -Bull ABC Vol 17 No 1 (2010)
Rufous Fishing Owl camera-trapped at midday: Conway et al.
Figure 3. Rufous Fishing Owl Scotopelia ussheri, Tagati Island, Sierra Leone, 16 June 2009; part of the facial disk is
visible (camera-trap photo)
Chouette-pecheuse rousse Scotopelia ussheri , ile de Tagati, Sierra Leone, 16 juin 2009 ; une partie du disque facial est
visible (photo prise par un piege photographique a infrarouges)
therefore noteworthy that the Rufous Fishing Owl
was photographed during the day and appeared
to be active. Whether this is normal behaviour is
unknown.
Rufous Fishing Owl is restricted to the forest
zone from Sierra Leone to south-west Ghana
and is considered Endangered, with an estimated
population of <2,500 individuals (BirdLife
International 2009). Tiwai Island, a Wildlife
Sanctuary with a research station, might represent
a convenient base to study this threatened species’
ecology, if it proves to occur there regularly. New
data could be used to support sustainable land
management and conservation plans for the area.
Acknowledgements
Research at Tiwai was funded by Conservation
International, Tulsa Zoo Conservation Program, The
University of Georgia Graduate School, and the Warnell
School of Forestry and Natural Resources at The
University of Georgia. We thank the Environmental
Foundation for Africa, officials of the Sierra Leone
Forestry and Wildlife Division in Freetown, and the staff
of Tiwai Island Wildlife Sanctuary for allowing access
to the island and for logistical support. Ron Demey,
Lincoln Fishpool and Jeremy Lindsell confirmed the
identification and commented on the manuscript.
References
BirdLife International. 2009. Species factsheet:
Scotopelia ussheri. www.birdlife.org (accessed 31
July 2009).
Borrow, N. & Demey, R. 2001. Birds of Western Africa.
London, UK: Christopher Fielm.
Kemp, A. C. 1988. Strigidae. In Fry, C. H., Keith, S.
& Urban, E. K. (eds.) The Birds of Africa. Vol. 3.
London, UK: Academic Press.
Konig C. & Weick F. 2009. Owls of the World. Second
edn. New Haven, CT: Yale University Press.
Marks, J. S., Cannings, R. J. & Mikkola, H. 1999.
Family Strigidae (typical owls). In del Hoyo,
J., Elliott, A. & Sargatal, J. (eds.) Handbook of
the Birds of the World. Vol. 5. Barcelona: Lynx
Edicions.
‘'Warnell School of Forestry and Natural Resources, The
University of Georgia, Athens, GA 30602 USA.
h Corresponding author E-mail: conwaya@warnell.uga.
edu
Received 23 September 2009; revision accepted 21
October 2009.
Rufous Fishing Owl camera-trapped at midday: Conway et al.
Bull ABC Vol 17 No 1 (2010) -91
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92 -Bull ABC Vol 17 No 1 (2010)
Advertisement
Noteworthy bird records from Sao Tome and Principe
Phillip Hall , A. P. LeventiP , Fdbio Olmof, Stephen Rumsey 1 and Longtong Turshak
Observations remarquables d’oiseaux de Sao Tome et Principe. Des observations remarquables d’une
douzaine d especes d oiseaux sont rapportees, faites a 1’occasion de visites a Sao Tome et Principe en
juillet-aout 2007 et janvier et aout 2008.
W e report noteworthy bird records made
during trips to Sao Tome and Principe in
July-August 2007, and January and August 2008.
For coordinates of the localities mentioned see
Jones & Tye (2006).
Little Egret Egretta garzetta
One near the mouth of the Rio Papagaio, Santo
Antonio town, Principe, on 7 August 2007 (FO &
LT; Fig. 1). It was feeding on the shallow ponds
among the sand and mudflats with a Whimbrel
Numenius phaeopus and two dark-morph Western
Reef Egrets E. gularis. Jones & Tye (2006)
mention only one record from Principe, also at
the mouth of the Rio Papagaio, in January in the
mid 1990s.
Intermediate Egret Egretta intermedia
One in a large grassy area around the Voice of
America facilities south of Sao Tome town, with
several Whimbrels and Cattle Egrets Bubulcus ibis,
on 18 January 2008 (Fig. 2). This appears to be
the first record for Sao Tome (Jones & Tye 2006),
although the species was previously recorded on
Principe, on 7 April 2003 (M. Melo in Bull. ABC
11: 77).
Dwarf Olive Ibis Bostrychia bocagei
On 23 January 2008 at least three were heard
calling at dusk at our camp near Monte Carmo
(sometimes known as Ribeira Peixe; 00°09’06”N
06°33’60”E). Next morning seven birds (including
three pairs) were found on a forested plateau
surrounded by deep valleys covering about 2.0 x
0.5 km. Most ibises were flushed from the ground
and perched nearby. A Critically Endangered
endemic, the population density at Ribeira Peixe
seems fairly high.
African Crake Crex egregia
A medium-sized rail with a short bill, dark legs
and a dull brown back mottled with black, flushed
from the track from Terreiro Velho to the Rio
Pipi, Principe, just before the start of the Oque
Pipi trail, on 22 January 2008, was identified as
an immature African Crake. On Sao Tome, FO
observed an adult crossing a track between Sao
Vicente and Praia Piscina on 22 August 2008.
The species is rarely recorded from Sao Tome
and Principe, where it is perhaps only a straggler
(Jones & Tye 2006).
Common Greenshank Tringa nebularia
Two were foraging with a Whimbrel near the
mouth of the Rio Papagaio, Principe, on 22 January
2008 (Fig. 4). Greenshanks have been recorded on
the islands mainly in December-January (Christy
& Clarke 1998), with few records from Principe
(Jones & Tye 2006).
Ruddy Turnstone Arenaria interpres
One on the east shore of Tinhosa Pequena and
two groups of four birds each at Tinhosa Grande,
near the slope allowing access to the island, on 21
January 2008 (Fig. 5). Considered uncommon
on Principe, with only one record from the
Tinhosas cited by Jones & Tye (2006). On 26
January 2008, one, with two Whimbrels, was
photographed by APL at Praia Jale, on the south-
west coast of Sao Tome.
Swifts Apus spp.
On 15 July 2007, LT and FO observed a pair of
all-dark swifts, noticeably smaller than the Little
Swifts Apus affinis nearby, over the outskirts of
Sao Tome. On 25 January 2008, SR also observed
a small, all-dark swift with a square tail, over the
dirt road between Sao Vicente and Praia Jale, in
south-west Sao Tome. Common Swifts A. apus
have been reported from Sao Tome (Christy &
Clarke 1998), but the birds we saw appeared too
small and had square tails unlike that species, so
their identity is uncertain.
Bird records from Sao Tome and Principe: Hall et al.
Bull ABC Vol 17 No 1 (2010) -93
94 -Bull ABC Vol 17 No 1 (2010)
Bird records from Sdo Tome and Principe: Hall et al.
Also, whilst the race bannermani of Little
Swift is supposedly endemic to both Sao Tome
and Principe, the Principe birds look noticeably
smaller than those on Sao Tome when compared
to the abundant African Palm Swifts Cypsiurus
parvus.
Blue-breasted Kingfisher Halcyon malimbica
dryas
One was observed smashing a land snail Columna
columna against a rock on the trail to Oque Pipi
on 22 January 2008 (Fig. 6). The anvil had the
remains of at least 100 Columna snails (C. columna
or the similar C. leai). Three more anvils along
the trail had mostly Columna spp. shells, but one
had fragments of a small Achatina bicarinata and
one crab. Anvils with broken snails found on
Principe were first attributed to thrushes until
it was realised that Principe kingfishers show
this behaviour (Jones & Tye 2006), which is
apparently unknown in mainland forms.
Whinchat Saxicola rubetra
Two were perched on the wires of an antenna at
Principe airport on 23 January 2008. One had
the dark mottling on the chest of a first-winter;
Legend to figures on opposite page
Figure 1 . Little Egret / Egrette garzette Egretta garzetta,
Santo Antonio, Principe, 7 August 2007 (F. Olmos)
Figure 2. Intermediate Egret / Egrette intermediate
Egretta intermedia , the Voice of America facilities, Sao
Tome, 18 January 2008 (F. Olmos)
Figure 3. Dwarf Olive Ibis / Ibis de Bocage Bostrychia
bocagei, Monte Carmo, Sao Tome (A. P. Leventis)
Figure 4. Common Greenshank / Chevalier aboyeur
Tringa nebularia , Santo Antonio, 22 January 2008 (A. P.
Leventis)
Figure 5. Ruddy Turnstones / Tournepierres a collier
Arenaria interpres, Tinhosa Grande, Principe, 21 January
2008 (A. P. Leventis)
Figure 6. Blue-breasted Kingfisher / Martin-chasseur a
poitrine bleue Halcyon malimbica breaking a Columna
snail against a rock, Oque Pipi, Principe, 22 January
2008 (A. P. Leventis)
Figure 7. Yellow Wagtail / Bergeronnette printaniere
Motacilla flava, Praia Seca, Principe, 6 August 2007 (F.
Olmos)
Figure 8. Sao Tome Grosbeak / Neospize de Sao Tome
Serinus ( Neospiza ) concolor , Monte Carmo, Sao Tome, 24
January 2008 (A. P. Leventis)
no details were noted of the second bird, as it flew
off immediately. There appears to be only one
old previous record, from Bafa de Santo Antonio
(Jones & Tye 2006).
Yellow Wagtail Motacilla flava
On 6 August 2007, during a visit to Praia Seca
(01°32’46”N 07°23’36”E), on the south-east
coast of Principe, FO and LT observed a Yellow
Wagtail in non-breeding plumage foraging on
the beach near some fishermen huts (Fig. 7). It
remained there throughout the afternoon and was
still in the same area the following day.
The occurrence of wagtails Motacilla spp. in
Sao Tome and Principe has been a minor mystery.
They were reported as fairly common in Principe
during the second half of the 19th century, and it
was suggested they were White Wagtails M. alba ,
but there are no specimens (Jones & Tye 2006).
This seems to be the first documented record of
this species for the country (Jones & Tye 2006).
Plain-backed Pipit Anthus leucopbnys
A group of four pipits seen twice flying over the
landing strip of Principe airport on 23 January
2008 had unmarked, dark brown upperparts,
buffish underparts without obvious spots or
stripes, and buff outertail feathers. These features
suggest Plain-backed Pipit, a common species in
Nigeria with which PH is very familiar. Although
in need of proper documentation, this seems to
be the first country record for the species (Jones
& Tye 2006).
Sao Tome Grosbeak Serinus ( Neospiza ) concolor
A pair was feeding on the small green fruit of a
Dicranolepis thomensis tree (a known food item)
at Monte Carmo, at c.315 m, on 24 January
2008 (Fig. 8). The birds peeled the husk off and
crushed the seed, and were readily attracted by
whistles mimicking their single-note contact calls,
similar to those of Principe Seedeater Serinus
rufobrunneus, but much stronger, lending support
to their suggested close relationship (Melo 2007).
The birds approached closely, singing in response
to the playback of a song recorded during a
previous visit to the area (available at http://xeno-
canto.org/africa, XC 18131).
Bird records from Sao Tome and Principe: Hall et al.
Bull ABC Vol 17 No 1 (2010)- 95
References
Christy, P. & Clarke, W. V. 1998. Guide des Oiseaux de
Sao Tome et Principe. Sao Tome: ECOFAC.
Jones, P. & Tye, A. 2006. The Birds of Sao Tome
& Principe with Annobon: Islands of the Gulf of
Guinea. An Annotated Checklist. BOU Checklist
No. 22. Oxford: British Ornithologists’ Union &
British Ornithologists’ Club.
Melo, M. 2007. Bird speciation in the Gulf of Guinea.
Ph.D. thesis. Institute of Evolutionary Biology,
University of Edinburgh.
"5 Louis Solomon Close, Victoria Island, Lagos, Nigeria.
E-mail: philhall. obe@btinternet. com
h 19 Ilchester Place, London W14 8AA, UK. E-mail:
elizabeth. thaddeus@leventis-overseas. com
‘ Largo do Paissandu 1 00 /4c, 01034-010, Sao Paulo, SP,
Brazil. E-mail: f-olmos@uol. com. br
d Ashes Farm, Hogg Hill, Icklesham, Winchelsea, East Sussex
TN36 4AH, UK. E-mail: srumsey@beamingbroadband.
com
' A. P. Leventis Ornithological Research Institute,
University of Jos, PO Box 13404, Plateau State, Jos,
Nigeria. E-mail: longtongturshak@yahoo.com
Received 8 October 2008; revision accepted 17
November 2009.
96 -Bull ABC Vol 17 No 1 (2010)
Bird records from Sao Tome and Principe: Hall et al.
Display behaviour of Shelley’s Oliveback Nesocharis shelleyi
Michael S. L. Mills
Parade du Dos-vert a tete noire Nesocharis shelleyi. La parade du Dos-vert a tete noire Nesocharis shelleyi,
une espece a repartition restreinte confinee a la Zone d’Endemisme pour les Oiseaux des Montagnes
camerounaises, n’a pas encore ete documentee. Cette note decrit la parade d’un male, observe au Mont
Cameroun, et fournit des informations sur son comportement et son chant.
T he olivebacks Nesocharis are a trio of Central
and West African finches (Estrildidae)
characterised by their distinctive grey, black and
olive plumage (Fry & Keith 2004). Shelley’s
Oliveback N. shelleyi is a range-restricted endemic
of the Cameroon Mountains Endemic Bird Area,
which straddles Cameroon, Nigeria and Equatorial
Guinea (Stattersfield et al. 1998). Little is known
concerning its behaviour or breeding (Goodwin
1982, Fry & Keith 2004), and its nuptial displays
are undescribed.
On 7 March 2009 I was observing birds on
the Race Track above Buea, Mt Cameroon, with
a group of nine other birders. At 14.00 hrs, at
1,700 m, I heard high-pitched calls emanating
from cA m above the ground, directly above the
trail. The source proved to be a male Shelley’s
Oliveback, distinguished from the female by its
having an olive breast and whitish borders to the
sides of the black head (Fig. 2). In its bill it held,
by the very tip, an upside-down grass stalk with
seeds, c. 15 cm in length. During c . 3 minutes of
observation it hopped back and forth along a bare
branch, singing as it did so. Some of the time its
flank feathers were expanded. This is similar to
the observed behaviour of a singing male White-
collared Oliveback N. ansorgei, its sister species,
which sang from a branch 10 m above the ground,
with its flank feathers expanded and its head and
bill raised (Chapin 1959).
Eighty seconds of song were recorded in .wav
format (using an Edirol R09 recorder with a
Sennheiser MKE400 microphone). Recordings
were inspected using Raven Lite software (Cornell
Lab of Ornithology 2003-08) and a sonogram
produced (Fig. 1). The song consisted of a repeated
series of 4-8 different, high-pitched, buzzy trills,
in the 5-8 kHz range. Within each series, trills
differed in duration, pitch and structure, some
having an upward or downward inflection, and
others being flat. Pitch appeared to undulate
between successive notes, and different trills were
repeated in a similar sequence, giving the song
quite a musical tone. During 80 seconds, the
sequence was repeated 14 times, lasting a mean
5.7 seconds.
Acknowledgements
Hemme Batjes, Andrew Bunting, Simon Colenutt,
Andy Deighton, Martin Kennewell, Ian Merrill,
Jonathan Newman, Volkert van der Willigen and
Barry Wright observed the bird with me. Volkert van
der Willigen recorded some invaluable video material,
which was used in the description, and Simon Colenutt
Series 1 Ser ics 2
Figure 1 . Sonogram of the display song of Shelley’s Oliveback Nesocharis shelleyi. The song consists of a series of 4-8
buzzy trills in the 5-8 kHz range and lasting 5-6 seconds; here series of five and six notes are shown.
'Sonogramme du chant de parade du Dos-vert a tete noire Nesocharis shelleyi. Le chant consiste de series de 4-8 trilles de
5-6 secondes dans la bande de 5-8 kHz ; ici des series de cinq et six notes sont montrees.
Display behaviour of Shelley ’s Oliveback: Mills
Bull ABC Vol 17 No 1 (2010) -97
Figure 2. Displaying male Shelley’s Oliveback Nesocharis shelleyi , holding a c. 1 5 cm grass stalk in its bill, Mt
Cameroon, Cameroon, March 2009 (Ian Merrill)
Dos-vert a tete noire Nesocharis shelleyi male en parade, tenant une tige d'environ 1 5 cm dans son bee, Mont
Cameroun, Cameroun, mars 2009 (Ian Merrill)
and Ian Merrill took some excellent photographs.
Hilary Fry, Guy Kirwan and Ron Demey helped to
improve the contents of this manuscript.
References
Chapin, R. T. 1959. The behaviour of the Olive
Weaver-Finch Nesocharis ansorgei. Proc. I Pan-Afr.
Orn. Congr., Ostrich Suppl. 3: 230-232.
Cornell Lab of Ornithology. 2003-08. Raven Lite 1.0.
Ithaca, NY: Cornell Lab of Ornithology.
Fry, C. H. & Keith, S. (eds.) 2004. The Birds of Africa.
Vol. 7. London, UK: Christopher Helm.
Goodwin, D. 1982. Estrildid Finches of the World.
London, UK: Br. Mus. (Nat. Hist.) & Oxford:
Oxford University Press.
Stattersfield, A. J., Crosby, M. J., Long, A. J. & Wege,
D. C. 1998. Endemic Bird Areas of the World:
Priorities for Biodiversity Conservation. Cambridge,
UK: BirdLife International.
“Birding Africa, PO Box 34146, Rhodesgift 7707, Cape
Town, South Africa. E-mail: michael@birdingafrica.com
Received 20 April 2009; revision accepted 3 November
2009.
98 -Bull ABC Vol 17 No 1 (2010)
Display behaviour of Shelley 's Oliveback: Mills
Little-known African bird:
Madagascar Serpent Eagle Eutriorchis astur
Jonathan C. Eames
Un oiseau africain peu connu : le Serpentaire de Madagascar Eutriorchis astur. Malgre le fait que nos
connaissances concernant le Serpentaire de Madagascar Eutriorchis astur ont avance de faqon significative
ces dernieres 15 annees, ce rapace globalement menace, qui est confine au nord-est de Madagascar, est
rarement observe et encore plus rarement photographic. Superficiellement, il ressemble a un Accipiter : il
a des ailes relativement courtes et une longue queue barree, ainsi que des parties superieures brunes et des
parties inierieures marquees de larges barres. La htterature mentionne qu’il pourrait etre confondu avec
1 Autour de Henst Accipiter henstii, dont la femelle a une taille similaire, mais le serpentaire est barre de
sombre dessus et a la queue plus arrondie, les barres sur la poitrine plus larges et une crete courte mais bien
visible. Contrairement a ce que son nom suggere, il ne prend que rarement des serpents, se nourrissant
principalement de cameleons Furcifer et Calumma spp. et de geckos Uroplatus spp.
Figures 1-2. Adult Madagascar Serpent Eagle Eutriorchis astur , Masoala National Park, Madagascar, 24 November
2008 0- C. Eames)
Serpentaire de Madagascar Eutriorchis astur adulte, Parc National de Masoala, Madagascar, 24 novembre 2008 (J. C.
Eames)
A bove all other poorly known or seldom
seen bird species of Madagascar, pride of
place surely belongs to Madagascar Serpent
Eagle Eutriorchis astur. This globally Endangered
Malagasy endemic has recently been recorded
only in the north-east where it occurs mainly in
primary forest (Thorstrom & Rene de Roland
2003, BirdLife International 2009). It has been
described as elusive and secretive, and is one of
the rarest birds of prey in the world (Thorstrom
& Rene de Roland 2000, 2003, Thorstrom et al.
2003). Although it is not the rarest of Malagasy
endemics, Madagascar Serpent Eagle is amongst
the hardest to see, even at the handful of sites from
which it is known.
Our knowledge of the species has advanced
significantly in the last 15 years and clarification
of its territorial call has lead to the eagle’s discovery
Figure 3. Adult Henst’s Goshawk Accipiter henstii,
Ranamofana National Park, Madagascar, 2 December
2005 (J. C. Eames)
Autour de Henst Accipiter henstii adulte, Parc National
de Ranamofana, Madagascar, 2 decembre 2005 (J. C.
Eames)
Little-known African bird
Bull ABC Vol 17 No 1 (2010)- 99
at several new sites (BirdLife International 2009).
However, there are few published images of the
species, helping to perpetuate the near-mythical
aura that surrounds this eagle. I have been able
to trace only five photographs, all by staff of The
Peregrine Fund, who have conducted most of
the research to date on this species. Probably the
two best known are those of an adult in the hand
and an adult perched in the forest subcanopy,
published in Morris & Hawkins (1998), whilst
two others, of an adult and fledgling at the nest,
and of a young bird in the canopy, were published
in Thorstrom & Rene de Roland (2003). A
photograph of an adult and pullus at the nest can
be viewed at http://www.peregrinefund.org/press.
Having not previously encountered the species,
I resolved to see and photograph it on a return visit
to Masoala National Park in November 2008.
Based at Masoala Forest Lodge, I made early-
morning forays into the forest with Andrianoelina
Fitia Lofontsiriniaina and guide Marco, in the
hope of hearing birds calling as they left their
nocturnal roost. From 19 to 24 November, we
searched daily along trails from 04.00 hrs. We
concentrated our efforts on a relatively small area
of primary littoral forest (according to Marco the
species never ventures into the hills at Masoala)
and visited two old nests. Although we never heard
the species calling and despite frequent heavy rain,
persistence finally paid off. In the early afternoon
of 24 November, c.500 m from Marco’s village of
Ambodifonaha and close to a pit-sawing site, we
disturbed a large raptor suspended upside-down
from an epiphytic fern (possibly an Asplenium sp.)
f.10 m from the trail in logged primary forest. It
hung, flapping, preoccupied with trying to take a
prey item, possibly a gecko or frog, from within
the fern. Upon our approach it dropped whatever
it had caught and flew to an exposed perch above
the trail, where it was dive-bombed by a Crested
Drongo Dicrurus forficatus. I was able to take three
photographs, of which two are published here
(Figs. 1-2). It then flew off through the forest and
despite a mad dash over several hundred metres we
were unable to relocate it.
Madagascar Serpent Eagle has been described as
a rather small and atypical snake eagle, having the
shape and general brown and barred appearance
of a large Accipiter (Morris & Hawkins 1998,
Ferguson-Lees & Christie 2001). Superficially
Madagascar Serpent Eagle does indeed appear
Accipiter-Yikf. it has relatively short wings and
a long barred tail, as well as brown upperparts
and broadly barred underparts. The similarity
is such that three specimens in collections were
originally misidentified as Henst’s Goshawk
Accipiter henstii (Ferguson-Lees & Christie 2001).
The two species are reportedly difficult to separate
(Morris & Hawkins 1998, Thorstrom & Rene de
Roland 2000). Indeed, female Henst’s Goshawk
is closely similar in size and plumage (Ferguson-
Lees & Christie 2001). However, the serpent eagle
averages larger (although some measurements
overlap) and has dark-barred upperparts, a fuller,
more rounded tail, broader breast barring and a
short but obvious crest. It also has conspicuous
and abundant rictal bristles and a slight ruff on
the nape, which has pale tips and dark subterminal
bars to each feather. Henst’s Goshawk lacks the
pale scaling on the nape and has plain, darker
brown upperparts and finer barred underparts.
In addition, the serpent eagle possesses 6-7 even-
width dark tail bars, which are narrower than the
brown gaps between them (Morris & Hawkins
1998, Ferguson-Lees & Christie 2001, Sinclair
& Langrand 2003). The bulging head shape is
also sometimes referred to (BirdLife International
2009). In life, at close range, the likeness to an
Accipter is superficial because of the odd bill,
teddy-bear like eye and facial shape and feathering.
A closely observed serpent eagle is instantly and
easily identified as such.
In Figs. 1-2 most of the diagnostic features
mentioned above can be seen; for comparison
with Henst’s Goshawk see Fig. 3. The short crest is
flattened and invisible. Although it has been stated
that the serpent eagle has short tarsi (Sinclair &:
Langrand 2003), they appear proportionately
long to me. Tarsus length is given as 80-92 mm
for Madagascar Serpent Eagle and 81-100 mm
for Henst’s Goshawk (Ferguson-Lees & Christie
2001), the latter a bird one would not describe
as having short tarsi. Other structural points to
note (mentioned by Ferguson-Lees & Christie
2001) are the apparently relatively short toes and
nails, although these are not easy to see. Also
noteworthy is the large yellow eye, an adaptation
perhaps to taking Uroplatus geckos, which are
nocturnal. Furthermore, note the swollen, bulbous
appearance of the bill, which lacks the tooth-
notched upper mandible of Henst’s Goshawk, and
the grey cere, which is largely hidden by the rictal
100 - Bull ABC Vol 17 No 1 (2010)
Little-known African bird
bristles. In the photographs at full resolution one
can see the scutellated tarsi, described elsewhere
as heavily scaled and knobbly looking (Ferguson-
Lees & Christie 2001).
Madagascar Serpent Eagle is traditionally
placed alongside Congo Serpent Eagle Dryotriorchis
spectabilis (Kemp 1994, Ferguson-Lees & Christie
2001) and it had even been suggested that this
genus and the monotypic Eutriorchis should be
united (Brown & Amadon 1968). However,
recent research has revealed that Eutriorchis astur
is not related to the serpent eagles Spiliornis of
Asia or to Dryotriorchis spectabilis — which have
now been placed together in the Circaetinae — but
nestles within one of two Old World vulture
clades, the Gypaetinae, alongside Lammergeier
Gypaetus barbatus , Egyptian Vulture Neophron
percnopterus and Palm-nut Vulture Gypohierax
angolensis (Lerner & Mindell 2005). Its English
name also does not accurately reflect its dietary
preferences as it rarely eats snakes. In a recent
study, snakes comprised just 1.5% of prey items
brought to a nest, whereas chameleons Furcifer
and Calumma spp. and leaf-tailed geckos Uroplatus
spp. comprised over 80% (Thorstrom & Rene de
Roland 2003). On this trip to Masoala, and despite
considerable effort, I failed to locate any Uroplatus
geckos, which I had easily found after dark on an
earlier visit. These geckos are popular in the exotic-
pet trade and in some areas there is concern that
collectors are reducing the populations (http://
www.wildmadagascar.org/wildlife/uroplatus.
html). I have no evidence of Uroplatus collecting
in Masoala National Park, but perhaps the issue is
worthy of further investigation?
Acknowledgements
I thank my Asity counterpart Andrianoelina Fitia
Lofontsiriniaina, Tsiry, who was simply invaluable, as
well as being good company. I would like also to thank
Voninavoko Raminoarisoa (aka Vony), Coordonnateur ,
Asity Madagascar for her support and collaboration.
Thanks also to Nigel Collar, Frank Hawkins, Simon
Mahood and Roger Safford for their encouragement
and for commenting on drafts of this article. Particular
thanks to Pierre & Sandra Bester for their hospitality,
and guide Marco at Masoala Forest Lodge. Special
thanks to Roger Safford for making many useful
comments added at proof stage and for suggesting
additional references.
References
BirdLife International. 2009. Species factsheet:
Eutriorchis astur. www.birdlife.org (accessed 22
July 2009).
Brown, L. H. & Amadon, D. 1968. Eagles, Hawks
and Falcons of the World. Feltham: Country Life
Books.
Ferguson-Lees, J. & Christie, D. A. 2001. Raptors of the
World. London, UK: Christopher Helm.
Kemp, A. C. 1994. Madagascar Serpent-eagle Eutriorchis
astur. In del Hoyo, J., Elliott, A. & Sargatal, J.
(eds.) Handbook of the Birds of the World. Vol. 2.
Barcelona: Lynx Edicions.
Lerner, H. R. L. & Mindell, D. P. 2005. Phylogeny of
eagles, Old World vultures, and other Accipitridae
based on nuclear and mitochondrial DNA. Mol.
Phyl. & Evol. 37: 327-346.
Morris, P. & Hawkins, F. 1998. Birds of Madagascar: A
Photographic Guide. Robertsbridge: Pica Press.
Sinclair, I. & Langrand, O. 2003. Birds of the Indian
Ocean Islands. Cape Town: Struik.
Thorstrom, R. & Rene de Roland. L. A. 2000. First nest
description, breeding behaviour and distribution of
the Madagascar Serpent-Eagle Eutriorchis astur. Ibis
142: 217-224.
Thorstrom, R. & Rene de Roland, L. A. 2003.
Eutriorchis astur, Madagascar Serpent-eagle,
Fandrasasalambo. In Goodman, S. M. & Benstead,
J. P. (eds.) The Natural History of Madagascar.
Chicago: The University of Chicago Press.
Thorstrom, R., Rene de Roland, L. A. & Watson, R. T.
2003. Falconiformes and Strigiformes: ecology and
status of raptors. In Goodman, S. M. & Benstead,
J. P. (eds.) The Natural History of Madagascar.
Chicago: The University of Chicago Press.
PO Box 89, 6 Dinh Le, Hanoi, Vietnam. E-mail:
EamesdPbirdlife. org. vn
Received 27 July 2009; revision accepted 23 October
2009.
Little-known African bird
Bull ABC Vol 17 No 1 (2010) - 101
Photospot:
Friedmann’s Lark Mirafra pulpa
Nik Borrow
L’Alouette de Friedmann Mirafra pulpa. Bien que l’Alouette de Friedmann Mirafra pulpa ait ete
decrite en 1930 — par l’ornithologue americain Herbert Friedmann sur la base d’un specimen collecte
en 1912 au sud de l’Ethiopie — ce n’est que pendant les annees 1970 que nos connaissances de l’espece
ont augmentees substantiellement. Elle demeure toutefois classee comme «InsufFisamment documentee».
L’oiseau est d’apparence quelque peu erratique et n’est pratiquement jamais observe en dehors de la periode
de reproduction, en saison des pluies. Son aire de repartition s’etend de la localite type en Ethiopie du sud
jusqu’a la Reserve de Mkomazi au nord de la Tanzanie, en passant par les Reserves de Samburu/Shaba et
du Parc National de Tsavo au Kenya. Les criteres d’identification sont presentes et illustres par des photos,
et compares avec celles d’autres especes d’alouettes.
Figure 1 . Friedmann’s Lark Mirafra pulpa, Shaba
National Reserve, Kenya, 3 November 2008 (Nik
Borrow). The drawn-out and far-carrying hoo-ee-oo song
is usually given during song-flight or from the topmost
branches of a prominent bush. Whilst singing the bright
white throat is forced outwards forming a distinctive
‘beard’.
Alouette de Friedmann Mirafra pulpa, Reserve Nationale
de Shaba, Kenya, 3 novembre 2008 (Nik Borrow). Le
chant etire et portant loin hoo-ee-oo est d’habitude emis
en vol ou a partir du sommet d’un buisson preeminent.
La gorge blanche est gonflee en chantant, formant ainsi
une ‘barbe’.
Figure 2. Friedmann’s Lark Mirafra pulpa, Shaba
National Reserve, Kenya, 3 November 2008 (Nik
Borrow). Features to look for on a silent bird include the
brown centres to the median and greater coverts that are
bordered by a darker submarginal line. Also, the streaks
on the breast-sides tend to coalesce, giving the illusion of
a dark patch.
Alouette de Friedmann Mirafra pulpa, Reserve Nationale
de Shaba, Kenya, 3 novembre 2008 (Nik Borrow).
Les caracteristiques a noter chez un oiseau silencieux
comprennent les centres bruns des moyennes et grandes
couvertures hordes d’une ligne sombre sub-marginale.
Les stries sur les cotes de la poitrine ont aussi tendance a
s’unir, donnant I’impression d’une tache sombre.
F riedmann’s Lark Mirafra pulpa is probably
one of those few birds that really deserve
the often-misused adjective ‘enigmatic’. The
species was described in 1930 by the American
ornithologist Herbert Friedmann from a specimen
collected in southern Shoa Province, Ethiopia,
by E. A. Mearns in May 1912 (Friedmann
102 -Bull ABC Vol 17 No 1 (2010)
Photospot: Friedmann s Lark
Figure 3. Friedmann’s Lark Mirafa pulpa, Tsavo East
National Park, Kenya, 28 November 2009 (Axel Smets).
In worn plumage the appearance is more uniform
but although the pale edges have abraded to quite an
extent, the brown-centred coverts with darker vane and
submarginal areas can still be seen. Even when not singing
this individual shows the distinctive white throat.
Alouette de Friedmann Mirafra pulpa , Parc National de
Tsavo Est, Kenya, 28 novembre 2009 (Axel Smets). En
plumage use 1’apparance est plus uniforme, mais bien que
les liseres pales soient deja bien abrases, les couvertures aux
centres bruns et les parties plus sombres des plumes sont
toujours visibles. La gorge blanche caracteristique est bien
apparente, meme chez cet individu silencieux.
Figure 4. Foxy Lark Mirafra alopex, Shaba National
Reserve, Kenya, 17 May 2009 (Adam Riley / Rockjumper
Birding Tours). The form that overlaps with Friedmann’s
Lark shows greater contrast and a much warmer tone to
the plumage than the latter. Note also that in Foxy Lark
the pale-fringed greater and median coverts are dark-
centred and the supercilium and semicircular mark below
the eye are whiter and more prominent; this effect is
further heightened by the blackish lores.
Alouette abyssinienne Mirafra alopex. Reserve Nationale
de Shaba, Kenya, 17 mai 2009 (Adam Riley / Rockjumper
Birding Tours). La forme qui chevauche avec l’Alouette de
Friedmann a un plumage plus contraste, au teint beaucoup
plus chaud, que 1 Alouette de Friedmann. Noter egalement
que chez l’Alouette abyssinienne les grandes et moyennes
couvertures ont un centre sombre et des liseres pales, et
que le sourcil et la marque semi-circulaire en dessous
de l’ceil sont plus blancs et plus prononces ; cet efifet est
augmente par les lores noiratres.
Figure 5. Williams’s Lark Mirafra williamsi, Shaba
National Reserve, Kenya, 3 November 2008 (Nik
Borrow). This lark prefers more open, rocky, lava or sandy
plains, is virtually plain-backed and blotched or spotted
below and not likely to be confused.
Alouette de Williams Mirafra williamsi, Reserve Nationale
de Shaba, Kenya, 3 novembre 2008 (Nik Borrow). Cette
alouette prefere les plaines plus ouvertes, rocailleuses, de
lave ou sablonneuses et est pratiquement unie dessus et
tachete dessous; il est improbable qu’elle soit confondue.
Figure 6. Somali Short-toed Lark Calandrella somalica,
Liben Plains, Ethiopia 19 October 2006 (Nik Borrow).
This species has a distinctive facial pattern with obvious
pale semicircular areas around the eye and a browner
plumage with dark centred median and greater coverts.
Alouette roussatre Calandrella somalica, Plaines de Liben,
Ethiopie, 19 octobre 2006 (Nik Borrow). Cette espece
a un pattern facial distinct avec des zones pales semi-
circulaires marquees autour de 1’oeil et un plumage plus
brun avec des grandes et moyennes couvertures aux centres
sombres.
Photospot: Friedmann 's Lark
Bull ABC Vol 17 No 1 (2010) -103
1930a). During the same expedition, three more
specimens were collected from near Archer’s Post
in the Samburu area of northern Kenya, but these
were originally described as a separate species
M. Candida (Friedmann 1930b). There were
subsequently no further records until December
1972 when the ringing team at Ngulia Lodge,
Tsavo West National Park, south-east Kenya,
found a corpse there after the bird flew into the
walls at night, having presumably been attracted
to the bright lights of the lodge (Lack 1977).
During the 1970s our knowledge of the bird
was much advanced, in particular by Peter Lack
who described its song and field features (Lack
1977). However, the species remains elusive and
somewhat erratic in its appearances ro this day,
and it is almost never seen outside the breeding
season (see Lack 1997 for all records prior to
1997). It is still classified as ’Data Deficient’
(BirdLife International 2009). In order to stand
a good chance of seeing Friedmann’s Lark the
visiting birder must firstly visit the known range,
which stretches from the type locality in southern
Ethiopia, through the Samburu/Shaba Game
Reserves and Tsavo National Park areas of Kenya
into the Mkomazi Game Reserve in northern
Tanzania. The species’ preferred habitat is rather
open grassland with sparse to dense bush cover.
The best time to look is definitely in the rainy
season, but as the rains can be erratic in this region,
this is not something that can be easily planned
several months in advance. However, a visit timed
within the months December to January (‘short’
rains) or possibly April to May (‘long’ rains) seems
to coincide with the optimum times.
Friedmann’s Lark usually makes its appearance
once the rains start falling but even this doesn’t
seem to be 100% guaranteed in the same localities
every season. Nonetheless, when the species is
present it is often reasonably numerous and
probably not easy to miss, provided its most
distinctive song is known. One should listen out
at any time of day (or night) for a single, long
drawn-out and far-carrying hoo-ee-oo with an
emphasis on the middle part. This simple phrase is
monotonously repeated at intervals of one to two
seconds, either from a conspicuous perch or in an
undulating but rather lazy song flight that reaches
up to a height of c. 10 m.
No other smaller lark in range sings like this;
Singing Bush Lark M. cantillans, Williams’s Lark
M. ivilliamsi, Flappet Lark M. mfocinnamomea,
Foxy Lark M. alopex and Somali Short-toed Lark
Calandrella somalica all give more complex or
variable scratchy, warbling or melodious songs.
The distinctive Short-tailed Lark Pseudalaemon
fremantlii sings a slow, deliberate, but slightly
slurred whistle from the ground seen seeu . . . seen
seen seeu . . . seeu seeu TEWleu. Perhaps the song of
Friedmann’s Lark might be overlooked as coming
from a White-browed Scrub Robin Cercotrichas
leucophrys , although this is rather unlikely.
Having heard the song the bird shouldn't be
difficult to locate, as it is by no means a ‘skulker’
when singing or displaying. Check the tops of
the bushes for a typical Mirafra lark that will be
slightly raising its crown feathers and puffing out
its pure white throat with every song phrase. This
prominent white throat extends in a half-collar
around the neck, immediately giving the bird
a most distinctive appearance totally unlike its
congeners (Figs. 1-2).
Perhaps the real mystery is to where this species
goes when it is not breeding and vocal. There is
some evidence to suggest that Friedmann’s Lark is
a local or intra-African migrant (for example, the
appearances at Ngulia Lodge at night), but if this
is the case exactly where are the non-breeding areas
that it migrates to and from? Perhaps part of the
problem lies in identifying the bird using plumage
alone and if faced with a silent lark in north-east
Africa what features should be looked for?
The larks in the genus Mirafra range in size
from small to large with short, rounded wings,
and variably shaped bills that can be short and
conical or long and decurved. Friedmann’s Lark
is typical of the smaller, shorter billed types. Of
the several comparable Mirafra larks, White-tailed
Lark M. albicauda occurs in dense grasslands on
black cotton soils, probably a habitat not suited to
Friedmann’s, and albicauda also appears blackish
from a distance and so can be immediately rejected
as a confusion species. The similar looking Flappet
Lark M. rufocinnamomea, unlike Friedmann’s,
lacks any white in the tail, although the buff or
rufous outer tail feathers can be confusingly pale
in some populations. The localised Williams’s
Lark M. ivilliamsi prefers more open, rocky, lava
or sandy plains, is virtually plain-backed and
blotched or spotted below, and again unlikely
to be confused. The distinctive facial pattern of
Somali Short-toed Lark Calandrella somalica with
104 - Bull ABC Vol 17 No 1 (2010)
Photospot: Friedmann s Lark
its obvious pale semicircular areas around the eye
and browner flight feathers should also be enough
to immediately discount this species.
We are therefore left with two widespread and
common species that perhaps offer the greatest
challenge to correct identification. A Foxy Lark M.
alopex was recently misidentified as Friedmann’s
Lark: see the photograph in Bull. ABC 16: 234,
reproduced here (Fig. 3). Comparing this bird
with Friedmann’s Lark, we should note that the
general coloration of Foxy Lark shows greater
contrast, being generally warmer and much more
rufous. I his is particularly noticeable on the edges
of the primaries, which form an obvious reddish
panel on the closed wing. The pale-fringed greater
and median coverts of Foxy Lark are dark-centred,
whereas in Friedmann’s Lark these feathers are
brown-centred with a darker submarginal line.
The white supercilium and semicircular mark
below the eye are whiter and more prominent
on Foxy Lark, which effect is heightened by the
blackish lores. An encounter with the little-known
rufous morph of Friedmann’s Lark may be more
problematic but this form should show an even
more uniform appearance with the white areas
washed warm buff.
Singing Bush Lark M. cantillans is somewhat
more similar in plumage tone to Friedmann’s
and is perhaps the most likely confusion species.
However, it is always a colder, greyer looking
bird and completely lacks the rufous fringes to
the flight feathers (Lack 1992, Zimmerman et al.
1996). The central rectrices of Friedmann’s are
also reddish-brown as opposed to cold grey or
sepia brown in the appropriate race, marginata ,
of Singing Bush Lark. Another feature seemingly
unique to Friedmann’s is that the streaks on the
breast-sides tend to coalesce, giving the illusion of
a dark patch somewhat akin to that often seen on
short-toed larks Calandrella spp.
With increased understanding of the field
features, perhaps it will not be too long before the
final mysteries of this little-known bird are finally
unravelled.
References
BirdLife International. 2009. Species factsheet: Mirafra
pulpn. www.birdlife.org (accessed 20 November
2009).
Friedmann, H. 1930a. A lark new to science from
southern Ethiopia. Occ. Pap. Boston Soc. Nat. Hist.
5: 237-259.
Friedmann, H. 1930b. A lark new to science from
north-central Kenya Colony. Auk 47: 418-419.
Lack, P. C. 1977. The status of Friedmann’s Bush-Lark
Mirafra pulpa. Scopus 1: 34-39.
Lack, P. C. 1992. Mirafra pulpa. In Keith, S., Urban,
E. K. & Fry, C. H. (eds.) The Birds of Africa. Vol.
4. London UK; Academic Press.
Lack, P. C. 1997. Lriedmann’s Lark Mirafra pidpa — an
enigma. Bull. ABC 4: 132-134.
Zimmerman, D. A., Turner, D. A. & Pearson, D.
J. 1996. Birds of Kenya and Northern Tanzania.
London, UK: Christopher Helm.
Flat 5, 63-67 St George’s Drive, London SW1V 4DD.
E-mail: n. borrow@btinternet. com
Received 1 5 November 2009.
Photospot: Friedmann ’s Lark
Bull ABC Vol 1 7 No 1 (2010) -105
Finding southern Ethiopia’s endemic birds
Claire N. Spottiswoode
Trouver les oiseaux endemiques au sud de l’Ethiopie. Le sud de l Ethiopie possede un endemisme
avien remarquable et est reconnu comme une Zone d'Endemisme pour les Oiseaux. Cet article fournit des
informations concernant cinq especes endemiques et explique comment les trouver sur le terrain. II s’agit
du Touraco de Ruspoli Tauraco ruspolii, de l’Engoulevent de Nechisar Caprimulgus solala, de l’Alouette
d’Erard Heteromirafra sidamoensis , de l’Hirondelle a queue blanche Hirundo megaensis et du Corbin de
Stresemann Zavattariornis stresemanni. Ces especes sont menacees par la degradation ou la destruction de
leur habitat par les activites d une population humaine toujours en augmentation.
^ cattered along the southernmost escarpment of
in
Ethiopia’s highlands are the tiny distributions
of five endemic bird species. This nucleus of
remarkable and unexplained endemism
grassland, savanna and juniper forest
is recognised as a global Endemic
Bird Area (EBA; Stattersfield et al.
1998). All five endemics are globally
threatened, one critically so, and
conservation projects in the region will
be beneficiaries of funds raised by the
2010 British Birdwatching Fair. This
support is urgently needed to avert
at least one imminent extinction:
without immediate conservation
intervention, southern Ethiopia’s
Liben Lark (previously known as
Sidamo Lark: see Collar 2009)
seems destined to become mainland
Africa’s first recorded bird extinction
(Spottiswoode et al. 2009).
Endemics aside, birdwatching in
this region is tremendously diverse,
enjoyable and for the most part
straightforward, owing to its open
habitats and dry climate. The focus of
this article is, however, the endemic
species, briefly sketching their ecology and how
and where each can most reliably be seen during
a short birding trip. Much of the information is
adapted from a forthcoming bird-finding guide to
Ethiopia (Spottiswoode et al. in press), which also
describes in detail other sites along the journey
‘linking’ the endemic species, from Negele to
Yabelo via the village of Arero.
Until recently, the pantheon of southern
Ethiopia’s endemics would also have included the
far-flung Degodi Lark Mirafra degodiensis , but
Collar et al. (2008) have shown this species to be
poorly defined with respect to morphology, voice
and genetics, and best regarded as a subspecies
of Gillett’s Lark Mirafra gilletti , itself a relatively
localised endemic to the Horn of Africa.
Above: general map of southern Ethiopia showing the
main areas discussed herein. All of the maps reproduced
here are by Claire Spottiswoode, and taken from Finding
Birds in Ethiopia , reproduced with permission of the
publishers.
Legend to figures on opposite page
Figures 1-2. Liben (formerly Sidamo) Lark / Alouette
d’Lrard Heteromirafra sidamoensis, Liben Plain, Ethiopia,
2 August 2007 (Greg Davies)
Figure 3. Prince Ruspoli s Turaco / Touraco de Ruspoli
Tauraco ruspolii, Arero Forest, Ethiopia, 31 August 2005
(Claire Spottiswoode)
1 06 -Bull ABC Vol 17 No 1 (2010)
Finding southern Ethiopia ’s endemic birds: Spottiswoode
■■H
Finding southern Ethiopia ’s endemic birds: Spottiswoode
Bull ABC Vol 1 7 No 1 (2010) -107
Prince Ruspoli’s Turaco Tauraco ruspolii
When Prince Ruspoli was trampled to death
by an elephant in south-west Ethiopia in 1893,
his collecting bag — happily intact— contained
the type specimen of this turaco. The specimen
was presumed to originate from Arero Forest
(described below), but it is now clear that the
bird occurs patchily over a wider area of southern
Ethiopia, and is not confined to forest. Despite
its tolerance of tall Acacia and secondary growth,
it remains heavily threatened by wood extraction
and agriculture (Borghesio et al. 2004). There is
little confidence that its distributional limits have
been properly defined, and any records outside its
established range (between Arero and the Genale
River) are of great interest and should be reported
to the Ethiopian Wildlife and Natural History
Society (EWNHS; BirdLife in Ethiopia). The
three sites below represent those where it can most
reliably be seen, but keep an eye out for the species
in any denser roadside vegetation throughout
the wooded highland foothills (particularly from
Negele to Kebre Mengist and Shakisso). This
species and the more widespread White-cheeked
Turaco T. leucotis occur alongside one another
at Arero Forest and in the Kebre Mengist region;
hybrids are worryingly widespread at the latter
(Lernould & Seitre 2002, Borghesio et al. 2004).
Finding it. Although habitat degradation in the
heavily populated Negele region has already taken
a heavy toll on Prince Ruspoli’s Turaco (Borghesio
et al. 2004), one site in this area is perhaps still the
simplest place to see it. Halfway between Negele
town and the Liben Plain (see Liben Lark below),
a drainage line with sparse thicket crosses the
road (1 on Negele map; 05°18.44’N 39°38.04’E).
Scan for turacos perched in the open on exposed
branches in the early morning and evening, often
calling hoarsely, or stroll through the habitat
to search for them; when flushed they typically
fly only a short distance to the next clump of
thicket.
Travelling between Negele and the Bale
Mountains, many birders have sought this species
(with some success) at the point where the road
crosses the Genale River. Stop at the sandy drift (2
on Negele map; 05°41.10’N 39°31.85’E) 2.8 km
south of the main Genale bridge, and search the
many impressive fig trees here, particularly in the
dry season. A local turaco guide, Adem Dube, may
well appear and help, and guide you up a beautiful
wooded valley to the east. Turacos also occur in
mixed Acacia-Terminalia-Combretum woodland
further from the Genale River.
Arero Forest, a mixed juniper and Podocarpus
evergreen forest west of Negele, is the presumed
type locality of Prince Ruspoli’s Turaco. This area
is prone to ethnic disputes so it is worth checking
on the security situation before visiting. Entering
Arero village, turn left at the large ‘roundabout’
centred on a big tree, and you will shortly
enter juniper forest (1 on Arero map). Turn
right 6.2 km from the roundabout (04°47.42’N
38°49.47’E), and keep an eye out from this point
for turacos at the roadside, although they are more
commonly seen further on. Continue through this
forest, beyond a cleared area, until you reach a
second, better-developed forest patch. Soon after
this point there is an area of exposed rock on the
right-hand side of the road (2 on map), which
provides a fine place to stand, ideally with a scope,
and scan the juniper canopy for turacos. Also walk
slowly along the road either side ol this site, and
keep alert for ‘crashing’ sounds in the canopy,
nasal, squirrel-like trilling or explosive alarm calls,
or red wings gliding amongst the junipers. Beware,
though, that all of these can also indicate White-
cheeked Turaco. The forest beyond the exposed
rock, extending along another 2.6 km of road, is
also an excellent area for the turaco. Arero Forest
itself can feel rather birdless, but other species
include Hemprich’s Hornbill Tockus hemprichii,
Northern Brownbul Phyllastrephus strepitans and
White-breasted Cuckooshrike Coracina pectoralis.
Nechisar Nightjar Caprimulgus solala
So far as is known the Nechisar Nightjar is
endemic to the isolated grasslands of the Nechisar
Plain, at the western extremity of this EBA. To
date it is known with certainty only from the type
specimen, a single and distinctive wing famously
rescued from a decomposing roadkill in 1990
(Safford et al. 1993), and an excellent guide to
its potential field identification has already been
published in Bull. ABC (Butchart 2007). There
has recently (2009) been a tantalising first claim
of a live bird (I. Sinclair pers. comm.), although
full details remain forthcoming. It is probable that
an individual will need to be captured to confirm
this species’ continued existence.
Finding it. The Nechisar Plains lie within the
spectacularly beautiful Nechisar National Park,
1 08 -Bull ABC Vol 17 No 1 (2010)
Finding southern Ethiopia 's endemic birds: Spottiswoode
near the town of Arba Minch in the Great Rift
Valley. At the time of writing the agonisingly
poor road from Shashemene to Arba Minch was
being remade, which will hopefully simplify future
searches. 1 he black cotton soils of the plains are
crisscrossed by several tracks, a jolting 30 km
(occasionally impassable after rain) beyond the
park entrance, and this is also the best place in
the world to see the oddly localised White-tailed
Lark Mirafra albicuuda. The area is very good for
nightjars in general, with nine species occurring in
all, and a night search is likely to turn up one or
several of the following: Slender-tailed C. clarus ,
Star-spotted C. stellata, Donaldson-Smith’s C.
donaldsoni. Montane C. poliocephaliis and perhaps
even Standard-winged Macrodipteryx longipennis.
Liben (formerly Sidamo) Lark Heteromirafra
sidamoensis
The Liben Lark is a perilously threatened bird
confined to the arid grassland of the Liben Plain
near Negele, and recent surveys indicate that
fewer — probably far fewer — than 250 individuals
survive within its tiny range, which continues to
be rapidly squeezed by habitat loss through crop
planting, overgrazing and scrub encroachment
(Collar et al. 2008, Spottiswoode et al. 2009).
By 2009 it was confined to less than 3,000 ha of
heavily degraded habitat (Donald et al. in press).
It belongs to a uniformly imperilled genus of
highland grassland larks that also comprises the
Vulnerable Rudd’s Lark H. ruddi of South Africa
and rhe Critically Endangered Archer’s Lark H.
archeri of Somaliland, which has not been seen
with certainty since its discovery in 1922.
Finding it. For a species so close to extinction,
the Liben Lark could still, at the time of writing,
relatively easily be seen. It remains most numerous
at the western end of the Liben Plain (3 on Negele
map; around 05°16.37’N 39°4l.08’E), just south
(1-2 km) of a dilapidated but still active military
camp, which it is essential to avoid. The lark is
found in relatively short grass with very sparse or
absent shrubs. Early mornings are best (especially
06.30-09.30 hrs), seemingly year-round, when
males are most likely to be heard giving their short
skylark Alauda- like aerial song that is audible at
several hundred metres. Males hover as they sing
only c.lO m above the ground, resembling a fly
on the horizon before they parachute down after
about 20 seconds. At closer range, their incredibly
elongated hindclaws can be seen dangling
conspicuously. This short and largely stationary
song-flight contrasts with the long, high, circular
and somewhat chirruping song-flights of Somali
Short-toed Lark Calandrella somalica, which is
very common here. When flushed, Somali Short-
toed Lark is easily distinguished by its rather nasal
flight call (if anything, a flushed Liben Lark gives a
rather melodious tseep-eeep-eeep-eeep, reminiscent
of a Pectoral-patch Cisticola Cisticola bnmnescens ) ,
and on the ground by its relatively heavy pinkish
bill, conspicuous whitish eye-ring, heavily streaked
(rather than scalloped) mantle, and generally pot-
bellied and horizontal posture. The alternative
(if you are unable to visit in the morning) is to
walk until you flush a Liben Lark; they tend not
to fly, but run quickly and rodent-like through
the grass, occasionally standing upright to scan
their surroundings, showing their pale, triangular-
looking head, markedly scalloped back and pale
central crown-stripe.
Birds are thin on the ground on the Liben
Plain, but other interesting species to be seen
here are Hartlaub’s Bustard Eupodotis hartlaubi,
remarkably high concentrations of Kori Bustard
Ardeotis kori , Somali Courser Cursor somalensis,
Black- winged Lapwing Vanellus melanopterus ,
White-crowned Starling Spreo albicapillus,
whilst Prince Ruspoli’s Turaco and Salvadori’s
Seedeater Serinus xantholaemus occur nearby.
Quail Plover Ortyxelos meiffrenii has been seen
here, and occasionally small groups of unusually
easterly White-tailed Swallows Hirundo megaensis
(Gabremichael et al. 2009).
White-tailed Swallow Hirundo megaensis
The range of this species overlaps almost perfectly
with that of the Ethiopian Bush Crow; this
coincidence is not at all understood, since the
birds have quite different ecologies. White-tailed
Swallows have an extremely agile, bat-like flight,
and are typically seen speeding gracefully over
open savannah and scrubland. They especially
favour places with sparser cover, such as open
valleys, but sometimes occur over woodland. The
species was first collected by Con Benson and his
Mozambican collector, Jali Makawa, while they
were stationed at Mega during the Second World
War and did much pioneering work (Benson
1946). Benson suspected that they bred in hollows
in termite mounds, and this has been confirmed
Finding southern Ethiopia s endemic birds: Spottiswoode
Bull ABC Vol 17 No 1 (2010) -109
110 -Bull ABC Vol 17 No 1 (2010)
Finding southern Ethiopia ’s endemic birds: Spottiswoode
Legend to figures on opposite page
Figure 4. White-tailed Swallow /
Hirondelle a queue blanche Hirundo
megaensis, Liben Plain, Ethiopia, 29 June
2006 (Claire Spottiswoode)
Figure 5. Ethiopian (Stresemann’s)
Bush Crow / Corbin de Stresemann
Zavattariornis stresemanni, between
Yabello and Arero, Ethiopia, 29 May
2009 (Paul Donald)
Left: map of the Negele region of
southern Ethiopia
Below: map of the Yabelo region of
southern Ethiopia, with (inset) details of
the Arero Forest.
to occur (M. N. Gabremichael pers.
comm.), but circumstantial evidence
strongly suggests that they may also
nest against the interior beams of
Borana houses, as does the sympatric
Ethiopian Swallow H. aethiopica. Any
breeding records are of interest and
should be submitted to EWNHS.
Finding it. White-tailed Swallows
can be seen anywhere in the Yabelo-
Arero-Mega triangle, and are likely
simply to be bumped into during a
couple of days birding in the area. If
time is short and luck is low, though,
there are some specific areas that
are well worth focusing on. Perhaps
best of all is the open, heavily grazed
vicinity of the village of Dubuluk
(2 on the Yabelo map). Scanning
the open country immediately north
and south of the village is likely to
turn up a swallow. The arid, rocky
country along the gravel road from
the main Yabelo-Mega road to Soda
(turn-off at 04°09.56’N 38°16.83’E;
3 on map) is also good for swallows,
as well as species typical of arid stony
country such as Somali Courser,
Short-tailed Lark Pseudalaemon
fremantlii and Somali Fiscal Lanins
somalicus. (Note that a smaller short-
cut track — 4 on the map — leaving
the tar road a little further north,
Finding southern Ethiopia s endemic birds: Spottiswoode
Bull ABC Vol 17 No 1 (2010) -111
at 04°12.52’N 38°16.87’E, and rejoining the
main Soda dirt road at 04°11.51’N 38°20.59’E
is also very good for birding; you might choose
to return this way.) A third place to search is
the open, largely cultivated area just south of
Mega town, on the road to Moyale. Stop along
the road 6-1 4 km south of the town (3 on the
map; 04°01.05’N 38°22.02’E) scanning especially
in open areas along river valleys. Beware that
Ethiopian Swallows also occur in all of these areas,
but are readily distinguishable by their dark tails,
breast markings, and noticeably less agile flight.
Ethiopian (Stresemann’s) Bush Crow
Zavattariornis stresemanni
Ethiopia’s star endemic is also an evolutionary
and ecological enigma: its closest relatives are the
ground-jays Podoces of central Asia (Ericson et al.
2005), and it is bafflingly confined to a small scrap
of arid savannah in the triangle formed by Yabelo,
Arero and Moyale in Ethiopia’s far south. Happily
it is patchily common in this area, and very easily
seen. The first sign of its presence is often its nest,
a large gourd of spiny sticks with an upward-
facing entrance tunnel, sitting on the flat top of an
Acacia. It is highly social, confiding, wonderfully
characterful, and especially common and tame in
the vicinity of villages and livestock enclosures,
where it turns over pieces of livestock dung in
search of grubs, and even perches on cattle. Flocks
are noisy and mobile, frequently giving metallic,
Eurasian Jackdaw Corvus monedula-XiVt calls, from
which comes its Borana name, kaka. Although
bush crows are still relatively numerous, there is
much concern that they are currently declining
owing to the whittling away of their habitat of
mature Acacia savannah by commercial cultivation,
charcoal production, and bush encroachment
probably caused by overgrazing and fire supression
(Borghesio & Giannetti 2005, Gedeon 2006,
Mellanby et al. 2008).
Finding it. Seeing an Ethiopian Bush Crow is
still unlikely to pose any problems. Any area with
some tall acacias and ideally a village or animal
enclosure nearby is likely to reveal a party of bush
crows. If time is very short, an excellent area to
focus on is the tall woodland just north of Yabelo,
on the main road to Addis Ababa (map) and in
the vicinity of a small settlement called Harobake
(1 on the Yabelo map; 04°59.56’N 38°12.59’E),
where a livestock market is held on Sundays. The
combination of tall acacias, little ground cover,
and the presence of cattle and camel enclosures
is prime habitat for bush crows, but take care
when photographing them that no livestock are
in the background, as this can offend their
owners. Another area with a particularly good
concentration of bush crows is the first 10-40 km
of the dirt road from Yabelo to Arero, where bush
crows are almost invariably present in the vicinity
of small Borana settlements.
General birding in the Yabelo-Mega area is
tremendously diverse and exciting, long after the
first bush crows and swallows have been sighted.
Species likely to be seen during a 2-3-day visit
include Somali Courser, Vulturine Guineafowl
Acryllium vulturinum, Short-tailed Lark, Somali
Short-toed Lark, Foxy Lark Mirafra alopex. Scaly
Chatterer Turdoides aylmeri , Somali Crombec
Sylvietta isabellina, Pygmy Batis Batis perkeo,
Pringle’s Puffback Dryoscopus pringlii, Somali
Fiscal, Red-naped Bushshrike Laniarius ruficeps,
White-crowned Starling and Northern Grosbeak
Canary Serinus donaldsoni.
The future
Ail of southern Ethiopia’s endemics are threatened.
The turaco faces habitat destruction from wood
cutting and agriculture, and the lark, swallow and
bush crow from bush enroachment, agricultural
expansion and rangeland degradation. There are
hints that new species to science might still
await discovery in the region, but if so they will
doubtless find themselves listed as threatened as
soon as they are described. In the face of relentless
population pressure and large-scale vegetation
shifts hastened by climate change, the long-term
challenges to the birds of southern Ethiopia are
truly daunting. Yet there is reason for optimism,
not least that human and conservation interests
often coincide in this region: bush encroachment
and rangeland degradation favour neither birds
nor pastoralists (Spottiswoode et al. 2009, Donald
et al. in press). The 2010 Birdfair will be the first
to focus on the Afrotropics for many years and
will bring significant support to the invaluable
work of the Ethiopian Wildlife and Natural
History Society. Most urgently of all, their efforts
at grassland restoration on the Liben Plain should
give the Liben Lark a fighting chance of seeing out
the new decade.
112 - Bull ABC Vol 17 No 1 (2010)
Finding southern Ethiopia 's endemic birds: Spottiswoode
Acknowledgements
I am grateful to Nigel Collar, 1 im Dee, Paul Donald,
Julian Francis, John Miskell and Nigel Redman for
helpfully commenting on earlier drafts, and ro Julian
Francis and Merid Gabremichael for their support and
collaboration in the field.
References
Benson, C. W. 1946. Notes on the birds of southern
Abyssinia. Ibis 88: 287-306.
Borghesio, L. & Giannetti, F. 2003. Habitat degradation
threatens the survival of the Ethiopian bush crow
Zavattariornis stresemanni. Oryx 39: 44-49.
Borgeshio, L„ Gianetti, F„ Ndang’ang’a, K„ Shimelis,
A., Borghesio, A., Rizzo, D. & Fufa, K. 2004. A
reassessment of the conservation status of Prince
Ruspoli’s Turaco Tauraco nispolii. Bull. ABC 11:
104-111.
Butchart, S. 2007. Birds to find: a review of ‘lost’,
obscure and poorly-known African bird species.
Bull. ABC 14: 139-157.
Collar, N. J. 2009. Letter. Conservation-driven changes
in English bird names, and the case of the Liben
Lark. Bull. ABC 16: 245.
Collar, N. J., Dellelegn, Y., Fishpool, L. D. C.,
Gabremichael, M. N., Spottiswoode, C. N. &
Wondafrash, M. 2008. Type locality, behaviour,
voice, nest, eggs and plight of the Sidamo Lark
Heteromirafra sidamoensis. Bull. ABC 15: 180-
190.
Collar, N. J., Dingle, C., Gabremichael, M. N. &
Spottiswoode, C. N. 2009. Taxonomic status of the
Degodi Lark Mirafra degodiensis, with notes on the
voice of Gillett’s Lark M. gilletti. Bull. Br. Ornithol.
Club 129: 49-62.
Donald, P. D., Buchanan, G. M., Collar, N. J., Dellelegn
Abebe, Y., Gabremichael, M. N., Mwangi, M.
A. K., Ndang’ang’a, P. K., Spottiswoode C. N.
& Wondafrash, M. (in press) Rapid declines
in habitat quality and population size in the
Sidamo (Liben) Lark Heteromirafra sidamoensis
necessitate immediate conservation action. Bird
Conserv. Intern.
Ericson, P. G. P., Jansen, A. L., Johansson, U. S. &
Ekman, J. 2005. Inter-generic relationships of
the crows, jays, magpies and allied groups (Aves:
Corvidae) based on nucleotide sequence data. J.
Avian Biol. 36: 222-234.
Gabremichael, M. N., Spottiswoode, C. N., Fishpool,
L. , Forsyth, E., Lewis, A., Pain, D., Thomas, R.
& Toye, N. 2009. Occurrence of the White-tailed
~ Swallow Hirundo megaensis near Negele, Ethiopia.
Bull. ABC 16: 83-86.
Gedeon, K. 2006. Observations on the biology of the
Ethiopian Bush Crow Zavattariornis stresemanni.
Bull. ABC 13: 178-188.
Lernould, J.-M. & Seitre, R. 2002. Observation
d hybrides naturels entre le Touraco a joues
blanches Tauraco leucotis et le Touraco du Prince
Ruspoli T. ruspolii. Alauda 70: 247-251.
Mellanby, R. J., Ross, B., Watt, A., Wondafrash,
M. , Ewnetu, M., Broadhurst, C., Critchlow, R.,
Dadesa, A., Deas, T., Enawgaw, C., Gebremedin,
B., Graham, E., MacLean, S., McKean, M., Collar,
N. J. & Spottiswoode, C. N. 2008. Distribution,
abundance and habitat preferences of White-tailed
Swallow Hirundo megaensis and Ethiopian Bush-
crow Zavattariornis stresemanni , two southern
Ethiopian endemics. Bird Conserv. Intern. 18:
395-412.
Safford, R. J., Ash, J. S., Duckworth, J. W., Telfer, M.
G. & Zewdie, C. 1995. A new species of nightjar
from Ethiopia. Ibis 137: 301-307.
Spottiswoode, C. N., Wondafrash, M., Gabremichael,
M. N., Dellelegn, Y., Mwangi, M. K., Collar, N.
J. & Dolman, P. M. 2009. Rangeland degradation
is poised to cause Africa’s first recorded avian
extinction. Anim. Conserv. 12: 249-257.
Spottiswoode, C. N., Gabremichael, M. N. & Francis,
J. E. (in press) Finding Birds in Ethiopia. London,
UK: Christopher Helm.
Stattersfield, A. J., Crosby, M. J., Long, A. J. & Wege,
D. C. 1998. Endemic Bird Areas of the World:
Priorities for Biodiversity Conservation. Cambridge,
UK: BirdLife International.
Department of Zoology, University of Cambridge,
Downing Street, Cambridge CB2 3EJ, UK. E-mail:
cns26 @cam. ac. uk
Received 22 December 2009; revision accepted 25
January 2009.
Finding southern Ethiopia 's endemic birds: Spottiswoode
Bull ABC Vol 17 No 1 (2010) -113
Recent Reports
These are largely unconfirmed
records published for interest only;
records are mostly from 2009,
with a few from earlier dates. We
thank all birders who have sent
in their records and urge them to
submit full details to the relevant
national or regional organisations.
It is suggested that observations
of each species be compared with
relevant literature to set new data in
context and that observers who are
unfamiliar with the status of birds
in a particular country refer to R.
J. Dowsett’s (1993) Afrotropical
avifaunas: annotated country
checklists (in R. J. Dowsett & F.
Dowsett-Lemaire. A Contribution
to the Distribution and Taxonomy
of Afrotropical and Malagasy Birds.
Tauraco Res. Rep. 5. Liege: Tauraco
Press) or more recent or appropriate
sources before submitting records.
Les observations ci-apres sont en
majeure partie non confirmees et
sont publiees uniquement dans le
but d informer. La plupart des
donnees sont de 2009 ; quelques-
unes sont plus anciennes. Nous
remercions tous les ornithologues
qui ont pris la peine de nous
faire parvenir leurs donnees
et nous recommandons de les
envoyer, dument documentees,
aux organisations nationales
ou regionales concernees. II est
conseille de verifier le statut des
especes observees dans la litterature
appropriee, afin de mettre les
nouvelles donnees en perspective,
et de consulter notamment R.
J. Dowsett (1993) Afrotropical
avifaunas: annotated country
checklists (en R. J. Dowsett & F.
Dowsett-Lemaire. A Contribution
to the Distribution and Taxonomy
of Afrotropical and Malagasy Birds.
Tauraco Res. Rep. 5. Liege :
Tauraco Press) ou des sources plus
recentes ou appropriees.
Azores
The following records are from
May-November 2009. The second
Black-capped Petrel Pterodroma
hasitata for the Azores was
photographed south of Queimada,
Pico, on 22 May (the first was on 26
May 2007), whilst the fifth Trindade
Petrel P. arminjoniana was a dark
morph photographed south of Faial
on 20 August. The Pied-billed
Grebe Podilymbus podiceps at Lagoa
das Furnas, Sao Miguel, first seen on
9 November 2008, was joined by a
first-year on 29 October with both
remaining to at least late November;
a third was on Flores in October-
November. An adult Brown Booby
Sida leucogaster was on the Mosteiros
cliffs, Sao Miguel, in November.
Double-crested Cormorants
Phalacrocorax auritus were seen on
Flores in October (one) and Sao
Miguel in November (up to two).
On Santa Maria, an American
Bittern Botaurus lentiginosus was
observed on 1 1 October, and the
long-staying Cattle Egret Bubulcus
ibis at Vila harbour pool through
October. Up to two American Great
Egrets Egretta alba egretta were on
Corvo in September-November,
with a Great Blue Heron Ardea
herodias there on 20-23 October
(and one on Flores on 30 October).
A White Stork Ciconia ciconia on
Terceira on 30 August was the first
for the Azores.
The third Greater White-fronted
Goose Anser albifrons for the Azores
remained at Vila harbour pool, Santa
Maria, until 4 June. A Pale-bellied
Brent Goose Branta ( bernicla ) hrota
was on Corvo from 18 October. On
Terceira, a flock of up to 19 Blue-
winged Teals Anas discors was seen
on 14-22 October, a juvenile Surf
Scoter Melanitta perspicillata from 3 1
October into November, and a male
Long-tailed Duck Clangula hyemalis
on 1 1-13 June. A female-plumaged
Ruddy Duck Oxyura jamaicensis on
Flores on 30 October that appeared
at Cabo da Praia, Terceira, next day,
is the first for the archipelago. Single
Taiga Merlins Falco columbarius
columbarius were reported on Corvo
on 3 November and Flores on
21 October and 4 November. If
accepted, a first-year Barbary Falcon
F. peregrinoides at Anjos, Santa
Maria, on 12 August will be the first
for the Azores.
Semipalmated Plovers Charadrius
semipalmatus were reported on
Terceira, in June-July and October-
November, on Sao Miguel on 17-23
October (up to two), and on Flores
on at least 21 October (up to four).
A Kildeer C. vociferus was on Flores
on 17-18 October and up to three
Eurasian Dotterels C. morinellus
on Corvo from 10 October into
November. Records of Calidris
sandpipers included Semipalmated
Sandpipers C. pusilla at Cabo da
Praia, Terceira, in early September
(three) and on Corvo on 16-23
October (one), a Western Sandpiper
C. mauri at Cabo da Praia, Terceira,
from 2 September, Least Sandpipers
C. minutilla on Corvo, on 14
September and 18-23 October (one),
Sao Miguel on 13 October (one),
Terceira on 14-31 October at least
(one), and Flores on 14-18 October
(one), White-rumped Sandpipers C.
fuscicollis on Terceira in September
(two) and at Caldeirao, Corvo, on
14 September (four), and Pectoral
Sandpipers C. melanotos at Cabo da
Praia, Terceira, from 2 September
114 - Bull ABC Vol 17 No 1 (2010)
Recent Reports
Figure 1 . Thick-billed Cuckoo / Coucou d’Audeberc Pachycoccyx audeberti, Gbadagba Game Ranch, north of Djidja, Zou,
Benin, 1 1 February 2009 (Bruno Portier)
Figure 2. Male Barka Indigobird / Combassou de Barka Vidua larvaticola , near Didani, west of Cobly, Benin, 30 August 2009
(Johannes & Sharon Merz)
(three). Other waders included a Jack
Snipe Lymnocryptes minimus on Sao
Miguel in October, Wilson’s Snipes
Gallinago (gallinago) delicata on Sao
Miguel on 25 October (two shot), on
Corvo in October— November, and
on Flores from 15 October (one).
An Upland Sandpiper Bartramia
longicauda was on Flores on 14-18
October and a Solitary Sandpiper
Tringa solitaria flew in off the sea
at Anjos on Santa Maria on 12
October. On Terceira, a Spotted
Sandpiper Actitis macularius and a
Willet Catoptrophorus semipalmatus
were found in September.
Gull records on Terceira include
a Laughing Gull Larus atricilla on
22 October and 3 November (with
another on Flores on 30 October)
and a first-year Bonaparte’s Gull L.
Philadelphia on 3 1 October and an
adult on 19 November. Two Sooty
Terns Sterna fuscata were still at
Ilheu da Vila, Santa Maria, during
June, but they failed to hatch young.
On Pico, possibly the same Bridled
Tern 5. anaethetus first reported this
year on 24 April was still present at
Manhenha in June. On Terceira,
a first-year American Black Tern
Chlidonias niger surinamensis
stayed at Cabrito reservoir from 1 1
September and a White-winged
Tern C. leucopterus was observed on
1 1-18 October.
Yellow-billed Cuckoos Coccyzus
americanus were recorded on Corvo
on 15-30 October (at least two)
and Sao Jorge on 16 October (one).
A Common Nighthawk Chordeiles
minor was on Corvo on 9 October,
and single Chimney Swifts Chaetura
pelagica on Corvo on 23-27 October
and Terceira on 31 October.
Four firsts for the Azores include a
Greater Short-toed Lark Calandrella
brachydactyla on Sao Jorge on 17
October, a possible Plain Martin
Riparia paludicola on Santa Maria on
28 May, a Citrine Wagtail Motacilla
citreola on Corvo on 14 September,
and a Ring Ouzel Turdus torquatus ,
also on Corvo, on 1-15 November.
Up to two BufF-bellied Pipits
Anthus rubescens were on Corvo
from 17 October to 15 November.
A ‘black-eared wheatear Oenanthe
hispanica / melanoleuca on Santa
Maria on 9 September was the
second for the archipelago.
As in previous years, an impressive
number of New World passerines
was reported in September-
November, including four firsts for
the Azores: on Corvo, a Canada
Warbler Wilsonia canadensis on
12 October and a Chestnut-sided
Warbler Dendroica pensylvanica on
13 October; and on Flores, a Dark-
eyed Junco Junco hyemalis on 5
November and two Dickcissels Spiza
americana on 6 November. Other
species seen, mainly in October, on
Corvo, include a White-eyed Vireo
Vireo griseus, a Yellow-throated
Vireo V. flavifrons, at least one
Philadelphia Vireo V. philadelphicus,
at least two Red-eyed Vireos V.
olivaceus , Black-and-white Warbler
Mniotilta varia, a Northern Parula
Parula americana , an American
Yellow Warbler Dendroica petechia,
up to two Black-throated Green
Warblers D. virens, a Myrtle
Warbler D. coronata, an American
Redstart Setophaga ruticilla, up to
two Ovenbirds Seiurus aurocapilla,
up to three Common Yellowthroats
Geothlypis trichas , a Savannah
Sparrow Passerculus sandwich ensis,
a Rose-breasted Grosbeak
Pheucticus ludovicianus , Indigo
Bunting Passerina cyanea, Bobolink
Dolichonyx oryzivorus and Baltimore
Oriole Icterus galbula. Flores held a
female Magnolia Warbler Dendroica
magnolia, a female Scarlet Tanager
Piranga olivacea, a Savannah
Sparrow, a White-crowned Sparrow
Zonotrichia leucophyrs, a Lapland
Bunting Calcarius lapponicus, a
Rose-breasted Grosbeak, an Indigo
Bunting and a Baltimore Oriole
(per Dutch Birding3\: 252-257,
311-322, 383-389).
Benin
Records from 2009 include the
following. Two Streaky-breasted
Flufftails Sarothrura boehmi were
heard and a female flushed in
rice fields east of Cobly, Atacora
department, on 5 September; the
Recent Reports
Bull ABC Vol 17 No 1 (2010) -115
next day a female and two juveniles
were seen at close range. These
are apparently the first records for
Benin (JM & SM). The following
species were found outside the range
indicated in Borrow & Demey
(2004. Field Guide to the Birds of
Western Africa). A Thick-billed
Cuckoo Pachycoccyx audeberti was
observed at Gbadagba Game Ranch,
north of Djidja, Zou, on 11 February
and 30 April (Fig. 1; BP). Zitting
Cisticolas Cisticola juncidis were
observed at several localities in the
communes of Cobly, Tanguieta
and Boukoumbe, Atakora, in the
north-west, and also at Cotonou, in
June-September. Two Whistling
Cisticolas Cisticola lateralis were
photographed and their song tape-
recorded 8 km east ofTchaourou,
Borgou, on 22 August. Two male
indigobirds with a greenish gloss
and uttering a call similar to that of
Black-faced Firefinch Lagonosticta
larvata near Didani, west of Cobly,
on 30 August, were thought to be
Barka Indigobirds Vidua larvaticola
(Fig. 2; JM &SM).
Botswana
The following records are from May
2009-early January 2010. Single
Black-necked Grebes Podiceps
nigricollis were observed at Lobatse
sewage ponds on 26 July (57), in the
Nata River close to Nata Delta on 7
September (PN) and on a small pan
near Ghanzi on 26 November ( KG ).
Some 36 Great White Pelicans
Pelecanus onocrotalus , including
brown immatures, were counted
along the Boteti River between
Makalamabedi and Samedupi in
late July (57); c.42 were at Shashe
Dam on 26 July, with 55 there on
23 January (PDA, NBo et al.), and
43 at Nata Delta on 10 August
( CB ). A single Pink-backed Pelican
P. rufescens was seen along the
Okavango River between Mohembo
and Shakawe on 1 8 July (PH et
al.); 45 were noted along the Savuti
Channel between Mantswe Pan and
Zibadianja on 17 July (GH, BG), one
at Bokaa Dam on 10 January (CB),
and 13 at Shashe Dam on 23 January
(PDA, NBo).
An African Openbill Anastomus
lamelligerus at a pan in the extreme
south-west in November, was well
out of range (ME); there was a large
influx of this species in South Africa
at the same time. Another was at
Thagale Dam, north ofMochudi
in the south-east on 23 January;
this is only the third record for this
region of Botswana (CB). Two Black
Storks Ciconia nigra were seen at
the Crocodile Pools in Mokolodi
Nature Reserve on 6 December
(DMc, MG, CV et al.). Large flocks
of c.300 Woolly-necked Storks
C. episcopus were noted in Moremi
Game Reserve in early January
(MM, AF). A single White Stork
C. ciconia, probably from the South
African breeding population, spent
the winter at Malema Pan in Khama
Rhino Sanctuary (IW); two were
at Mokubilo Pan on 30 July (57)
and one was at Lake Ngami on 17
August (CB). Unusual in south-east
Botswana, a Saddle-billed Stork
Ephippiorhynchus senegalensis was
at Mokolodi Nature Reserve, near
Gaborone, in late October-early
November (GB, SB). Few Greater
Flamingos Phoenicopterus (ruber)
roseus were seen in July, other than
four at Phakalane sewage ponds,
near Gaborone, on 5 th (JD), three
at Ramotswa sewage ponds and one
at Thagale Dam on 12th, and 52 at
Bokaa Dam on 26th (CB), a single at
Rysana Pan on 31st (57), with 300
at Nata Delta on 10 August; on 18
October there were 80 at Bokaa Dam
(CB). In mid December r.100,000
Lesser Flamingos Phoenicoenias
minor were in the country, including
c.60,000 along the edge of Sua Pan
and 10,000 at Nata Sanctuary (CB).
Two Fulvous Whistling
Ducks Dendrocygna bicolor were at
Phakalane sewage ponds on 5 July
(JD), one at Bokaa Dam on 18
October, and eight at Thagale Dam
on 23 January (CB). White-backed
Ducks Thalassornis leuconotus were
seen at Mogobane Dam on 22 July
(one: CB), at Lake Ngami on 29
July (174: RR, PFf) and at Mokolodi
Crocodile Pools on 6 December
(two: DMc, MG et al ). At Thagale
Dam, 260 Southern Pochards
Netta erythrophthalma (with 670 at
nearby Bokaa Dam) on 23 January
represents a good count (CB). July
counts of Maccoa Ducks Oxyura
maccoa included two at Phakalane
sewage ponds on 5th (JD), five at
Jwaneng sewage ponds and 77 at
Moshupa Dam on 20th (MG, DG,
HH) and three at Lobatse sewage
ponds on 26th (57); one was at
Mokolodi Crocodile Pools on 6
December (MG et al.) and 32 were at
Sekagwana Dam, near Modipe Hill,
in late December-early January (IW).
An Osprey Pandion haliaetus
was at Lake Ngami in late December
(CB). Three Hooded Vultures
Necrosyrtes monachus were at a Giraffe
Giraffa Camelopardalis carcass and
four at a pan in Moremi game reserve
on 9 August (57), with six between
Xakanaxa and Paradise pools on
15 September (PN). Lappet-faced
Vulture Torgos tracheliotus records
include three south of Ghanzi on
28 May (DB, BB), a pair nesting in
the Central Kakahari Game Reserve
in May (GH), one near Gaborone
on 12 July (CB), one with White-
backed Vultures Gyps africanus near
Mopipi and two near Rakops on
31 July, one near Samedupi on 1
August (57), two in Khutse Game
Reserve in September and one at
Nxai pan on 9 September (PN).
Single White-headed Vultures
Trigonoceps occipitalis were seen at the
Khwai River on 9 August (57) and in
Khutse Game Reserve in September
(CB). A European Honey Buzzard
Pernis apivorus was photographed
along the Old Matsiloje road south-
east of Francistown on 22 November
(MS). A juvenile Western Marsh
Harrier Circus aeruginosus was seen
at Gaborone Game Reserve on 21—22
December (IW) and a Pallid Harrier
C. macrourus in Khutse Game
Reserve on 28 November (CV). A
pair of Black Sparrowhawks Accipter
melanoleucus was between Crocodile
Pools, Ngotwane, and Ramotsa on 7
July (CB) and one was also regularly
seen near Maun in late December-
early January (MM). Lesser Kestrels
Falco naumanni were seen in Khutse
Game Reserve on 28 November ( CV)
and a Eurasian Hobby F. subbuteo
north of Sua in early December (CB).
116 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
African Crakes Crex egregia were
frequent along the northern edge
of Lake Ngami in late December
(CB). An estimated 2,000-3,000
Black-winged Stilts Himantopus
himantopus were at the same lake in
August {MM, AF , CB, ST). In early
December, c. 100 Black-winged
Pratincoles Glareola nordmanni
were 20 km east of Sua Spit within
Nata Sanctuary, Makgadikgadi Pans
{CB)-, a group of 4-8 was seen at
Segakwana Dam, in the south-east,
on 24 and 26 December {IW), 180
at Bokaa Dam on 10 January, and
one at Thagale Dam on 23 January
{CB). A Caspian Plover Charadrius
asiaticus at Lake Ngami on 17 August
was early. Thirty-six Common
Ringed Plovers C. hiaticula were at
Bokaa Dam on 18 October. At Nata
Delta, a single Chestnut-banded
Plover C. pallidus and four Bar-
tailed Godwits Limosa lapponica
were seen on 10 August {CB). Green
Sandpipers Tringa ochropus were
present along the Kwando River in
the Caprivi on 27 October (one), at
Mowana on 1 November (two), and
at the sewage works west of Gang in
early November (one) (per 777). A
Ruddy T urnstone Arenaria interpres
was at Bokaa Dam on 19 September,
with two there on 18 October {CB).
Caspian Tern Sterna caspia records
include two at Lake Ngami in late
December {CB), one at Phakalane
sewage ponds in early January
(per IW) and two at Bokaa Dam
on 10 January {CB). Due to high
water levels, there were few records
ol African Skimmers Rynchops
flavirostris, but on the Okavango
River, where levels were dropping
by mid July, two were observed
between Mohembo and Shakawe
Lodge on 18 July and ten between
Phillipo Channel junction, one at
the Nxamaseri turn-off and three on
the Phillipo Channel on 19 July {PH
et al.)] at least one was at Mowana
Lodge, Kasane and on the Chobe
River within the park on 26-27
August {HH).
An African Cuckoo Cuculus
gularis was calling at Ngotwane,
south of Gaborone, on 28
September — a very early date. Also
there, a Klaas’s Cuckoo Chrysococcyx
klaas was calling on 29 September.
Of note was a pair of Grey-headed
Kingfishers Halcyon leucocephala at
Kumakwane, in the Gabane Hills, on
1 November {CB, MG et all)-, this is
a summer visitor mainly to northern
Botswana. A Black Cuckooshrike
Campephaga flava south of Gaborone
on 25 September is an early record. A
single Grey Wagtail Motacilla cinerea
on a lawn at Chobe Safari Lodge,
Kasane, on 12 November {RR) was
only the fourth record for Botswana.
Along the Thamalakane River in
Maun, 5-6 Thrush Nightingales
Luscinia luscinia were heard in early
January {MM, RR).
Cameroon
Records from Domaine de
Petpenoun, near Foumban, West
Province, in October 2009, include
eight White-faced Whistling Ducks
Dendrocygna viduata , on lower
Petpenoun Lake (larger numbers
occur on nearby Bamenjin reservoir)
and a pair of Fox Kestrels Falco
alopex in the crater of the extinct
volcano Mbapit. There are rather few
records of these species from the area
( JvdW) .
Canary Islands
Records from May— November
2009 include the following. On
Lanzarote, Red-billed Tropicbirds
Phaethon aethereus were observed
off Arrecife on 27 May (one), at
Costa Teguise on 7 July (two), and
again off Arrecife on 14 November
(a first-year). A Wood Duckv4/x
sponsa was at Erjor Ponds, Tenerife,
on 18 August. A Purple Swamphen
Porphyrio porphyrio was picked up
exhausted on Gran Canaria on 2
October and, after fully recovering,
was released on 25 October and seen
again next day.
Noteworthy waders include a
juvenile American Golden Plover
Pluvialis dominica at Las Martela
ponds, La Palma, on 19 October,
an adult Least Sandpiper Calidris
minutilla at Charca de Maspalomas,
Gran Canaria, on 6-8 August, a
juvenile Pectoral Sandpiper C.
melanotos at an irrigation pond near
El Medano, Tenerife, on 7 October,
and a juvenile Greater Yellowlegs
Tringa melanoleuca near Las Palmas,
Gran Canaria, on 22-24 August.
A Bar-tailed Lark Ammomanes
cinctura was found with a Trumpeter
Finch Bucanetes githagineus near
Roquito del Fraile, Tenerife, on 9
October. Single Yellow-browed
Warblers Pbylloscopus inornatus
were observed on Lanzarote from 23
October to 19 November at least and
at Betancuria, Fuerteventura, on 15
November (per Dutch Birding 5 1 :
317, 370-383; Birding World 22:
236, 279, 373,416, 456).
Egypt
In April-October 2009 the following
were reported. A Red-billed
Tropicbird Phaethon aethereus was
seen near Surnaka Island, south
of the Ras Banas peninsula, on
7 August (per Dutch Birding 31:
313). Two Goliath Herons Ardea
goliath were seen again north of
Bir Shalatin in October (per Dutch
Birding 31: 370). An African
Openbill Anastomus lamelligerus
photographed on Crocodile Island,
Luxor, on 26 May will be the first
for Egypt, if accepted (per Dutch
Birding 31: 253). At El Gouna golf
course, at least three Black-winged
Pratincoles Glareola nordmanni
were seen on 9 April and a Caspian
Plover Charadrius asiaticus on 9-13
May (per Sajidgrouse 31: 209-210).
Up to three Three-banded Plovers
C. tricollaris were found at Aswan on
9-10 September. The first Richard’s
Pipit Anthus richardi reported in
autumn 2009 was as early as 12
September (per Dtitch Birding 31:
317-319).
Ethiopia
The following records are from
November 2009. A first-winter
Slender-billed Gull Larus genei was
photographed at Lake Awassa on 1 2
November; there are very few records
in Ethiopia (Fig. 3; AB). At Dinsho,
in the Bale Mountains, an African
Long-eared Owl Asio abyssinicus was
also photographed (Fig. 4; SR)-, this
generally uncommon species is locally
common in Ethiopia. More than ten
Egyptian Nightjars Caprimulgus
aegyptius were claimed from the Bilen
area on 25 November; Ash & Atkins
Recent Reports
Bull ABC Voi 17 No 1 (2010) -117
Figure 3. First-winter Slender-billed Gull / Goeland railleur Larus genei, Lake
Awassa, Ethiopia, 12 November 2009 (Artur Bujanowicz)
Figure 4. African Long-eared Owl / Hibou d’Abyssinie Asio abyssinicus, Dinsho,
Ethiopia, November 2009 (Steve Rooke / www.sunbirdtours.co.uk)
Figure 5. Grey-headed Silverbill / Capucin a tete grise Lonchura griseicapilla,
Yabello, Ethiopia, 15 November 2009 (Kris Blachowiak)
Figure 6. Wilson’s Phalarope / Phalarope de Wilson Phalaropus tricolor, Cape
Lopez, Gabon, 10 October 2009 (Guillaume Passavy)
Figure 7. Red Phalarope / Phalarope a bee large Phalaropus fulicarius, near
Georgetown, Central River Division, The Gambia, 12 November 2009 (John
Cooper)
Figure 8. Eurasian Bittern / Butor etoile Botaurus stellaris , near the White Volta,
Ghana, 4 December 2009 (Daphne Gemmill)
(2009. Birds of Ethiopia & Eritrea)
mention only a single record. A male
Menetries’s Warbler Sylvia mystacea
observed at Lalibela on 29 November
represents a new site for this rarely
observed Sylvia. A Grey-headed
Silverbill Lonchura griseicapilla
was photographed at Yabello on 15
November; there are few records of
this uncommon species (Fig. 5 \AB).
Gabon
A Wilson’s Phalarope Phalaropus
tricolor was photographed at Cape
Lopez on 10 October 2009 (Fig. 6;
GP ).
The following records from the
south-west, all outside the range
indicated on the distribution maps in
Borrow & Demey (2004. Field Guide
to the Birds of Western Africa), are
from late December 2009-January
2010. An adult Allen’s Gallinule
Porphyrio alleni was observed near
Moupia, south of Franceville, on 11
January and a juvenile at Gare de
Moanda on 1 4th. A Black-collared
Lovebird Agapornis swindernianus,
perhaps losely associated with
numerous Red-headed Lovebirds A.
pullarius, was seen in Moanda town
on 6 January. About 250 African
River Martins Pseudochelidon
eurystomina were perched on wires in
Bakoumba, south-west of Moanda,
on 3 January, whilst singles, in the
company of other hirundines, were
seen at Moyabi, near Moanda, on
7th, at Mounana on 8th, and at
11 8 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
Lekoni bridge, on the Franceville-
Okondja Road at Onvouri-Oulinga,
on 10th. Several Mountain Wagtails
Motacilla clara were on a stream just
west of Kessala along the Franceville—
Kessala road on 9 January. A pair of
Violet-tailed Sunbirds Anthreptes
aurantium was observed at Eaux
Claires near Lekoni on 29 December
and several Reichenbach’s Sunbirds
Anabathmis reichenbachii in swamps
at the outskirts of Moanda on 3
January and at Franceville on 9th.
Several Yellow-billed Oxpeckers
Buphagus africanus were seen on
African Buffaloes Syncerus caffer
near Moupia, south of Franceville,
on 11 January. On 31 December,
a small flock of Zebra Waxbills
Sporaeginthus subflavus was recorded
outside Lekoni town (KD).
The Gambia
A belated report, from November
2008, concerns a pair of Common
Moorhens Gallinula chloropus
breeding and producing six young at
Kartong, Western Division (WD);
this is the first definite breeding
record for the country. Also there,
single Great Reed Warblers
Acrocephalus arundinaceus were mist-
netted on 25 and 28 April 2009;
there are few previous records (JH).
In July 2009-January 2010 the
following were reported. A Dwarf
Bittern Ixobrychus sturmii stayed at
Kotu, WD, in December-January;
this species is rarely seen on the coast
(per KR). Twenty Black Storks
Ciconia nigra were observed near
River Gambia National Park, Central
River Division (CRD), on 24 January
( MSe ); although still rare, this species
is being increasingly recorded. A Bat
Hawk Macbeirbampbus alcinus was at
Lamin Kotu, WD, on 5 November.
Thirty adult Rtippell’s Vultures Gyps
rueppellii bathing near N’jau, CRD,
on 6 November is a remarkably
large number at the end of the
rains (per CBa). An Ayres’s Hawk
Eagle Hieraaetus ayresii was seen at
Tanku Bolong, Bao Bolon Wetland
Reserve, North Bank Division, on 5
January (WT); there are an increasing
number of reports of this species,
which was formerly considered rare,
from a variety of wooded habitats in
The Gambia. A Little Buttonquail
Turnix sylvaticus was observed at
Farasuto, WD, on 7 December;
this species is rarely seen {CBa).
On 17 November, two Senegal
Lapwings Vanellus lugubris were at a
small pool near Lamin Lodge, WD
(PS). A Red Phalarope Phalaropus
fulicarius was feeding in rice fields at
Jahally Swamp, near Georgetown,
CRD, on 12 November (Fig. 7;
JQ. At Wassu, CRD, a Red-necked
Nightjar Caprimulgus ruficollis
corpse was found on the road on
5 November (CBa). A Black-and-
white Mannikin Loncbura bicolor
was reliably reported by a ranger at
Brufut, WD, on 12 July (AJ)\ this
would be the first record for The
Gambia, if accepted.
Ghana
The following records are from late
November-early December 2009. A
Eurasian Bittern Botaurus stellaris
was photographed at a flooded pan
near the White Volta on 4 December
(Fig. 8). At Sakumo Lagoon, an
American Golden Plover Pluvialis
dominica was observed on 2 1
November. A male Blue Rock
Thrush Monticola solitarius was
found in the Tongon Hills on 6
December and a Western Bonelli’s
Warbler Pbyllosco pus bonelli was near
Tono Dam on 5th; subsequently four
were seen there. Nimba Flycatcher
Melaenornis annamarulae was seen
again in Atewa Forest (where it was
discovered in 2006: see Bull. ABC 15:
95-96) on 8 December. Two White-
billed Buffalo Weavers Bubalomis
albirostris were east of Bolgatanga
on 5 December, whilst two Ortolan
Buntings Emberiza bortulana were in
the Tongon Hills on 6th (DIP).
Guinea
In November-December 2009,
a search for Sierra Leone Prinia
Schistolais leontica was conducted at
1 1 sites in the Fouta Djalon, from
‘La Dame du Mali’ in the north to
Dalaba in the south. The species was
encountered only at Dalaba, where
five pairs were located in a small
and threatened forest behind the old
colonial governor’s residence in the
centre of town (10°40’N 12°16’W),
at 1,196-1,314 m, on 1 1-12
December (MBC & KS). There is
only one previous record of Sierra
Leone Prinia in the Fouta Djalon,
involving a single pair near Dalaba at
1,160 m in October 1999 (see Bull.
ABC 13: 45-48).
Kenya
The following reports are from
July-December 2009, with
additional records from April-June
2009 not mentioned in previous
Recent Reports. Several White-tailed
Tropicbirds Phaethon lepturus were
seen off Kiwaiyu, north of Lamu,
in early November; this species is
probably more common than reports
suggest, due to the lack of observers
at sea. A Eurasian Honey Buzzard
Pernis apivorus was at Lake Baringo
Club on 18 April — this species is
uncommon in the Rift Valley; two
Recent Reports
Bull ABC Vol 17 No 1 (2010) -119
were observed in Kakamega Forest
on 22-23 September and a third
near Kisumu on 25 September — it is
normally only occasional in western
Kenya. An Ovampo Sparrowhawk
Accipiter ovampensis, a scarce species
in Kenya, was seen at Kichwa
Tembo, Masai Mara, on 25 April. An
adult female Eurasian Sparrowhawk
A. nisus was photographed in Tsavo
West National Park (=NP) on 17
November (Fig. 9); this probably
overlooked species is only recorded
every few years. In 2009, there were
several records of Lizard Buzzard
Kaupifalco monogrammicus in
Nairobi, where it is normally rare.
Displaying Red-winged
Francolins Francolinus levaillantii
were observed on the Keekorok
road, Masai Mara, on 26 April;
this is the first record in Kenya for
over 20 years. Two juvenile Allen’s
Gallinules Porphyrio alleni on a pond
at Nguu Tatu, Mombasa, on 15
August, are suggestive of breeding. A
Baillon’s Crake Porzana pusilla was
at Sukari Dam, Brookside Dairies,
Thika, on 23 September; this species
is very rarely recorded in Kenya. A
Eurasian Oystercatcher Haematopus
ostralegns on the beach at Watamu,
on 5-6 November, is the first record
there for many years. A Eurasian
Thick-knee Burhinus oedicnemus
was photographed near Lukenya,
Machakos, on 15 November (Fig.
10); this is the first record in Kenya
for many years. Four Madagascar
Pratincoles Glareola ocularis at
Sabaki on 4 April is an early date.
A flock of c.50 Caspian Plovers
Charadrius asiaticus at Aruba, Tsavo
East NP, on 16 September, is an
unusually high number for eastern
Kenya. A Temminck’s Stint Calidris
temminckii at Lake Jilore, Malindi,
on 5 April, is noteworthy as there are
relatively few coastal records.
Seven Namaqua Doves Oena
capensis in Nairobi NP on 20 June
suggest a local influx to an area
where the species is rare. Also in
Nairobi NP, a Thick-billed Cuckoo
Pachycoccyx audeberti was seen on
3 May (second inland record) and
an immature Eurasian Cuckoo
Cuculus canorus on 21 September
(an early date). An adult Eurasian
Scops Owl Otus scops was ringed
at Lions Bluff, Lumo Conservancy,
Taita, on 21 November. Another late
record is a Forbes-Watson’s Swift
A pits berliozi at Arabuko-Sokoke on
4 April. On 4 August, a Bar-tailed
Trogon Apaloderma vittatum was
photographed in Masai Mara, where
the species is rarely recorded.
Friedmann’s Larks Mirafra pulpa
were reported in Shaba National
Reserve on 15 April (three) and in
Tsavo West NP on 20 November
(at least three singing). If accepted,
two Greater Short-toed Larks
Calandrella brachydactyla behind
Turtle Bay Beach Club, Watamu, on
5 November, will be the third record
for Kenya. A Red-rumped Swallow
Cecropis daurica of the Palearctic race
rufula was ringed at Ngulia, Tsavo
West NP, on 19 December; this will
be the first record of this race for East
Africa, if accepted. A Yellow Wagtail
Motacilla flava of the white-headed
race leucocephala was seen on Solio
Ranch on 16 April — this race is very
uncommon in Kenya; an adult flava-
type in Nairobi NP on 13 September
was very early. Three Sharpe’s
Longclaws Macronyx sharpei were
observed in grasslands 1 1 km west of
Molo near the Mau Forest, on the
western escarpment, on 16 August;
this endemic is mostly reported
from the highlands east of the Rift.
A Common Redstart Phoenicurus
phoenicurus ringed at Ngulia, Tsavo
West NP, on 20 December, is only
the 12th to be ringed there since
1969, during which time almost half
a million birds have been ringed at
this well-known site. An adult female
Whinchat Saxicola rubetra stayed
in Nairobi NP from 20 June to 28
August; it is unusual for this species
to over-summer.
An Acrocephalus ringed at Ngulia,
Tsavo West NP, on 17 December
had all the features of Blyth’s Reed
Warbler A. dumetorunr, blood
samples are being analysed and if
the results and the description are
accepted, this will be the first record
for Africa. Further noteworthy
records from Nairobi NP include
a Grey Penduline Tit Anthoscopus
caroli on 13 November (possibly
the first since 1971), a Red-billed
Buffalo Weaver Bubalornis niger on
20 I une, a Blue-capped Cordon-
bleu Uraeginthus cyanocephalus on
13 September (first record) and a
Somali Bunting Emberiza poliopleura
on 14 August (second record).
Two or three pairs of Blue-capped
Cordon-bleus were found atop the
Limuru-Mai Mahiu escarpment,
at 2,200 m; perhaps the birds were
driven there by the drought, as it is
very unusual for this species to occur
at this altitude (per CJ).
Liberia
In Sapo National Park, White-
breasted Guineafowl Agelastes
meleagrides appeared in a remarkably
high proportion of photographs
taken by camera-traps in 2009; this
Upper Guinea forest endemic is
considered rare at the site ( BQ .
Madeira
Records from late April-November
2009 include the following. During
an expedition on 20-29 April, 13
Zino’s Petrels Pterodroma madeira
were observed at sea off Madeira, of
which four were photographed; full
details concerning their identification
will be published in due course.
Daily maximum counts of seabirds
off Porto Moniz during the first week
of September included 3,482 Cory’s
Shearwaters Calonectris diomedea
borealis on 1 September, 5,072 Great
Shearwaters Puffin us gravis on 2nd
and 862 Manx Shearwaters P.
puffinus on 6th. A Wilson’s Storm
Petrel Oceanites oceanicus was seen
off Deserta Grande on 27 August.
A Red-billed Tropicbird Phaethon
aethereus was observed south of
Funchal on 3 and 7 August. The
first Brown Booby Sula leucogaster
for Madeira involved an immature
photographed between Funchal and
Bugio on 1 September.
Single Squacco Herons Ardeola
ralloides were at Porto da Cruz on
7 July and Machico on 18 July,
whilst juvenile Purple Herons Ardea
purpurea were noted at Ribeiro
Salgado on 6 October and on Porto
Santo on 7 October. Three Eurasian
Spoonbills Platalea leucorodia were
seen at Tanque on 4 October. A
female-type Wood Duck Aix sponsa
1 20 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
remained at Ribeira de Janela from
27 October until late November
at least, whilst three American
Wigeons Anas americana stayed
at Lugar de Baixo throughout
November. The long-staying first
Green-winged Teal A. ( crecca )
carolinensis for the island was still at
Ribeira da Janela in November, and
the second at Lugar de Baxio was
still there in July. A Ring-necked
Duck Aythya collaris was observed at
Tanque on 4 October.
On 20 July, a Long-legged
Buzzard Buteo rufinus was at Ponta
do Pargo. A pale-morph Eleonora’s
Falcon Falco eleonorae photographed
at Ribeira de Janela on 14 and 16
August was the fourth for Madeira.
A Peregrine Falcon F. peregrinus
was at Ponta do Pargo on 10-13
October. The third Barbary Falcon
F. peregrinoides for the island was
photographed on Porto Santo on
31 August; probably the same bird
was seen there again on 5 October.
A Hudsonian Whimbrel Numenius
phaeopus hudsonicus that remained
at Porto Moniz from 7 July to 28
August at least is reportedly the
second for Madeira. Three adult
Long-tailed Skuas Stercorarius
longicaudus flew past Porto Moniz on
24 August and three Alpine Swifts
Tachymarptis melba were observed
at Machico on 7 July (per Birding
World 22: 204-218, 279, 329,
416, 435; Dutch Birding 31: 253,
311-317, 370).
Mauritania
In 2009, a juvenile Saker Falcon
Falco cherrug , satellite-tracked from
Hungary to Spain and Portugal,
migrated south along Morocco’s
coast (see below) and arrived at Banc
d’Arguin in October (see www.
sakerlife.mme.hu/en/gmap; per
Dutch Birding 31: 373); there are few
records of the species in the country.
Morocco
Records from the period April —
November 2009 are as follows. A
Western Reef Egret Egretta gularis
found at Essaouira on 18 April
was still present on 13 November.
In 2009, White-headed Ducks
Oxyura leucocephala succesfully raised
young at Sidi Bou-Rhaba, Kenitra,
where at least seven were counted
on 4 October; this accidental visitor
was a resident until at least the
early part of the 20th century, but
occasional breeding was considered
likely following the recent increase
in numbers in Spain. A satellite-
tracked Saker Falcon Falco cherrug ,
a juvenile from Hungary, flew via
Spain and Portugal to Morocco;
Thevenot et al. (2003. The Birds of
Morocco) mention just two certain
previous records, one collected in
the late 19th century and another
captured in May 1963. Two
adult Grey-hooded Gulls Larus
cirrocephalus were photographed
at Oued Souss, Agadir, on 19-21
May. In July, Cricket Warblers
Spiloptila clamans continued to be
seen between Dakhla and Awserd. A
Red-breasted Flycatcher Ficedula
parva was reported from Goulimime
on 1 1 November (per Dutch Birding
31 : 317, 370-383; Birding World
22: 279).
Mozambique
In little-known Quirimbas National
Park, Capo Delgado province,
northern Mozambique, some unusual
records were made in 2008-09 which
were either ‘firsts’ for Mozambique
or for the park. A Western Banded
Snake Eagle Circaetus cinerascens
was claimed from Taratibo on 24
October 2008, with two along the
main road near the park headquarters
at Biaque. There were also two
Southern Banded Snake Eagles
C. fasciolatus at Mareja and one
along the road to Guludo. These
two species are usually considered
allopatric but apparently occur
together in the park; the former
would be new for the Mozambique
list. On Matemo Island, a Eurasian
Oystercatcher Haematopus ostralegus
was seen on 24 October 2008. A
Northern Carmine Bee-eater Merops
nubicus was photographed on Situ
Island in February 2008, five were
seen at Tandanhangue in March
2008, and more were photographed
on 14 January 2009 (Fig. 1 1); these
are the first records for Mozambique
and apparently the southernmost
for the species. A pair of Ulunguru
Violet-backed Sunbirds Anthreptes
neglectus was observed at Taratibo
on 25 October 2008. Gorgeous
Bushshrikes Malaconotus quadricolor
(■■ =Telophorus viridis) are quite
common at Nemau and on Ibo
Island, although not mapped for this
area on distribution maps.
Other noteworthy records from
the north-east include two European
Honey Buzzards Pernis apivorus at
Lake Kagevero, one at Bilibiza on 30
May 2008 and one at Tandanhangue
on 15 April 2009, a Horus Swift
Apus horus at Pemba on 9 April
2009, two Mascarene Martins
Phedina borbonica at Marerja on
2 June 2008, and a Northern
Wheatear Oenanthe oenanthe south
of Pemba on 16 October 2009 (very
few previous records for the country,
all from the south; cf. Roberts’ Birds
of Southern Africa 2005: 949-950).
About 1 00 African Paradise
Flycatchers Terpsiphone viridis
congregated at Pemba on 9 April
2009 (MW).
More southern records, for
the period September-December
2009, include the following. Single
Eurasian Honey Buzzards were
reported from the Panda area in early
November and near Inhamitanga
in December. A Western Marsh
Harrier Circus aeruginosas was
recorded at Gorongosa National
Park in September. At Inhambane,
Crab Plovers Dromas ardeola were
seen again in September and early
November. The Panda area also
produced a Common Redshank
Tringa totanus in early November.
A ‘Lesser’ Cuckoo Cuculus sp.
was reported near Chinuzua in
December; unfortunately, the bird
was not calling nor did it respond to
any playback, and the photographs
will not enable positive identification:
Asian Lesser Cuckoo C. poliocephalus
and Madagascar Cuckoo C. rochii are
indeed extremely difficult to separate
reliably (per TH).
Namibia
Records from July-December 2009
include the following. A trip aboard
a bottom trawler off the coast of the
north of the country (more or less
at the latitude of Etosha National
Recent Reports
Bull ABC Vol 1 7 No 1 (2010) -121
Figure 9. Eurasian Sparrowhawk / Epervier d’Europe Accipiter nisus, Tsavo West
National Park, Kenya, 17 November 2009 (Toby Collett)
Figure 10. Eurasian Thick-knee / CEdicneme criard Burhinus oedicnemus , near
Lukenya, Machakos, Kenya, 15 November 2009 (Phoebe Munyoro)
Figure 11 . Northern Carmine Bee-eaters / Guepiers ecarlates Merops nubicus ,
Situ Island, Quirimbas National Park, Mozambique, 14 January 2009 (Tess
Macdonald)
Park) in July produced three
Wandering Albatrosses Diomedea
exulans and at least four Spectacled
Petrels Procellaria ( aequinoctialis )
conspicillata. A Tristan Albatross
D. ( exulans ) dabbenena was seen
offshore on 3 August; the bird was
ringed and appeared to be from the
colony on Gough Island. Another
individual was photographed just
beyond the 200 nautical mile limit in
August. These waters also produced
a Sooty Albatross Phoebetria
fusca and a Blue Petrel Halobaena
caerulea, the latter probably one of
the northernmost records of this
species (per TH). A Madeiran Storm
Petrel Oceanodroma castro was
photographed on Halifax Island just
off Luderitz in mid October (JK &
JPR per TH).
In early November, a Grey
Kestrel Falco ardosiaceus was
observed c.50 km west of Katima
Mulilo, in the easternmost Caprivi
Strip; this species is normally
restricted to north-western Namibia.
A Eurasian Oystercatcher
Haematopus ostralegus stayed in
Walvis Bay from late September
to December at least. Up to three
Common Redshanks Tringa totanus
were present at Mile 4 Salt Works
north of Swakopmund throughout
the period, with one also at Walvis
Bay from late October. Three Terek
Sandpipers Xenus cinereus were at
Walvis Bay on 11-12 July; this is
generally a scarce species here and
decidedly rare in winter. Walvis Bay
also held Red-necked Phalaropes
Phalaropus lobatus on 11-12 July
(ten) and again from late September
to December, with up to 31 on 12
November and still up to 15 in mid
December (one still in breeding
plumage). Also there was a Common
Black-headed Gull Larus ridibundus
(initially in full breeding plumage)
from 23 September until December
at least.
In the Caprivi, a Ross’s Turaco
Musophdga rossae was seen on Ntwala
Island, near Impalila Island, in
mid October; if photographs can
be obtained, this would constitute
the first substantiated record of the
species in southern Africa. A Great
Spotted Cuckoo Clamator glandarius
was observed east of Luderitz in July;
not only is this further south than
its normal range, but the time of
year is also odd. On 22 November,
a Woodland Kingfisher Halcyon
senegalensis was located at Monte
Christo Guest Farm, c.30 km north
of Windhoek; this is more than 400
km south of this species’ regular
range in the country.
A Grey Wagtail Motacilla
cinerea was reported at Popa Falls in
October (apparently the sixth record
for Namibia) and on Friedental farm,
c.80 km south-west of Windhoek, in
early December (per TH). Shelley’s
Sunbird Cinnyris shelleyi was seen
again in the north, at Shamvura
Lodge, Kavango, on 23 September
(ID). Of regional interest is a pair
of Village Indigobirds Vidua
chalybeata (of the white-billed race
okavangoensis) at Avis Dam, just
outside Windhoek, on 20 December;
the nearest known resident
population is in the Okavango Delta,
at least 650 km to the north-east, but
it is perhaps not that surprising given
the recent colonisation of Red-billed
Firefinches Lagonosticta senegala, its
primary host, in the Windhoek area
(per TH).
Niger
During a field trip by the Sahara
Conservation Fund Termit project
44 Great White Pelicans Pelecanus
onocrotalus were seen on 16 August
2009 north of Goure, in south-east
Niger ( CN per JB); there are very
1 22 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
few recent records in Niger, all of
singles or very small groups. In
autumn 2009, a satellite-tracked
Red-footed Falcon Falco vespertinus
flew from Romania to its wintering
grounds in Angola via Niger (see
www.kekvercse. mme.hu/ en / gmap) .
Photographs of a juvenile taken near
Termit on 20 February 2004, whilst
one or two other individuals were
observed nearby, subsequently came
to light ( TW ); this was very early
in the year, suggesting that some
may winter in West rather than
southern Africa. A Eurasian Hobby
F. subbuteo from Germany took a
similar route via Niger to Angola and
Zambia in autumn 2008 (see www.
raptor-research.de/); of this species,
too, there are only a handful of
observations in Niger (JB ).
Sao Tome & Principe
A belated record has been received
of an adult Squacco Heron Ardeola
ralloides at an artificial lake next to
Sao Tome airport from 20 November
2007 to 31 January 2008 at least (SA,
MMe)\ the first record for Sao Tome,
from January 2003, was at the same
site {Bull. ABC 11: 77).
Senegal
The following were recorded during
field work in the Khossanto-
Bambaraya-Sabodala area, north of
Kedougou, in the extreme south-
east, in July-August and November
2009. The first Lesser Jacana
Microparr a capensis for the country
was discovered at a reservoir on
29 July; there are very few records
from neighbouring countries west
of the Inner Niger Delta in Mali.
At the same dam, a male Little
Bittern Ixobrychus minutus on 29
July and 1-2 males and one female
on 4 August are the first records
for the south-east. Also there was
an immature Black Stork Ciconia
nigra on 14 November; this species
is rarely observed inland. A Little
Buttonquail Turnix sylvaticus was
flushed from the long grass at the
reservoir’s edge on 4 August; this
species is known from relatively few
records in the country, mainly from
the north. Also new for the south-
east were African Crake Crex egregia
(singles observed at three localities),
Allen’s Gallinule Porphyrio alleni
(three at the reservoir) and Purple
Swamphen P. porphyrio (up to four
at the reservoir), all in July-August.
A foraging Adamawa Turtle Dove
Streptopelia hypopyrrha was observed
at Khossanto on 23 July, whilst
in the dry season, in November,
four singing birds were found at
three other sites; these are new
localities for this inadequately
known species, which has been
recorded in Niokolo-Koba to the
west and in south-west Mali to the
east. In the rainy season, at least
nine singing Dorst’s Cisticolas
Cisticola guinea were recorded; all
were silent in November. Small
numbers of Croaking Cisticolas
C. natalensis were seen throughout;
there are remarkably few records in
Senegambia of this species. A male
Heuglin’s Masked Weaver Ploceus
heuglini in breeding plumage was
with a mixed-species flock on 14
July; this species was not mapped for
the south-east. Two Mali Lirefinches
Lagonosticta virata were found on a
rocky hillside on 20-22 November
(RD).
Seychelles
Reports received by Seychelles Bird
Records Committee (SBRC) from
mid-June to mid-November 2009
include the first record of Herald
Petrel Pterodroma aterrima, one
on Cousin on 10-1 1 June 2009. A
Squacco Heron Ardeola ralloides
at Roche Caiman Bird Sanctuary,
Mahe, on 3 April-26 June was the
fourth report for Seychelles. Single
Indian Pond Herons A. grayii on
Alphonse on 30—31 October, on
Desroches on 1 1 November and on
Denis Island on 10 December 2007
(details received late) were the fifth
to seventh reports for Seychelles. A
remarkable number of Common
Swifts Apus apus were reported
on Desroches, beginning with one
on 18 October, rising to ten the
following day, declining to five on
20 October, with one remaining
until 25 October. Of 16 previous
records, 14 involved solitary birds,
whilst the remaining two involved
two individuals, and no sightings
have been made over such a sustained
period, the majority being present
on one day only. There was also a
Common Swift at Alphonse on 19
October.
Also of interest were a Great
Egret Egretta alba on Paul Island,
St. Joseph Atoll, on 10 November
and another at Beau Vallon, Mahe,
on 15 November (13 previous
accepted records), a Purple Heron
Ardea purpurea on Alphonse on 22
October and one on Desroches on
24 October (37 previous records),
an adult Collared Pratincole
Glareola pratincola on Alphonse on
5 November (nine previous records),
an adult Black-winged Pratincole
G. nordmanni on F regate on 12
June (seven previous records), a
Ruff Philomachus pugnax at Roche
Caiman, Mahe, on 23 September
(27 previous records), a Common
Snipe Gallinago gallinago on Aride
on 12 October and two on Alphonse
on 20 October-6 November (14
previous records), a Common Sand
Martin Riparia riparia on Alphonse
on 20-26 October (18 previous
records), a Common House Martin
Delichon urbicum on Alphonse on
4-5 October (eight previous records),
and an adult male White Wagtail
Motacilla alba on D’Arros on 7
November (27 previous records)
(AS).
South Africa
Records from July-December 2009
include the following. During pelagic
trips south-west of Cape Point, 1-2
Wandering Albatrosses Diomedea
exulans, 1-3 Southern Royal
Albatrosses D. epomophora and
1-2 Northern Royal Albatrosses
D. ( epomophora ) sanfordi were
regularly seen in August-October,
single Grey-headed Albatrosses
Thalassarche chrysostoma in July,
single white-morph Southern Giant
Petrels Macronectes giganteus in July—
September, 1-2 Southern Fulmars
Fulmarus glacialo ides in August-
October, and single Flesh-footed
Shearwaters Pujfinus carneipes in
October. Also observed were an
adult Salvin’s Albatross Thalassarche
(i cauta ) salvini c.30 nautical miles
south-west of Hout Bay on 9 August,
Recent Reports
Bull ABC Vol 1 7 No 1 (2010) -123
a Spectacled Petrel Procellaria
(, aequinoctialis ) conspicillata on 14
July and another in October, a Little
Shearwater Puffinis assimilis a few
miles off Cape Point on 1 August, a
Red Phalarope Phalaropus fidicarius
in September, and a pale-morph
South Polar Skua Cathamcta
maccormicki on 25 July.
The most interesting species seen
within Western Cape waters during a
36-day fishing trip which returned to
Cape Town on 8 September included
Wandering, Northern Royal
and Southern Royal Albatrosses
(almost daily), 20 Grey-headed
Albatrosses, c. 1 0 Sooty Albatrosses
Phoebetria fiisca, four Light-mantled
Albatrosses P. palpebrata, 20 Blue
Petrels Halobaena caerulea, c. 50
Grey Petrels Procellaria cinerea , a
few Little Shearwaters (races tunneyi
and elegans), a few probable Salvin’s
Prions Pachyptila salvini, several
Slender-billed Prions P. belcheri
and, best of all, at least one Fairy
Prion P. turtur. A two-week trip
in September 60-90 nautical miles
south-west of Cape Point produced
at least 35 Wandering Albatrosses,
12 Northern and six Southern
Royal Albatrosses, a Grey-headed
Albatross, two Grey Petrels, a Blue
Petrel and a White-headed Petrel
Pterodroma lessonii.
A juvenile Northern Rockhopper
Penguin Eudyptes chrysocome moseleyi
came ashore at Struisbaai in early
August; the bird was weak and
wounded, and was taken into care.
Two tropicbirds seen briefly at St.
Francis Bay, Eastern Cape, on 25
December, were suspected to be
Red-tailed Tropicbirds Phaethon
rubricauda. An Australian Gannet
Morus senator was on Malgas
Island, Western Cape, on 24 August
and from mid November until
mid December at least. A Cape
Cormorant Phalacrocorax capensis
influx into coastal KwaZulu-Natal
continued with an unprecedented
count of 14 birds in Durban Bay
on 6 August. In Eastern Cape, a
Crowned Cormorant P. coronatus
was on Bird Island in Algoa Bay in
early August; this is at least 350 km
further east than usual. An immature
Greater Frigatebird Fregata minor
soared over the Illovo River near
Durban, KwaZulu-Natal, on 21
December and, probably the same
bird, over the Umgeni River mouth
the next day.
In Northern Cape, four Black
Herons Egretta ardesiaca were
reported at Twee Rivieren in
Kgalagadi Transfrontier Park
in July. An influx of African
Openbills Anastomus lamelligerus
occurred throughout the country in
November-December; most records
involved singles, but a group ol over
20 was seen in Potchefstroom, North
West. Sightings within the species’
normal range suggest a marked
increase, with reports of a flock of
200-300 at St. Lucia and over 1,000
near Skukuza, Kruger National Park
(=NP). Records of regional interest
include a Black Stork Ciconia
nigra at Grootvadersbosch Farm,
Western Cape, in late August and
single Marabou Storks Leptoptilos
crumeniferus in Durban, KwaZulu-
Natal, on 12 August, and near
Kimberley, Northern Cape, on 12
December. A pair of African Pygmy
Geese Nettapus auritus was east of
Letaba, Kruger NP, on 1 1 October.
In Mpumalanga, a male Tufted
Duck Aythya fuligula was found at
Dullstroom Nature Reserve on 1 1
November.
Eurasian Honey Buzzards Pernis
apivorus were reported from Phinda
Game Reserve, KwaZulu-Natal,
on 8 November; Irene, Gauteng,
in mid November; Swadini Resort,
Limpopo, on 29 November;
Newlands, Western Cape, on 2
December; Witwatersberg Mountain
Range; Gauteng, on 1 0 December;
Mokala NP, Northern Cape, on
13 December; and Mkhuze Game
Reserve, KwaZulu-Natal, on
16 December. Single Palm-nut
Vultures Gypohierax angolensis
were seen along the Mphongolo
Loop, Kruger NP, on 27 August,
and near Plettenberg Bay, Western
Cape, on 13 December, where,
according to a local farmer, the
bird has been present for at least
two years. In Western Cape, an
adult Black-chested Snake Eagle
Circaetus pectoralis was located south
of the Vredenberg-Paternoster
road on 5 July and a Brown Snake
Eagle C. cinereus at Vergelegen
on 19 November. An African
Harrier Hawk Polyboroides typus at
Kimberley, Northern Cape, in July
is of regional interest. Single Pallid
Harriers Circus macrourus were seen
west of Kimberley in early October,
and west of Alexandria, Eastern
Cape, on 1 1 December. Western
Marsh Harriers C. aeruginosas were
reported from Phinda Game Reserve,
KwaZulu-Natal, in early October,
and Marievale Bird Sanctuary,
Gauteng, on 22 November and 19
December, with a further two records
from Vogelfontein on the same day
and the Kgomo-Kgomo floodplain
on 20 December. A female Amur
Falcon Falco amurensis was near
Plettenberg Bay, Western Cape, on
13 December.
An unseasonal Lesser Moorhen
Gallinula angulata was near Ellisras,
Limpopo, in late July; one at Stanger,
KwaZulu-Natal, on 30 August is a
rather early record. A female African
Finfoot Podica senegalensis was at
Northern Farm, Gauteng, on 6 July;
a sighting of this species at what is
effectively a sewage works is rather
unusual. In Western Cape, a Kori
Bustard Ardeotis kori was reported
at Cape Agulhas from 9 September,
whilst a pair was found in Bontebok
NP in November. In KwaZulu-
Natal, a Red-crested Bustard
Lophotis ruficrista was in Nambiti
Game Reserve, near Ladysmith, in
November.
A Crab Plover Dromas ardeola
was at Richards Bay, KwaZulu-Natal,
from 2 October until 1 1 October
at least. A Eurasian Oystercatcher
Haematopus ostralegus occurred
in the Sundays River mouth area,
Eastern Cape, in November. Of
regional interest are African Black
Oystercatcher H. moquini records
from KwaZulu-Natal, in Durban
on 8-9 August (one), Mpenjati
estuary on 22 August (one) and
Isipingo on 23 August (two). In
the same province, a Pied Avocet
Recurvirostra avosetta was at the
Umzumbe River estuary on 17-19
October. In Kruger NP, a pair of
Three-handed Coursers Rhinoptilus
cinctus was found breeding near
124 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
Pafuri in August; there are few
breeding records in South Africa. A
Three-handed Courser was present
near Ngala Lodge, Limpopo,
in mid December. A Collared
Pratincole Glareola pratincola at
Mkhombo Dam, Mpumalanga, on
13 December, was several hundred
kilometres west of the species’ normal
distribution.
In West Coast NP, Western
Cape, up to five Lesser Sand Plovers
Chamdrius mongolus were present
in August; at least one stayed until
late November. Also there in August
were three Greater Sand Plovers
C. leschenaultii, with another three
at Swartvlei, on the Garden Route,
Western Cape, on 27 October.
Caspian Plovers C. asiaticus were
located in the Viljoenskroon area,
Free State, on 13 September (one)
and east of Nigel, Gauteng, on
14—29 November (up to nine).
In Western Cape, a Common
Redshank Tringa totanus found
at Velddrif on 12 August was still
present on 24 September. Single
Green Sandpipers T. ochropus
were recorded in Kruger NP in
late September-mid October,
on 7 and 19 November, and 9
December; others were seen in
Ndumo Game Reserve, KwaZulu-
Natal, on 21 November, and at
Ngala, Limpopo, on 18 December.
A Terek Sandpiper Xenus cinereus
was at Rondevlei, near Wildernis,
Western Cape, on 18 October. In the
same province, a Ruddy Turnstone
Arenaria interpres at Beaufort West
sewage works on 1 1 October was a
rather interesting find. A Red-necked
Phalarope Phalaropus lobatus was at
Soutvlei, Eastern Cape, on 13-19
November, and a Red Phalarope
at Haarlem, in the Langkloof area,
Western Cape, on 13 November.
An adult Common Black-
headed Gull Larus ridibundus in
full breeding plumage was observed
in West Coast NP, Western Cape,
on 12 November and, probably the
same bird, at Velddrif on 27-29
November. A Lesser Black-backed
Gull L. fuscus was reported from a
small wetland north-east of Kriel,
Mpumalanga, on 31 July, whilst
another, which was relocated at
Orient Beach in East London,
Eastern Cape, on 20 August after a
nearly two-month absence, remained
until early September at least. A
group of 15-20 Roseate Terns
Sterna dougallii was reported in a
tern roost near Gansbaai, Western
Cape, on 8-9 August. In the Eastern
Cape, at least one Antarctic Tern
S. vittata was still present in a tern
roost near Gonubie Point, East
London, on 14 August. The Bridled
Tern S. anaethetus at Cape Recife in
Port Elizabeth, Eastern Cape, was
relocated on 7 July and still present
a week later. A Sooty Tern S. fuscata
first reported from Bird Island, Algoa
Bay, Eastern Cape, in early June
was still present on 4 August; on 3
November one was on Dyer Island
near Gansbaai, Western Cape.
A Barred Long-tailed Cuckoo
Cercococcyx montanus was reported
from Ndumo Game Reserve,
KwaZulu-Natal, on 21 November.
In Northern Cape, up to four Little
Bee-eaters Merops pusillus were in
Rooipoort Nature Reserve, near
Kimberley, in July. In Mpumalanga,
an out-of-range Swallow-tailed
Bee-eater M. hirundineus was
discovered in the Beerlaagte area,
north of Villiers, on 12 September;
another was in Western Cape,
where the species is rarely recorded,
near Wildernis on 29 September.
Two White-fronted Bee-eaters M.
bullockoides in Augrabies Falls NP,
Northern Cape, on 30 June, were
probably the same two found there
on 22 March; another out-of-range
pair was reported near Aliwal North,
Eastern Cape, in August. Crested
Barbets Trachyphonus vaillantii were
still in Augrabies in late October — a
considerable westward range
extension.
An African Pitta Pitta angolensis
in Durban, KwaZulu-Natal, on 13
October, is a remarkable record. In
North West, a Mountain Wagtail
Motacilla clara was in Tonqani
Gorge, east of Rustenburg, on
26 October. Southern Africa’s
tenth Golden Pipit Tmetothylacus
tenellus was at Futululu Park, near
St. Lucia, KwaZulu-Natal, on 12
August, and the 1 1th was at Mkuze
Game Reserve, also in KwaZulu-
Natal, on 3-4 October. In early
August, a Long-tailed Pipit Anthus
longicaudatus was observed west
of Christiana, North West, with
another at Garingboom, Free State.
On 23 October, a male Blackcap
Sylvia atricapilla was claimed from
the Pafuri picnic site, Kruger NP.
A Sedge Warbler Acrocephalus
schoenobaenus and a moulting male
Long-tailed Paradise Wliydah
Vidua paradisaea at Nossob,
Kgalagadi Transfrontier Park,
Northern Cape, in mid December,
were well out of range. A Spotted
Flycatcher Muscicapa striata in
West Coast NP, Western Cape, on
16 December, is probably the same
individual that has returned to this
site for several successive seasons.
The immature Bush Blackcap
Lioptilus nigricapillus first found in
a Heidelberg garden, south-east of
Johannesburg, Gauteng, in June was
still present in mid July. A Malachite
Sunbird Nectarinia famosa at
Kimberley, Northern Cape, in July,
is of regional interest.
In Western Cape, a juvenile Red-
backed Shrike Lanius collurio was
in West Coast NP on 22 November
and an adult near Beaufort West
on 20 December. A yellow-morph
Crimson-breasted Shrike Laniarius
atrococcineus has been regularly
seen at Klipfontein Lodge, c.45
km from Klerksdorp, North West;
this unusual form is normally quite
difficult to find. A Fork-tailed
Drongo Dicrurus adsimilis in Darling
in October probably represents the
first record on the west coast north
of Cape Town. In Mpumalanga,
an out-of-range a pair of Yellow
Weavers Ploceus subaureus was found
near Tonga on 20 August; this is
the first record in the province since
the mid-1970s. Red-headed Finch
Amadina erythrocephala, recorded
for the first time in Kruger NP
in 2009, was still present in large
numbers north of Satara in October.
In Western Cape, a male Village
Indigobird Vidua chalybeata was
coming to a garden in Melkbos
in late November-December. An
eruption ol Lark-like Buntings
Emberiza impetuani occurred on the
west coast in October-November,
Recent Reports
Bull ABC Vol 1 7 No 1 (2010) -125
Figure 12. Beaudouin’s Snake Eagle / Circaete de Beaudouin Circaetus beaudouini,
Kazinga Channel, Uganda, 26 July 2009 (Bernard Hanus)
Figure 13. Cape Shoveler / Canard de Smith Anas smith'd, Chisamba IBA,
Zambia, 15 July 2009 (Manfred Wichmann)
Figure 14. Spur-winged Lapwing / Vanneau a eperons Vanellus spinosus , Lion
Camp, South Luangwa National Park, Zambia, 17 August 2009 (P. Bentley)
with maximum numbers of over
1 ,000 being recorded in West Coast
NP on 21-22 November; two on
Robben Island on 5 November was a
rather southerly record and only the
second for the site (per TH).
Uganda
Records in July-October
2009 include the following. A
Beaudouin’s Snake Eagle Circaetus
beaudouini was photographed at the
Kazinga Channel on 26 July (Fig.
12; HD). On 23 October, in the
south, a juvenile male Pallid Harrier
Circus macrourus and a Crested
Barbet Trachyphonus vaillantii were
seen at Mityebili, south of Kyotera,
and a White Wagtail Motacilla alba
in the Sango Bay area. Three Red-
knobbed Coots Fidica cristata were
observed on Lake Victoria during
a boat trip to the Sesse Islands, on
1 1 October, whilst on 31 October,
Common Teal Anas crecca, Dunlin
Calidris alpina and Caspian Tern
Sterna caspia were noted en route
to the lagoon at Lutembe {RS). The
report of a pair of Bronze-winged
Coursers Rhinoptilus chalcopterus in
Lake Mburo National Park in July
2008 (see Bull. ABC 16: 111) has
prompted an earlier record of a pair
at the same locality on 19 September
2000 to be submitted (AW).
A Semi-collared Flycatcher
Ficedula semitorquata was at
Makerere University on 15 October
(RS). Three Yellow Penduline Tits
Anthoscopus parvulus were seen just
south of the Nile River in Murchison
Falls National Park in July 2009
(KV); there have been other (as
yet unpublished) reports from the
area recently (per NB) and also one
from the north-west of the country
(GP per NB). At Kajansi, south of
Kampala, four Brown Twinspots
Clytospiza monteiri were seen on
24 September and a pair of White-
collared Olivebacks Nesocharis
ansorgei next day (RS).
Zambia
In 2009 the following were reported.
Cattle Egrets Bubulcus ibis were
found breeding at Siansowa
Crocodile Farm, 40 km west of
Sinazongwe, on 21 November; this
is the first confirmed breeding record
for Zambia (55). A roost of c. 1 00
Slaty Egrets Egretta vinaceigula was
found in reeds on the Lingongole
River, Simungoma Important
Bird Area (=IBA), on 1 1 August
(LR). A pair of Cape Shovelers
Anas smithii at Chisamba IBA, on
12-16 July (Fig. 13; MW, K0) is
the seventh record for the country.
A Spur- winged Lapwing Vanellus
spinosus was at Lion Camp, South
126 -Bull ABC Vol 17 No 1 (2010)
Recent Reports
Luangwa National Park, on 17-22
August (Fig. 14; PB)\ this is the
most southerly record in Zambia of
this rapidly spreading species. About
12 Black Saw-wings Psalidoprocne
pristoptera of the eastern race
orientalis at Katombora Rapids, near
Livingstone, on 28 July constitute
the most westerly Zambian record
by c.250 km ( BS ). A Red-rumped
Swallow Cecropsis daurica of the
Palearctic race rufula was mist-netted
near Kabwe on 27 January ( BvdB );
this is the southernmost confirmed
record in Africa of this race.
Records were collated by Ron Demey
from contributions supplied by
Stajfan Andersson ( SA ), Clive Barlow
(CBa), P. Bentley (PB), Nik Borrow
(NB), Nicky Bousfield (NBo), Chris
Brewster ( CB), Brian Bridges (BB),
Doline Bridges (DB), Bennie van den
Brink (BvdB), Joost Brouwer (JB),
Grant Buckmaster ( GB), Siobhan
Buckmaster (SB), Artur Bujanowicz
(AB), Ben Collen (BC), Mohamed
Balia Conde (MBC), John Cooper
(JC), John Dalziel (JD), Peter
DArcy (PDA), Ian Davidson (ID),
Ron Demey (RD), Klaas-Douwe
Dijkstra (KD), Hugues Dufourny
(HD), Maria Eifler (ME), Ali Flatt
(AE), B. Gerenamotse (BG), Daphne
Goldsworthy (DG), Mike Goldsworthy
(MG), Kevin Grant (KG), John
High (JH), Glynis Humphrey (GH),
Harold Hester (HH), Pete Hancock
(PH), Trevor Hardaker (TH), David
Hoddinott / Rockjumper Birding
Tours (DH), Colin Jackson (CJ),
Aba Jarju (AJ), Jessica Kemper (JK),
Doreen McColaugh (DMc), Martim
Melo (MMe), Johannes Merz (JM),
Sharon Merz (SM), Mark Muller
(MM), Christian Noirard ( CN),
Pat Nurse (PN), Kaj 0stergaard
(K0), Guillaume Passavy (GP),
Bruno Portier (BP), Richard Randall
(RR), Leslie Reynolds (LR), Steve
Rooke (SR), Jean-Paul Roux (JPR),
Kev Roy (KR), Paul Seligman (PS),
Matt Selwinsky (MSe), Roger Skeen
(l IS), Adrian Skerrett (AS), Mike
Soroczynski (MS), Kadiatou Soumah
(KS), Bob Stjernstedt (BS), Wande
Touray ( WI ), Steph Tyler (ST), Keith
Valentine / Rockjumper Birding Tours
(KV), Cheryl Vroom (CV), Jaap van
der Waarde (JvdW), Tim Wacher
(TW), Ian Walker (IW), Manfred
Wichmann (MW), Malcolm Wilson
(MW), and from Africa — Birds &
Birding, Birding World, Dutch
Birding, Sandgrouse, capebirdnet,
SARa reBi rdA lert, www. zestfo rbi rds.
co.za and sa-rarebirdnews@
googlegroups. com.
Contributions for Recent Reports can
be sent to Ron Demey, Tenierslaan
24, B-3500 Hasselt, Belgium and
(preferably) by e-mail: rondemeyl @
gmail.com or recent _reports@
africanbirdclub. org
Recent Reports
Bull ABC Vol 17 No 1 (2010) -127
Reviews
Birds of Ethiopia and Eritrea:
An Atlas of Distribution
John Ash & John Atkins, 2009. London,
UK: Christopher Helm. 464 pp, numerous
photographs (16 pp in colour) and more
than 872 maps. Hardback. ISBN: 978-1-
4081-0979-3. UKE45.00.
For the scholar and discerning
traveller alike, a good distributional
atlas to the avifauna of a region
is an invaluable key to unlocking
its ornithological gems. The two
countries, Ethiopia and Eritrea,
covered by this well-produced book
are most certainly an avian treasure
house, with a grand total of 872
species having been recorded from
within their boundaries. More than
30 of these are endemic to the
region and most of these specialities
are mouth-wateringly depicted in a
photo gallery section.
These ancient lands are
undeniably fascinating, possessing as
they do a rich and colourful history,
and superb natural scenery, albeit
greatly modified by the effects of
mankind. The lengthy Blue Nile
commences its journey in Ethiopia
flowing out from the enormous high
inland Lake Tana that provides a
livelihood for fishermen using their
traditional papyrus boats before it
tips its waters over the dramatic
Tissisat Falls. The extensive highland
plateau dissected by the Great
Rift Valley covers an area that lies
predominantly over 2,000 m and
ultimately peaks at 4,620 m on Ras
Deshen in the Simien Mountains.
These lofty lands have acted as a
natural fortress, both protecting
and isolating, over the centuries. In
contrast, at the base of these sheer,
vertical cliffs stretch the lands that
lead to the Danakil Desert, a desolate
but equally mystifying place that
reaches 110 m below sea level and is
occupied by the fearsome Afar tribe.
Although Ethiopia is landlocked,
there are numerous rocky islands
along the Eritrean coastline holding
important seabird colonies. This is
certainly a land of contrasts!
John Ash and John Atkins are
indisputably both highly qualified
to prepare this book for between
them they have lived and worked
in Ethiopia for a total of 1 3 years.
Over the course of the past four
decades, they have summarised their
own records and included a huge
number of sightings submitted by
many of the other long- and short-
term visitors to these countries.
Impressively, they have also
assimilated a mass of historical
records (all well referenced in the
concise bibliography).
This largish book (246 x 189
mm) is somewhat deeper than the
norm but snuggles up perfectly on
the bookshelf alongside John Ash
and John Miskell’s previous atlas and
authoritative sister volume Birds of
Somalia. This new book, however, is
a much more refined and somewhat
thicker volume containing 463
pages, the first 80 of which provide
an excellent insight to Ethiopia and
Eritrea’s ornithology. An initial
general introduction proffers a
thumbnail sketch of culture and
politics, and this is followed by well-
researched, readable and informative
essays covering such subjects as the
history of bird-finding, topography,
hydrography, geology, vegetation,
climate, habitats, conservation and
breeding habits, all generously
illustrated with photographs and
tables. A suite of coloured maps
provides information on political
boundaries, topography, geology,
rainfall and notable localities
including national parks and wildlife
refuges. The physical situation of
these two countries and the dramatic
nature of the terrain have an obvious
effect on migrants moving in and
out of Africa, making the chapter
on migration especially interesting.
B I R D S O F
ETHIOPIA &
ERITREA
It looks into where these birds are
coming from and outlines the status
of each species within the region, as
well as giving information on their
arrival and departure dates, all of
which will be immensely useful to
the visitor.
The bulk of the book comprises
the atlas and species accounts.
Sequence and nomenclature
generally follow The Howard &
Moore Complete Checklist of the
Birds of the World (Dickinson
2003) although some English
names have been changed to fall
into line with the choices made in
the recently published and essential
companion field guide Birds of the
Horn of Africa (Redman et al. 2009).
Therefore, there are no great surprises
taxonomically and the book is as up
to date as possible, and rightly no
longer treats ‘Degodi’ Lark Mirafra
degodiensis as a species but as a form
of Gillett’s Lark M. gilletti.
Three species are laid out
per page, the text for each being
accompanied by a large-scale,
monochrome ochre-coloured map
indicating basic topographical
contours and major rivers. On a grid
of half-degree squares, each species’
presence is clearly recorded by the
presence of black (breeding) or white
(sight) circles with other symbols
being used for uncertain sightings or
unconfirmed breeding records. The
layout is exceedingly pleasing to the
eye and the superimposed data are
128 - Bull ABC Vol 17 No 1 (2010)
Reviews
clear and very easy to read against the
background map, which although
strongly coloured is not obtrusive.
The written account confirms
the species’ presence in either one or
both of the countries and endemic
species are highlighted. Sadly, a more
global indication of a species’ range
and distribution is not included.
However, all subspecies known to
occur in the area are taken into
account and where there is more
than one race represented then the
known boundaries between the
forms are outlined in black on the
map. With migrants such as Yellow
Wagtail Motacilla flava, where
multiple races overlap and ranges
cannot be so defined then the known
status in either country is stated.
Information on breeding is briefly
summarised and succinctly covers
laying dates and clutch size. There
is a wealth of information given in a
relatively small space and, from each
account, there is enough to inform
the reader in which habitat to find
the species, what altitude it prefers,
habits where relevant, migratory
movements and often exact localities
to look for the birds. Appendices
cover hybridisation, potential and
rejected species lists, Important Bird
Areas, ringing and a very thorough
gazetteer.
This excellent atlas summarises
a wealth of field experience from
real authorities and all that is
known to date from the literature
about the distribution of birds in
these two exciting countries. Both
clear and precise, it sets a new high
standard in works of this kind and
definitely forms a benchmark. It is
a fitting monument to John Ash’s
long-standing work and discoveries
in the region, and is thus an
absolutely essential reference for
anyone interested in the countries.
For many years now Ethiopia has
been an increasingly popular tourist
destination for those interested in
its wildlife and culture. I would
recommend this atlas to any potential
visitor, as it will provide the perfect
overview to the distribution of a rich
avifauna and a superb aid as to where
to find the special birds.
Nik Borrow
References
Ash, J. S. & Miskell, J. 1998. Birds of
Somalia. Robertsbridge: Pica Press.
Dickinson, E. C. (ed.) 2003. The
Howard and Moore Complete
Checklist of the Birds of the
World. Third edn. London, UK:
Christopher Helm.
Redman, N., Stevenson, T. &
Fanshawe, J. 2009. Birds of the
Horn of Africa. London, UK:
Christopher Helm.
Living on the Edge: Wetlands
and Birds in a Changing Sahel
Leo Zwarts, Rob G. Bijlsma, Jan van der
Kamp & Eddy Wymenga, 2009. Zeist:
KNNV Publishing. 564 pp, numerous photo-
graphs, drawings, figures, tables and maps.
Hardback. ISBN 978-90-5011-280-2. €64.95
(www.knnvpublishing.nl) or UK£87 (NHBS).
This hefty and beautifully produced
volume truly is a superb book. It
mainly focuses on the ecology of
Palearctic birds in the Sahel and
offers a fascinating synthesis of
numerous studies and the authors’
own field work, conducted between
1982 and early 2009. Their field
work began as low-budget affairs,
partly financed by the participants
themselves, but have since
developed into larger-scale projects
encompassing several West African
countries. The authors’ statement
that ‘Paid, underpaid or unpaid, the
passion remained the same’ shines
through on every page.
Each year, hundreds of millions of
birds breeding in Europe undertake
the daunting journey south to sub-
Saharan Africa, where they spend the
greater part of their lives, mainly in
the c.500 km-wide band of northern
savannahs stretching 3,500 km from
west to east. Although this habitat
can appear superficially poor and
dry, especially during the Palearctic
migrants’ stay, it is actually a
complex ecosystem, where seasonal
variations in the leafing, flowering
and fruiting of trees and shrubs
provide food and shelter for birds
throughout the northern winter, i.e.
the region’s dry season. Survival here
depends mainly on unpredictable
rainfall in the short wet season and
the flood extent of the inundated
areas. Droughts, whose frequency
and duration have increased since
1969, have a huge adverse impact on
birds, which has been magnified by
negative habitat changes associated
with human population growth,
such as deforestation, reclamation of
wetlands and irrigation. Additionally,
overgrazing and hunting take their
toll. It should therefore not come as a
surprise that population numbers of
75 out of 127 trans-Saharan migrants
are decreasing, with those wintering
in the Sahel suffering the strongest
declines.
The book, which pays tribute to
the ideas aired by Reg Moreau — the
‘forefather of African ecology’ — in
The Palaearctic-African Bird
Migration Systems (1972), documents
and analyses the multiple problems
faced by trans-Saharan migrants. It
does so extremely thoroughly and
in a highly readable and attractive
form, despite the huge amount
of information presented and the
often-sad message. The whole is
lavishly illustrated in full colour
throughout, with hundreds of clear
diagrams and maps, 35 tables and
nearly 500 excellent and functional
photographs — even the index has
delightful bird drawings, by Jos
Zwarts, at the bottom of every page!
The language occasionally betrays
that the book was written by Dutch
researchers, but the overall quality of
the work is of such a high standard
that to mention it is almost nit-
picking.
First, rainfall, rivers, vegetation
and land use in the Sahel are
presented, followed by chapters
on the major wetlands: the Inner
Niger Delta, the Senegal Delta, the
Hadejia-Nguru floodplains, the Lake
Chad Basin, the Sudd and the rice
fields. Next are 27 chapters devoted
to single bird species, selected to
identify events pivotal to numerical
fluctuations, such as migration
strategies, distribution and habitat
selection in Africa, and changing
conditions on the breeding grounds.
These species range from Grey
Ardea cinerea and Purple Herons
A. purpurea through Black-tailed
Godwit Limosa limosa and Eurasian
Reviews
Bull ABC Vol 1 7 No 1 (2010) -129
Wryneck Jynx
torquilla to Lesser
Sylvia curruca
and Common
Whitethroats S.
I communis. A
chapter, by Wim
3 Mullie, gives
an overview of
recent outbreaks
of locusts and
grasshoppers
and the use
of chemical pesticides for their
control, explains the ecology of
these insects in the region, and
discusses bird-acridid relationships
and the ‘ecological service’ provided
by birds by suppressing acridid
populations. The book concludes
with a discussion of the impact of
ecological changes in the Sahel on
Eurasian bird population trends.
Evidence accumulated over many
years of field work, like that by the
authors, indicates that population
fluctuations of several species are
indeed largely determined by rainfall
and flood extent in the Sahel.
This, coupled with changes in the
breeding areas and stopover sites
along migration routes, leaves little
scope for optimism.
Nevertheless, Leo Zwarts
and his co-workers hope,
‘against their own better
judgement’, that their
negative predictions will
prove incorrect and that
Afro-Palearctic birds
will be sufficiently
resilient to cope with
the changes.
New data constantly
lead to new lines of
research, whilst a lot of questions
remain unresolved. Fortunately,
for what is known on Palearctic
birds in the Sahel we now have an
excellent synthesis which constitutes
a milestone for ecological studies in
the region. This outstanding book
is a splendid achievement for which
the authors and publisher are to be
congratulated.
Ron Demey
i
An Atlas of Wader Populations
in Africa and Western Eurasia
Simon Delany. Derek Scott, Tim Dodman
& David Stroud (eds.), 2009. Wageningen:
Wetlands International. 521 pp, many colour
photographs and maps. Hardback. ISBN
78-90-5882-047-1. UK£70.
Over ten years in the ‘making’,
this atlas has been well worth the
wait. It collates the vast amount
of information stored in the
Wetlands International databases,
as well as drawing on an extensive
bibliography. Not only does it map
individual species distributions but
also provides population estimates
and identifies key sites according to
various criteria including the 1%
population level, cold weather and
drought refuges, presence of globally
threatened species and whether there
may be a high degree of turnover
of the population during passage
periods. The maps of key sites in
Europe and especially Africa are
fascinating and really highlight the
importance of areas such as the Banc
d’Arguin in Mauritania and the
Senegal and Niger River deltas.
Most people will turn straight
to the species accounts. Ninety
species were considered, ranging
from the probably
extinct Slender-billed
Curlew Numenius
tenuirostris and the
rare endemic St Helena
Plover Charadrius
sanctaehelenae to more
abundant species such
as Northern Lapwing
Vanellus vanellus and
Eurasian Woodcock
Scolopax rusticola. A
summary of the different
races is given along with a map of
key sites and a description of the
routes taken by different populations.
These maps reveal the complexity
of migration undertaken by these
shorebirds. Individuals from the same
Siberian breeding area could end up
on the east or west coast of Africa,
thousands of kilometres from each
other or, conversely, birds in the
same South African wintering area
could breed in parts of the Arctic
many thousand of kilometres apart.
An Atlas of Wader
For many Afrotropical species we
don’t understand the distribution
or population sizes particularly well.
Some African countries are not
covered by any counts leaving huge
gaps in coverage for parts of Central
and North Africa. For many species
such as Egyptian Plover Pluvianus
aegyptius, which tend to be widely
spread in suitable habitats from West
to East Africa, population estimates
tend to be informed guesses. This
species at least congregates around
watercourses where they can be
counted but estimates for birds like
Bronze-winged Courser Rhinoptilus
chalcopterus, which are thinly spread
across a vast area, must be treated
as highly provisional. With such
uncertainty surrounding population
estimates, the determination of any
population trends is impossible and
these are only really possible for
those species that pass through a
small number of key sites that are
monitored, or are picked up during
large-scale European surveys. These
gaps in our knowledge are one of
the main take-home messages from
the atlas and they also provide an
inspiration to go out and fill them!
Despite such limitations, the
distillation of the International
Waterbird Census counts has
identified 876 key sites in 85
countries, which are listed in the
back of the book. These provide
a snapshot of our current best
knowledge and will be especially
useful for policy makers and
conservation bodies alike. The
editors have done a fantastic job
pulling together information from
a huge variety of sources and the
bibliography stretches over 30 pages
and numbers over 1 ,000 references.
The book contains a wealth of
information and is produced to a
very high standard. It is illustrated
throughout with excellent colour
photographs and its design makes it
very easy to read. It will be essential
for anyone working with waders but
also deserves a place on the bookshelf
of anyone with even a passing
interest in shorebirds, their ecology,
distribution and conservation.
Phil Atkinson
130 - Bull ABC Vol 17 No 1 (2010)
Reviews
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Bull ABC Vol 1 7 No 1 (2010) -131
Letters to the Editor
A second record of American
Golden Plover in The Gambia
I have belatedly noticed the paper
describing the first American
Golden Plover Pluvialis dominica
for Mauritania (Schmaljohann
& Thoma, 2005, Bull. ABC 12:
158-161), wherein a table of records
of the species from West Africa is
presented. There is, however, an
additional record missing from
that list. Just one occurrence was
mentioned for The Gambia, in 1984,
but there is a second, a bird that I
found and photographed at Kotu
Sewage Farm, Western Division,
on 1 1 November 1997, which was
also seen by a group of birders,
among them Clive Barlow and Tony
Disley, senior author and artist,
respectively, of A Field Guide to Birds
of The Gambia and Senegal (Barlow
et al. 1997; Robertsbridge: Pica
Press). Because I assumed that Clive
Barlow would publish the details as
appropriate, I never submitted the
record anywhere, but a photograph
of the bird appeared in Birdwatch 67:
42-43 (wrongly credited to me, but
the published image was taken by
Tony Disley).
Dominic Mitchell
Managing Editor, Birdwatch,
Warners Group Publications pic,
The Chocolate Factory,
5 Clarendon Road,
London N22 6XJ, UK
Name changes
Nigel Collar’s letter ( Bull . ABC
16: 245) raises more issues than
he acknowledges. Whilst there
is certainly a case to be made
for changing some names for
conservation purposes, as he suggests,
there are also good reasons not to
change established English names of
birds.
In the present flush of taxonomic
changes due to DNA phylogenetic
research, scientific names are subject
to considerable flux. Genera and
species are split or (more rarely)
combined, and what had been
a fairly stable situation for most
groups over many decades is in
upheaval. On top of this comes
the attempt at a standardised list
of English names promoted by
the International Ornithological
Congress (IOC), enshrined in Gill &
Wright (2006) — -this despite much
apathy or silent opposition from
many ornithologists who declined
to be part of the initiative.The net
result of these two independent but
simultaneous processes is that there is
unprecedented flux in both English
and scientific names of birds, tending
to cause confusion (and irritation)
amongst ordinary birders.
Given that the ‘true’ name of
any taxon is the scientific name,
which is subject to both taxonomic
fashion and phylogenetic research, to
maintain a degree of stability some
herpetologists have proposed that
split genera should be recognised
as full genera, but grouped under
their previous umbrella, in the same
way that subgenera are sometimes
characterised, by using brackets.
Thus Sooty Gull Larus ( Icthyaetus )
hemprichi or White-bellied Black
Tit Parus ( Melaniparus ) albiventris.
So far, given that The Birds of Africa
(and thus the ABC checklist) has
been fairly conservative, much of this
upheaval has escaped the continent
and hence this Bulletin , but Europe
and the Americas are much affected.
Where a familiar species has been
found to comprise two or more
cryptic species one can similarly
bracket the old species name, e.g.
Madagascar Hoopoe Upupa ( epops )
marginata or the expected African
Hoopoe U. (e.) africana.
However, the above is just to
provide background to the issue
of changing English names. A
quick glance at Peter Lack’s latest
changes in the ABC checklist’s
preferred names, incorporating the
IOC ‘international names’, many
against his own grain as he admits,
reveals the scale of mostly arbitrary
alterations that have taken place
within the ABC area — 108 in all. As
I noted in reviewing Gill & Wright
{Ibis 149: 429-431), some of these
names are daft. Calling Foudia
madagascariensis ‘Red Fody’ instead
of Madagascar (Red) Fody is pretty
absurd when most male fodies (five
of the seven extant species) are red,
and when, if it is to be changed at
all, there is the French / Creole name
Cardinal (hence ‘Cardinal Fody’)
in use throughout its range (except
on St. Helena). Why change Pacific
Swift Apus pacificus to Fork-tailed
Swift — it is neither the only swift
in the Pacific area, nor the only
swift in the world with a forked tail;
replacing one inadequate name with
another is no improvement! Others
are simply banal: Pintado Petrel has
long been an attractive alternative
to the traditional mariner’s name
Cape Pigeon for Daption capense ,
but why lose the charm of both with
Cape Petrel? In at least one case
Lack has defied the IOC, though
it’s another banal one — Fairy Tern
Gygis alba becomes White Tern (a
long-standing alternative); the IOC
invented Angel Tern de novo. Some
are still behind the times: Circus
maillardi Madagascar Marsh Harrier
becomes Reunion Harrier, but
maillardi has for some years been
generally split from C. macrosceles ,
so whilst the former is indeed
the Reunion Harrier, the latter is
inevitably again the Madagascar
(Marsh) Harrier. The inappropriate
retention of ‘Marsh’ for these birds
is purely based on their relationship
to Eurasian Marsh Harrier C.
aeruginosas- — they hunt in forests, not
marshes.
132 - Bull ABC Vol 17 No 1 (2010)
Letters to the Editor
The ABC has always accepted
alternative names in the checklist,
and I hope will long continue to do
so. However, they are relegated to
an inferior status in relation to the
'preferred name’, even if, as Lack
refreshingly states, he is ‘well aware
that English names in particular
are major causes of argument and
potentially confusion. Whatever
names are chosen will not be liked by
everyone’.
My suggestion is to retain an
international name, but demote it to
a junior partner of local usage. Hence
the bird called Rose-ringed Parakeet
by the IOC ( Psittacula krameri)
would be cited (pending revision in
progress . . . ) as Long-tailed Parakeet
(Rose-ringed Parakeet) in a paper on
West Africa, Ring-necked Parakeet
(Rose-ringed Parakeet) in a paper on
Mauritius, but simply Rose-ringed
Parakeet in South Africa. Thus even
if the international name changed
(e.g. in the next edition of the IOC
list), the local name would not, and
continuity would be maintained.
In the case of Collar’s
Heteromirafra sidamoensis, itself a
segregate from the former Long-
clawed Lark H. ruddi (the nominate
always Rudd’s Lark in South
Africa), there is no long tradition
of an English name, since the taxon
was only described in 1975. Erard
made a very reasonable attempt to
localise the bird with the scientific
name, and it is hardly his fault
that all the traditional provinces
in Ethiopia (including Sidamo)
were abolished in 1996. However,
that leads onto another important
issue — whether English bird names
should slavishly follow changes in
local political nomenclature. I was
rather struck when reviewing Gill
&C Wright that a regrettably ignored
Indian contribution to English bird
nomenclature submitted to the
IOC (Manakadan & Pittie 2002)
had retained names using ‘Ceylon’,
whereas the ‘politically correct’ IOC
changed them to ‘Sri Lanka’. The
IOC was in fact very inconsistent in
this process: even ‘Abyssinia’ survived
in at least one name, and Bioko
failed to displace Fernando Po in
several. In this respect, retaining or
adopting a discoverer’s name, in this
case Erard’s Lark (as used by Ash &
Atkins 2009), is a safeguard against
geographical name changes. The
same applies to Lybius chaplini also
discussed by Collar, who persuaded
BirdLife International to change
its name from Chaplin’s Barber to
Zambian Barbet: Chaplin remains
himself — Zambia was Northern
Rhodesia earlier in the 20th century,
and prior to that was simply a
disparate large area with no unified
name.
Although there is no real reason
why English geographical names
should change when local usage does
(we don’t call Egypt ‘el Misr’ or
India Bharat’), there is nonetheless a
general tendency to do so, in Africa
more than anywhere else. It is very
sobering to look at an 1898 map of
Africa and hardly recognise any place
names or state boundaries — half of
today’s countries lack names on the
map altogether! Politically driven
name changes are understandable
in relation to colonial names with
unfortunate connotations (e.g.
Rhodesia), less so where it is possible
to separate the political entity from
the geographical place; e.g. the
Republic of Burkina Faso occupies
the geographical area formerly known
in Europe as Upper Volta, Malawi
the shores of Lake Nyasa. Some name
changes are simply revised ways of
spelling: Botswana/Bechuanafiand] ,
Lesotho/Basuto [land] .
In short, we should be very wary
of name changes, especially when
advanced for sectional interests,
and remember that conservation is
by no means the only issue to be
taken into account when tampering
with established nomenclature.
Even the conservation issue is not
clear cut — the successful rescue of
Psittacula eques and Nesoenas mayeri
has been under the banners of Echo
Parakeet and Pink Pigeon — no
mention of Mauritius, though the
IOC stubbornly prefers ‘Mauritius
Parakeet’.
References
Ash, J. & Atkins, J. 2009. Birds of
Ethiopia and Eritrea: An Atlas
of Distribution. London, UK:
Christopher Helm.
Gill, F. & Wright, M. 2006. Birds of
the World: Recommended English
Names. London, UK: Christopher
Helm.
Manakadan, R. & Pittie, A. 2002.
Standardized English and scien-
tific names of the birds of the
Indian subcontinent. Newsletter for
Birdwatchers 42(3): i-viii, 1-36.
Anthony Cheke
139 Hurst Street,
Oxford OX4 1HE, UK
E-mail: anthony.cheke@
innerbookshop. com
Letters to the Editor
Bull ABC Vol 1 7 No 1 (2010) -133
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The ABC welcomes original contributions on
all aspects of the birds of Africa, here defined
as the area covered by Collar, N.J. & Stuart,
S.N. 1985. Threatened Birds of Africa and
Related Islands: The ICBP/IUCN Red Data
Book. Cambridge, UK: International Council
for Bird Preservation, namely continental
Africa, Indian Ocean islands west of 80'E,
e.g. Madagascar, the Mascarene Islands and
Socotra; Atlantic Ocean islands on or east
of the mid-Atlantic ridge, e.g. the Tristan da
Cunha group, the Azores and the Canaries.
Contributions will be accepted subject
to editing and refereeing by independent
reviewers, where appropriate. The Editorial
Team will be happy to advise authors on
the acceptability of material at draft stage
if desired.
Submissions
Two hard (printed) copies should be sent
unless submitting by e-mail (preferred) to
the editor’s address on the inside front cover.
Typewritten manuscripts should be double-
spaced, on one side of the paper only, with
wide margins all round. All submissions are
acknowledged.
Contributions are accepted in English
or French: French summaries are required
Notes for Contributors
for all papers published in English, and vice
versa. Those submitting papers should supply
a summary for translation into English, or
French, as appropriate.
If you submit your contribution on CD
or floppy disk, please state computer (e.g.
IBM compatible PC, Macintosh) and word-
processing package (e.g. Word, WordPerfect)
used.
When sending your contribution on
disk, please do not key anything in ALL
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between each column. Unless a sketch map
is provided as part of the article, the names
of places should follow those on standard or
readily available maps (preferably a recent
edition of The Times Atlas of the World).
Preferred names
Given the current instability over worldwide
lists of bird names, authors are requested to
follow those used in The Birds of Africa Vols.
1-7. The African Bird Club has recently pub-
lished (www.africanbirdclub.org/resources/
checklist.html) a checklist of birds in its
region. This is based on Birds of Africa but
incorporates more recent revisions where
appropriate. It includes preferred scientific,
English and French names, as well as races
and alternatives used by publications widely
used in Africa. For bird names this list should
be used or at least the preferred name used
there should be given as an alternative. For
non-Birds of Africa species (e.g. from the
Malagasy region) use Dowsett & Forbes-
Watson (1993). Deviation from such works
should be noted and the reasons given. The
Editorial Team will keep abreast of changes
in nomenclature and when an agreed list
of African names is available, will consider
switching to follow it.
Style
Authors are requested to follow conventions
used in The Bulletin of the African Bird Club
and to refer to a recent issue for guidance. A
detailed style guide can be obtained, either
electronically or as a hard copy, on request
from the Managing Editor.
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Mixed Sources
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r C199« Forest Stewardship Council
Ascension Island: John Hughes, The Old Shop, High
Street, Shipton Bellinger, Hampshire SP9 7UE, UK,
E-mail: rasuk@btconnect.com.
Angola: Pedro de Franca Doria vaz Pinto, Rua Holder
Neto 12, 7 A; Luanda. E-mail: pvpinto@clix.pt.
Australia: K. David Bishop, PO Box 1234, Armidale,
NSW 2330. E-mail: kdbishop@ozemail.com.au.
Austria: Graham Tebb, Graf Starhemberggasse 20/14,
1040 Vienna. E-mail: tebb@fwf.ac.at.
Belgium: Jan Goossens, Vruntebaan 18, 2520
Emblem. Tel/fax: +32 3 488 13 71. E-mail: jan.
goossens5@pandora.be.
Botswana: Chris Brewster, PO Box 26292, Gaborone.
E-mail: cbrewster@botsnet.bw.
Canada: Antonio Salvadori, 17 Colborn Street, Guelph,
Ontario. NIG 2M4. E-mail: Salvadori@rogers.com.
Canary Islands/Spain: Tony Clarke, Repiiblica
Dominicana No. 61, Barrio de Fatima, 38500
Gtifmar, Tenerife. E-mail: bluechaffinch@
btopcnworld.com.
Central African Republic: Nigel Voaden, 18 Fair Hill,
Shipham, Winscombe, Somerset BS25 1TH, UK.
E-mail: nigel.voaden@talk21.com.
Denmark: Uffe Gjol Sorensen, Ovengaden Oven
Vandet 68,2, 1415 Copenhagen. E-mail: ugs@post7.
tele.dk.
Democratic Republic of Congo: Byamana Robert
Kizungu, Head of Ornithology Laboratory, CRSN-
Lwiro, DRC, BP02 Cyangugu, Rwanda. E-mail:
kbyamana@yahoo.com.
Djibouti: Abdi Jama, do Guelle Osman Guelle,
PO Box 239, Djibouti City. E-mail: abdi.jama@
ymail.com.
Egypt: Sherif & Mindy Baha El Din, 2 Abdalla El
Katib St. Apt. 3, Dokki, Cairo. Tel/Fax: 3608160.
E-mail: egyptcalling@yahoo.com.
Eritrea: Russom Teklay, do Andeberhan Teklay,
PFDJ, zone: Maekel, sub-zone: south east, PO Box
4618, Asmara. E-mail russotek79@yahoo.com.
Ethiopia: Mengistu Wondafrash, Ethiopian Wildlife
& Natural History Society, PO Box 13303, Addis
Ababa. E-mail: m.wondafrash@ewnhs.org.et.
France: Bob & Fran^oise Dowsett, Le Pouget,
Suniene, F30440. E-mail: Dowsett@aol.com.
Finland: Annika Forsten, Tornvalksv. 2 bst 15,
02620 Esbo. E-mail: annika.forsten@elisanet.fi.
The Gambia: Solomon Jallow, do WABSA,
Department of Parks & Wildlife, Management HQ,
Abuko Nature Reserve, Abuko, PMB 676 S/K.
E-mail: habitatafrica@hotmail.com.
Supported and Affiliated Membership
The Supporting Members scheme is a key part
of the Club’s strategy of encouraging the spread
of knowledge and understanding of birds as
widely as possible throughout Africa. The scheme
enables Africans who would not otherwise have
the resources to join, to become members of
the Club. The scheme is funded by Supporting
Members who pay a minimum of UKT30 to
cover their own membership and the subscription
of at least one African member. The money they
contribute over and above their own subscription
is placed in a special fund that is used to cover
the membership expenses of African members
whom they may have nominated, or who have
been nominated by other Club members.
Although we have suggested a minimum
of UKT30 to become a Supporting Member,
any contribution is welcome. All members of the
Club, even if they do not feel able to become
Supporting Members themselves, are invited to
nominate candidates for supported memberships.
Candidates should be nationals of an African
country, with a genuine interest in wild birds
but without the resources to become members
in their own right. Africans who think they
may qualify are very welcome to put their own
ABC Representatives
Ghana: Samuel Kofi Nyarne, PO Box KIA 30284,
Airport, Accra. E-mail: samknyame02@yahoo.com.
Italy: Giuseppe Micali, Via Volterra 3, Milano,
Ml 1-20146. E-mail: xeaym@tin.it.
Kenya: Simon Nganda Musila, Department of
Ornithology, National Museums of Kenya,
PO Box 40658, GPO 00100, Nairobi. Email:
surnbirds@yahoo.com.
Liberia: Moses A. Massah, Society for the
Conservation of Nature of Liberia, Monrovia Zoo,
PO Box 2628, Monrovia. E-mail: mosesmassah@
yahoo.com.
Libya: Abdulmaula A. Hamza, Head, Marine
Conservation, Nature Conservation Dept.,
Environment General Authority EGA, Box 13793
Tripoli. E-mail: abdhamza@gmail.com.
Madagascar: Julien Ramanampamonjy,
Section Oiseaux, PBZT, BP 4096, 101 Antananarivo.
E-mail: julien_asity@mel.moov.mg (mark FAO:
Julien Ramanampamonjy).
Malawi: Tiwonge Mzumara, do Likhubula House,
PO Box 111, Mulanje. E-mail: tiwongem@yahoo.com.
Namibia: Tim Osborne, PO Box 22, Okaukuejo,
vis Outjo 9000. E-mail: kori@iway.na.
Nigeria: Phil Hall, A. P. Leventis Ornithological
Research Institute, Jos. E-mail: philhall.obe@
btinternet.com.
Rwanda: Marcell Claassen, Elegantafrica, PO Box 181,
Musanze. E-mail: marcell@elegantafrica.com
Sao Tome & Principe: Angus Gascoigne, CP 289,
Sao Tome. E-mail: agascoigne@eits.st.
Seychelles: Adrian Skerrett, Shipping House,
PO Box 336, Victoria, Mahe. Fax: 380538. E-mail:
maheship@seychelles.net or adrian@skerrett.fsnet.
co.uk.
Sierra Leone: Kenneth Gbengba, Conservation
Society of Sierra Leone, 2 Pyke Street, PO Box
1292, Freetown, Sierra Leone. E-mail: factsfinding@
yahoo.com.
Somaliland/Somalia: Abdi Jama, do Guelle Osman
Guelle, PO Box 239, Djibouti City, Republic of
Djibouti. E-mail: abdi.jama@ymail.com.
South Africa: Adam Riley, Managing Director,
Rockjumper Birding Tours, PO Box 13972, Cascades
3202. E-mail: info@rockjumper.co.za.
Swaziland: Dr Ara Monadjem, UN1SWA, P/Bag 4,
Kwaluseni. E-mail: ara@uniswacc.uniswa.sz.
Tanzania: Lota Melamari, CEO/Coordinator, Wildlife
Conservation Society of Tanzania, Garden Avenue,
names forward, supported by a letter of recom-
mendation from someone such as their employer,
teacher or an officeholder in a local wildlife
organisation.
The scheme now also includes clubs who
wish to be affiliated with the African Bird Club
in African countries where it is difficult for local
individuals to become members in their own
right. Clubs accepted for membership under
the scheme receive up to six copies of each
issue of the bulletin for circulation among their
members. Instead of paying a membership fee.
Clubs are asked to provide a short annual report
on their activities that may be published in the
bulletin. Clubs interested in becoming Affiliated
Member Clubs are invited to apply to the ABC
Secretary giving details of their membership, their
constitution or a statement of their objectives
and conditions of their membership, and their
activities to date.
ABC Information Service
ABC offers a service to help members with
information requests. Perhaps you are planning
a trip to Africa and need local advice, or maybe
you are in search of an obscure fact about an
African species. The Club does not guarantee
Plot 39; PO Box 70919, Dar es Salaam. E-mail:
melamarilota@yahoo.co.uk.
Tunisia: Hichem Azafzaf, 1 1 rue Abou el alia el maari,
Cite el liouda, 2080 Ariana. E-mail: azafzaf@gnet.tn.
Uganda: Prof. Derek Pomeroy, Makerere University
Institute of the Environment and Natural Resources,
PO Box 7298, Kampala. E-mail: derek@imul.com.
USA: Kurt Leuschner, 70065 Sonora Road #267,
Mountain Centre, CA 92561. E-mail: kleuschner@
collegeofthedesert.edu.
Zambia: Rod Tether, Kutandala Camp, North
Luangwa NP. E-mail: rod@kutandala.com
Zimbabwe: Rod Tether, Kutandala Camp, North
Luangwa NP. E-mail: rod@kutandala.com.
The ABC Representatives scheme aims to support
existing members by providing a local point of
contact in their region, for example, to answer queries
to the Club, to solicit submissions for the bulletin,
and possibly to arrange local meetings for members.
Existing ABC members can contact their local
Representative in the first instance with queries relating
to the Club. ABC Representatives help to recruit new
members in their region, for example, by distributing
posters and arranging local advertising. In Africa, ABC
Representatives help to identify opportunities to invest
the ABC Conservation Fund and candidates for the
Supported Membership scheme.
The Club aims to appoint many further ABC
Representatives. If you are interested in supporting
and promoting the Club in your region, have any
queries, or require further information relating to the
ABC Representatives scheme please do not hesitate to
contact the Membership Secretary at the Club address,
e-mail membership@africanbirdclub.org.
ABC is seeking Country Representatives in the
following countries, principally within the Club's
region: Algeria, Azores, Benin, Burkina Faso, Burundi,
Cameroon, Cape Verde Islands, Chad, Comoros &
Mayotte, Cote d’Ivoire, Djibouti, Equatorial Guinea,
Gabon, Guinea-Bissau, Guinea Conakry, Madeira,
Mali, Mauritania, Mauritius, Morocco, Mozambique,
Netherlands, Niger, Reunion, Rodriguez, Senegal,
Socotra, Somalia, St Helena, Sudan, Togo, Tristan da
Cunha and USA.
to find all the answers but will try to help. The
service is free to ABC members. Contact: Keith
Betron, who is also custodian of ABC’s journal
library', at 8 Dukes Close, Folly Hill, Farnham,
Surrey, GU9 ODR, UK. Tel: +44 1252 724068.
E-mail: info@africanbirdclub.org.
AfricanBirding e-mail discussion list
Launched, in October 2000, by the ABC and
the Pan-African Ornithological Congress,
AfricanBirding or AB, as it is known, has become
a useful forum for those interested in African
birds. To join the discussion, which averages
1-2 messages a day, send a blank e-mail to
African Birding-subscribe@)'ahoogroups.com.
You w'ill then receive an e-mail instructing you
how to join.
The Club also maintains a list of members'
e-mail addresses. This list is confidential and used
only for Club purposes, e.g. for informing mem-
bers of upcoming events and news concerning
the Club. It is not divulged to any'body outside
the Club or used for commercial advertising. At
present it includes addresses for about 50% of
the membership. Please send any additions or
amendments to the membership secretary: mem-
bership@africanbirdclub.org.
Humblot’s Heron / Heron de Humblot Ardea humbloti by Martin Searle, www.mtsphotography.com